TWI572559B - Purification and Recovery of Ammonia from Wastewater by Ammonia Wastewater - Google Patents
Purification and Recovery of Ammonia from Wastewater by Ammonia Wastewater Download PDFInfo
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- TWI572559B TWI572559B TW103115246A TW103115246A TWI572559B TW I572559 B TWI572559 B TW I572559B TW 103115246 A TW103115246 A TW 103115246A TW 103115246 A TW103115246 A TW 103115246A TW I572559 B TWI572559 B TW I572559B
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- containing wastewater
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- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 title claims description 229
- 229910021529 ammonia Inorganic materials 0.000 title claims description 115
- 239000002351 wastewater Substances 0.000 title claims description 64
- 238000000746 purification Methods 0.000 title claims description 9
- 238000011084 recovery Methods 0.000 title description 9
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 37
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 claims description 25
- 235000011114 ammonium hydroxide Nutrition 0.000 claims description 25
- 238000000034 method Methods 0.000 claims description 25
- 239000007788 liquid Substances 0.000 claims description 22
- 238000000926 separation method Methods 0.000 claims description 17
- 239000005457 ice water Substances 0.000 claims description 16
- 238000001704 evaporation Methods 0.000 claims description 13
- 239000007791 liquid phase Substances 0.000 claims description 12
- 238000001179 sorption measurement Methods 0.000 claims description 12
- 238000010521 absorption reaction Methods 0.000 claims description 11
- 230000008020 evaporation Effects 0.000 claims description 11
- 230000009615 deamination Effects 0.000 claims description 10
- 238000006481 deamination reaction Methods 0.000 claims description 10
- 239000007787 solid Substances 0.000 claims description 10
- 229910001385 heavy metal Inorganic materials 0.000 claims description 9
- 150000002500 ions Chemical class 0.000 claims description 9
- 230000000694 effects Effects 0.000 claims description 8
- 239000002699 waste material Substances 0.000 claims description 8
- 238000001816 cooling Methods 0.000 claims description 7
- 238000010438 heat treatment Methods 0.000 claims description 7
- 229910021645 metal ion Inorganic materials 0.000 claims description 7
- NWUYHJFMYQTDRP-UHFFFAOYSA-N 1,2-bis(ethenyl)benzene;1-ethenyl-2-ethylbenzene;styrene Chemical compound C=CC1=CC=CC=C1.CCC1=CC=CC=C1C=C.C=CC1=CC=CC=C1C=C NWUYHJFMYQTDRP-UHFFFAOYSA-N 0.000 claims description 5
- 239000003456 ion exchange resin Substances 0.000 claims description 5
- 229920003303 ion-exchange polymer Polymers 0.000 claims description 5
- 239000012071 phase Substances 0.000 claims description 5
- 239000007921 spray Substances 0.000 claims description 5
- 238000011001 backwashing Methods 0.000 claims description 4
- 239000003638 chemical reducing agent Substances 0.000 claims description 4
- 239000002893 slag Substances 0.000 claims description 4
- 230000015572 biosynthetic process Effects 0.000 claims description 3
- 238000001914 filtration Methods 0.000 claims description 3
- 238000001514 detection method Methods 0.000 claims description 2
- 239000003595 mist Substances 0.000 claims description 2
- 238000010025 steaming Methods 0.000 claims description 2
- 238000005406 washing Methods 0.000 claims description 2
- 125000004122 cyclic group Chemical group 0.000 claims 1
- 239000011347 resin Substances 0.000 claims 1
- 229920005989 resin Polymers 0.000 claims 1
- 229920006395 saturated elastomer Polymers 0.000 claims 1
- 150000003384 small molecules Chemical class 0.000 claims 1
- 239000012535 impurity Substances 0.000 description 12
- 238000004064 recycling Methods 0.000 description 8
- 239000000047 product Substances 0.000 description 7
- 238000005516 engineering process Methods 0.000 description 4
- 150000002736 metal compounds Chemical class 0.000 description 4
- 238000009833 condensation Methods 0.000 description 3
- 230000005494 condensation Effects 0.000 description 3
- 238000002309 gasification Methods 0.000 description 3
- 150000001875 compounds Chemical class 0.000 description 2
- 239000012141 concentrate Substances 0.000 description 2
- 238000003795 desorption Methods 0.000 description 2
- 230000007613 environmental effect Effects 0.000 description 2
- 238000004458 analytical method Methods 0.000 description 1
- 238000000889 atomisation Methods 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 229940125833 compound 23 Drugs 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 238000004821 distillation Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000003912 environmental pollution Methods 0.000 description 1
- 238000007689 inspection Methods 0.000 description 1
- 229920002521 macromolecule Polymers 0.000 description 1
- 238000004519 manufacturing process Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 239000012466 permeate Substances 0.000 description 1
- 230000008929 regeneration Effects 0.000 description 1
- 238000011069 regeneration method Methods 0.000 description 1
- 239000004065 semiconductor Substances 0.000 description 1
- 239000013589 supplement Substances 0.000 description 1
- 238000009834 vaporization Methods 0.000 description 1
- 230000008016 vaporization Effects 0.000 description 1
- 238000010792 warming Methods 0.000 description 1
- 238000004065 wastewater treatment Methods 0.000 description 1
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- Heat Treatment Of Water, Waste Water Or Sewage (AREA)
- Treatment Of Water By Ion Exchange (AREA)
- Physical Water Treatments (AREA)
Description
本發明係與含氨廢水中純化濃縮回收氨再利用方法相關,特別在氨的純化濃縮提純氨水濃度與脫除重金屬離子技術相關,如何防止二次汙染及資源化目標,讓回收利用可達市售標準商品,實現無害化再生使用技術。 The invention relates to the method for purifying and concentrating and recovering ammonia in the ammonia-containing wastewater, in particular, the ammonia concentration in the purification and concentration of ammonia is related to the technology of removing heavy metal ions, how to prevent the secondary pollution and resource utilization target, and the recycling can reach the city. Standardized products are sold to achieve harmless recycling technology.
現今科技產業中均有大量使用氨,我們從LED、面板、太陽能電池(光伏)、半導體產業、PCB產業中均有大量使用,相對在使用後則形成大量的含氨廢水,而其含氨廢水中存有重金屬離子,形成汙染環境的風險,重金屬不去除直接回收有汙染擴大風險。而目前回收作業上往往忽略這項因素,不知不覺造成環境上破壞。在目前含氨廢水回收氨的處理,將氨蒸發出來的方法,主要有吹脫法及蒸氨法來進行處理(是全面性處理廢水),運用過多熱能讓氨在廢水中蒸發,運用於較高濃度的廢水,往往需要大設備及較多能源,分析說明如下: A large amount of ammonia is used in the technology industry today. We use it extensively from LED, panel, solar cell (photovoltaic), semiconductor industry, and PCB industry. After use, it forms a large amount of ammonia-containing wastewater, and its ammonia-containing wastewater. There are heavy metal ions in the middle, which poses a risk of polluting the environment. Heavy metals are not removed and directly recovered. At present, this factor is often ignored in recycling operations, and it is unconsciously causing environmental damage. In the current treatment of ammonia recovery from ammonia-containing wastewater, the method of evaporating ammonia is mainly carried out by the stripping method and the ammonia distillation method (which is a comprehensive treatment of wastewater), and the excess heat is used to vaporize the ammonia in the wastewater. High-concentration wastewater often requires large equipment and more energy. The analysis is as follows:
一.吹脫法處理 1. Blowout treatment
利用載體(空氣或水蒸氣)通入廢水中應用氣液介面,經由氣相與液相接觸,使水中溶解游離的氨,透過氣液介面向氣相轉移。吹脫法一般有兩個主要設備,吹脫池(移出)及吹脫塔(吸附)兩種設備,在操作時需要大量氣體打入廢水中,水中會隨該氣體使氨移 出,而後端氣體吸附裝置必須足夠吸附能力,其吸附是大量空氣及氨混合氣體(設備大),或高溫水蒸氣及氨(吸附需有大冷凝系統),相對成本高,一般僅用於高濃度含氨廢水回收氨,經濟效益有限。 The carrier (air or water vapor) is introduced into the wastewater to apply the gas-liquid interface, and the liquid phase is contacted with the liquid phase via the gas phase to dissolve the free ammonia in the water, and the gas-liquid medium is transferred to the gas phase. The stripping method generally has two main equipments, a blow-off tank (removal) and a stripping tower (adsorption). In operation, a large amount of gas is required to be driven into the wastewater, and the water will move the ammonia with the gas. Out, the back-end gas adsorption device must have sufficient adsorption capacity, its adsorption is a large amount of air and ammonia mixed gas (large equipment), or high-temperature water vapor and ammonia (adsorption requires a large condensation system), relatively high cost, generally only used for high The recovery of ammonia from the concentration of ammonia-containing wastewater has limited economic benefits.
二.蒸氨法處理 2. Steaming ammonia treatment
主要是利用額外熱能直接對廢水加熱,把氨從廢水中蒸發出來,蒸發需要大量熱能。完全利用熱把廢水中氨蒸發出來,需要有較高溫度,溫度愈高水蒸氣多且溫度高對後段吸附則需要大能源損耗,一樣僅限於高濃度含氨廢水處理應用,該設備裝設空間需要很大,投資高且效率低。 It is mainly to use the extra heat to directly heat the wastewater, to evaporate ammonia from the wastewater, and to evaporate requires a large amount of heat. The use of heat to completely evaporate the ammonia in the wastewater requires higher temperature. The higher the temperature, the higher the water vapor and the higher the temperature, the higher the energy consumption for the latter stage. The same is limited to the high-concentration ammonia-containing wastewater treatment application. It needs a lot of money, high investment and low efficiency.
由上述可知含氨廢水的處理需要有大量能源且設備成本高,需要有大的處理場所,需要外加能源或載體,形成過多損耗,如何有效率、低成本把廢水中氨提純濃縮,達到市場化標準是當前環保一大難題。 It can be seen from the above that the treatment of ammonia-containing wastewater requires a large amount of energy and high equipment cost, requires a large treatment site, requires additional energy or a carrier, forms excessive loss, and how to purify and concentrate ammonia in the wastewater efficiently and at low cost to achieve marketization. The standard is a major environmental problem.
本發明主要目的,防止含氨廢水中重金屬離子汙染環境,特別在回收程序中加以去除,讓氨回收資源化且無害化,預防環境汙染,提高可再利用範圍。 The main purpose of the invention is to prevent heavy metal ions in the ammonia-containing wastewater from polluting the environment, especially in the recycling process, to make the ammonia recovery resource-recycling and harmless, prevent environmental pollution, and improve the reusable range.
本發明另一主要目的,將廢水中氨加以氣化、純化及濃縮(將大分子雜質遺留在液相),去除雜質提高回收氨的品質及濃度,提高回收產品價值,讓其符合市售商品規格,提昇回收效益,讓工廠有投資意願。 Another main object of the present invention is to vaporize, purify and concentrate ammonia in wastewater (to leave macromolecular impurities in the liquid phase), remove impurities, improve the quality and concentration of recovered ammonia, and increase the value of recycled products to make them conform to commercial products. Specifications, improve recycling efficiency, let the factory have a willingness to invest.
本發明另一主要目的,將廢水中的氨蒸出,應用高效率節 能方法降低氨回收能源損耗,特別應用擴大表面積模式,讓含氨廢水表面積能有效極大化,特別應用了加壓噴霧蒸發模式,讓含氨廢水霧化,讓氨能快速移出液相,進一步透過氣液分離槽把氣液相分開,讓大部份的氨能由氣相移出,達到純化及濃縮目的,再將氣化部份透過循環水冷凝補捉(利用文氏管原理吸附)把氨溶於冰水中,隨時間累積吸收,可達市售商品濃度規格,實現商品化目標。 Another main object of the present invention is to distill ammonia from waste water and apply a high efficiency section. It can reduce the loss of ammonia recovery energy, and especially expand the surface area mode to maximize the surface area of ammonia-containing wastewater. In particular, the pressurized spray evaporation mode is applied to atomize ammonia-containing wastewater, allowing ammonia to be quickly removed from the liquid phase and further penetrated. The gas-liquid separation tank separates the gas and liquid phases, so that most of the ammonia can be removed from the gas phase for purification and concentration purposes, and then the gasification part is condensed by circulating water to capture (using the venturi principle to adsorb) ammonia. Dissolved in ice water, accumulated absorption over time, up to the concentration specifications of commercial products, to achieve commercialization goals.
本發明另一主要目的,利用能源轉移技術,降低回收氨處理成本,特別建置熱泵系統,應用熱泵冷熱交換優勢(熱輸出端溫度40℃~80℃,冷輸出端溫度0℃~20℃),讓熱輸出端能量提供給廢水中氨蒸發熱能,滿足蒸發前加熱需求。而另一冷輸出端提供循環冰水冷卻效果,將氨溶於水所產生熱能帶走,讓氨快速溶於水中,達到有效捕捉。 Another main object of the present invention is to use energy transfer technology to reduce the cost of recovery ammonia treatment, especially to build a heat pump system, and to apply the advantages of heat pump cold heat exchange (heat output temperature 40 ° C ~ 80 ° C, cold output temperature 0 ° C ~ 20 ° C) The heat output energy is supplied to the ammonia in the waste water to evaporate heat energy to meet the heating demand before evaporation. The other cold output provides a cooling effect of circulating ice water, and the heat energy generated by dissolving ammonia in water is taken away, so that ammonia is quickly dissolved in water to achieve effective capture.
為達上述目的特別建置了全新的處理回收資源化方案,應用氨蒸發條件將氨自廢水中蒸出,讓氨脫離水達到純化目的,一般大分子雜物會留在液相,不會隨氨蒸出,因而對氨形成純化及濃縮作用。特別從蒸發條件上進行系統的設計,蒸發除了基本熱能外還有氣壓及表面積,壓力愈低愈容易蒸發。而另一個是表面積,擴大表面積易可達到快速蒸發效果,因而在系統中建置了加壓霧化來增加表面積,利用循環冰水建立文氏管負壓吸收效果,讓廢水中氨能快速蒸發出來,進一步經以純化循環冰水吸收氨,透過吸收濃度會逐漸上升,可達市售產品規格,達到商品化目的。 In order to achieve the above purposes, a new treatment and recycling resource scheme has been specially established. The ammonia is evaporated from the wastewater by ammonia evaporation conditions, and the ammonia is separated from the water to achieve the purpose of purification. Generally, the macromolecular impurities will remain in the liquid phase and will not follow The ammonia is distilled off, thereby purifying and concentrating ammonia. Especially in the design of the system from the evaporation conditions, in addition to the basic heat energy, there is air pressure and surface area. The lower the pressure, the easier it is to evaporate. The other is the surface area. The surface area is easy to achieve rapid evaporation. Therefore, pressurized atomization is built into the system to increase the surface area. The venturi water is used to establish the negative pressure absorption effect of the venturi, so that the ammonia in the wastewater can be quickly evaporated. When it comes out, it absorbs ammonia by purifying circulating ice water, and the absorption concentration will gradually increase, reaching the specifications of commercial products, and achieving commercialization.
其實施程序說明如下(如圖一所示), The implementation procedure is as follows (as shown in Figure 1).
程序(一)、過濾除渣 Procedure (1), filtering and slag removal
將廢氨水進行除渣,去除水中懸浮物及固體物,將水中雜 質攔截下來,可透過逆洗方式將固體雜質移出。 Dissolve the waste ammonia water to remove suspended solids and solids from the water, and mix the water The mass is intercepted and the solid impurities can be removed by backwashing.
程序(二)、重金屬離子吸附 Procedure (2), heavy metal ion adsorption
利用離子交換樹脂吸附,去除廢水中重金屬離子,防止氨回收使用有二次汙染風險,該吸附金屬離子可以利用還原劑將金屬離子化合物移出系統外,讓含氨廢水得到進一步去除雜質及純化。 The use of ion exchange resin adsorption to remove heavy metal ions in the wastewater to prevent ammonia pollution has secondary pollution risks. The adsorbed metal ions can use the reducing agent to remove the metal ion compounds out of the system, so that the ammonia-containing wastewater can be further removed and purified.
程序(三)、加壓及昇溫 Procedure (3), pressurization and warming
讓含氨廢水透過加壓泵動力進行輸送,而在進行過程中透過熱泵及熱交換器提供蒸氨所需能量讓氨加溫,其溫度設定在40℃~80℃,可增加氨的脫除效果,提高設備處理能力。 The ammonia-containing wastewater is transported through the pressurized pump power, and during the process, the heat required to supply the ammonia through the heat pump and the heat exchanger is used to warm the ammonia, and the temperature is set at 40 ° C to 80 ° C to increase the removal of ammonia. The effect is to improve the processing power of the device.
程序(四)、噴霧蒸發 Procedure (four), spray evaporation
利用高壓透過噴嘴讓含氨廢水表面積擴大化(形成霧狀),讓氨能快速蒸發移出液相,而大部份氨與部份水蒸發,形成氨的純化與濃縮效果,大分子不易氣化分子則會留在液相,進一步氣化則讓氨得到純化,更進一步提昇氨與水濃度比例,形成了氨濃縮效果。 The high-pressure permeation nozzle is used to enlarge the surface area of the ammonia-containing wastewater (formation of mist), allowing ammonia to evaporate quickly and remove the liquid phase, and most of the ammonia and part of the water evaporate to form an ammonia purification and concentration effect, and the macromolecule is not easily vaporized. The molecule will remain in the liquid phase, and further gasification will allow the ammonia to be purified, further increasing the ratio of ammonia to water concentration, and forming an ammonia concentration effect.
程序(五)、氣液分離 Procedure (5), gas-liquid separation
透過緩衝氣液分離槽,大分子量雜質及水凝結成液相之脫氨後廢水,由氣液分離槽下方移出,而氨及部份水氣化由上方引出。 The deaminated wastewater, which has a large molecular weight impurity and water condensed into a liquid phase, is removed from the gas-liquid separation tank through a buffer gas-liquid separation tank, and ammonia and a part of water vaporization are taken out from above.
程序(六)、循環冰水吸收 Procedure (6), circulating ice water absorption
其冷凝溫度設定在0℃~20℃,吸收氨形成再生氨水,氣相 的氨氣及水氣可以用循環水循環吸附,運用文氏管原理形成負壓吸附作用,可將氣化物能快速吸收,形成再生氨水,該再生氨水會因循環時間增加,增加再生氨水濃度,進而達到市售商品濃度標準,能直接售出或進一步再濃縮形成液氨,達到資源化目的。 The condensing temperature is set at 0 ° C ~ 20 ° C, absorbing ammonia to form regenerated ammonia water, gas phase The ammonia gas and water vapor can be circulated and adsorbed by circulating water, and the venturi principle is used to form a vacuum adsorption effect, which can quickly absorb the gasification to form regenerated ammonia water, and the regenerated ammonia water will increase the concentration of regenerated ammonia water due to an increase in cycle time, and further It can reach the concentration standard of commercial products and can be directly sold or further concentrated to form liquid ammonia to achieve the purpose of resource utilization.
程序(七)、濃度檢測 Procedure (7), concentration detection
針對吸收槽中氨水進行濃度監測,當氨水濃度檢查符合商品規格時即可直接再利用,為確保資源回收之再生品質,引出再生氨水後再補充純水吸收氨。 The concentration of ammonia water in the absorption tank is monitored. When the ammonia concentration check meets the product specifications, it can be directly reused. In order to ensure the regeneration quality of the resource recovery, the regenerated ammonia water is introduced and the pure water is added to absorb the ammonia.
程序(八)、出貨行銷 Procedure (8), shipping marketing
當品質檢查合格後,可將再生氨水引出系統儲存於暫存槽內等待出貨。 After the quality inspection is passed, the regenerated ammonia water can be taken out of the system and stored in the temporary storage tank for shipment.
針對上述氣液分離槽中液相廢水為脫氨廢水,已經脫除大部份氨,能簡易處理後排放,更可將脫氨廢水直接回生產製程中再利用,如作廢氨氣排放處理洗滌水、循環吸收水或清潔用水,提昇水再利用率,達到節能減排目標。而其前段昇溫廢氨水蒸發設定為40℃~80℃及後段冰水循環水氨氣冷卻吸收為0℃~20℃,則可共同一組熱泵達到能源有效轉換方式,減少能源損耗,達到清潔處理之目標。 The liquid phase wastewater in the gas-liquid separation tank is de-ammonia wastewater, and most of the ammonia has been removed, which can be discharged after simple treatment, and the de-ammonia wastewater can be directly returned to the production process for reuse, such as waste ammonia treatment and washing. Water, circulating water or clean water, improve water reuse, and achieve energy saving and emission reduction targets. The evaporation of the ammonia water in the front section is set to 40 °C ~ 80 °C and the absorption of ammonia water in the downstream ice water circulating water is 0 °C ~ 20 °C, then a group of heat pumps can achieve a energy efficient conversion mode, reducing energy loss and achieving clean treatment. aims.
1‧‧‧含氨廢水 1‧‧‧Ammonia wastewater
2‧‧‧脫氨廢水 2‧‧‧Deamination wastewater
3‧‧‧純水 3‧‧‧ pure water
4‧‧‧吸氨循環冰水 4‧‧‧Ammonia cycle ice water
5‧‧‧高濃度純化氨水 5‧‧‧High concentration of purified ammonia
6‧‧‧除雜質含氨廢水 6‧‧‧In addition to impurities containing ammonia wastewater
10‧‧‧過濾器 10‧‧‧Filter
11‧‧‧過濾器脫附裝置 11‧‧‧Filter desorption device
12‧‧‧殘渣收集槽 12‧‧‧ Residue collection tank
13‧‧‧固態殘渣 13‧‧‧ solid residue
20‧‧‧離子交換樹脂吸附槽 20‧‧‧Ion exchange resin adsorption tank
21‧‧‧脫附逆洗裝置 21‧‧‧Desorbed backwashing device
22‧‧‧金屬化合物收集槽 22‧‧‧Metal compound collection tank
23‧‧‧金屬化合物 23‧‧‧Metal compounds
24‧‧‧還原劑 24‧‧‧Reducing agent
25‧‧‧除雜質含氨廢水收集槽 25‧‧‧In addition to impurity ammonia-containing wastewater collection tank
30‧‧‧加溫熱交換器 30‧‧‧heating heat exchanger
40‧‧‧氣液分離槽 40‧‧‧ gas-liquid separation tank
41‧‧‧噴霧蒸發器 41‧‧‧ spray evaporator
42‧‧‧氣液分離槽氣相出口 42‧‧‧ gas-liquid separation tank gas outlet
T1‧‧‧加熱溫控表 T1‧‧‧heating temperature control table
T2‧‧‧冷卻溫控表 T2‧‧‧Cooling temperature control table
P‧‧‧壓力表 P‧‧‧ pressure gauge
P1‧‧‧含氨廢水輸入泵 P1‧‧‧Ammonia wastewater input pump
P2‧‧‧加壓泵 P2‧‧‧Pressure pump
P3‧‧‧脫氨廢水輸出泵 P3‧‧‧Deamination wastewater output pump
P4‧‧‧循環冰水輸送泵 P4‧‧‧Circulating ice water pump
P5‧‧‧高濃度純化氨水輸出泵 P5‧‧‧High concentration purified ammonia water output pump
Q‧‧‧濃度計 Q‧‧‧ concentration meter
L1‧‧‧蒸發器液位計 L1‧‧‧Evaporator Level Gauge
L2‧‧‧循環冰水液位計 L2‧‧‧Circulating ice water level gauge
L3‧‧‧高濃度純化氨水液位計 L3‧‧‧High concentration purified ammonia water level gauge
L4‧‧‧脫氨廢水液位計 L4‧‧‧Deamination wastewater level gauge
43‧‧‧氣液分離槽液相出口 43‧‧‧liquid-liquid separation tank liquid outlet
44‧‧‧氨氣 44‧‧‧Ammonia
45‧‧‧水氣 45‧‧‧Water and gas
50‧‧‧冷凝循環吸收槽 50‧‧‧Condensation circulation absorption tank
51‧‧‧文氏管 51‧‧‧ venturi tube
52‧‧‧純水補充閥 52‧‧‧Pure water supplement valve
53‧‧‧高濃度純化氨水收集槽 53‧‧‧High concentration purified ammonia water collection tank
54‧‧‧高濃度純化氨水輸出裝置 54‧‧‧High concentration purified ammonia water output device
55‧‧‧排放裝置 55‧‧‧Draining device
60‧‧‧冷卻熱交換器 60‧‧‧Cooling heat exchanger
70‧‧‧熱泵系統 70‧‧‧Heat pump system
80‧‧‧脫氨廢水收集槽 80‧‧‧Deamination wastewater collection tank
81‧‧‧脫氨廢水收集裝置 81‧‧‧Deamination wastewater collection device
圖1、含氨廢水中純化濃縮回收再利用流程圖。 Figure 1. Flow chart of purification, concentration, recovery and reuse in ammonia-containing wastewater.
圖2、廢氨水回收純化系統圖。 Figure 2. Diagram of waste ammonia recovery and purification system.
如圖二所示,將工廠中含氨廢水1透過含氨廢水輸入泵P1引入過濾器10中,將固態殘渣13遺留在過濾器10上,該過濾器10上固態殘渣13可利用過濾器脫附裝置11,將固態殘渣13脫附移入殘渣收集槽12中。通過過濾器10的廢氨水再流入離子交換樹脂吸附槽20中,將廢氨水中金屬離子吸附,形成除雜質含氨廢水6再流入除雜質含氨廢水收集槽25中,達到初級純化目的,該金屬離子化合物可透過還原劑24及脫附逆洗裝置21,將吸附金屬離子脫附出來,形成金屬化合物23,導入金屬化合物收集槽22中。 As shown in FIG. 2, the ammonia-containing wastewater 1 in the plant is introduced into the filter 10 through the ammonia-containing wastewater input pump P1, and the solid residue 13 is left on the filter 10. The solid residue 13 on the filter 10 can be removed by the filter. Attached to the device 11, the solid residue 13 is desorbed and moved into the residue collection tank 12. The waste ammonia water passing through the filter 10 is further flowed into the ion exchange resin adsorption tank 20, and the metal ions in the waste ammonia water are adsorbed to form an impurity-containing ammonia wastewater 6 and then flowed into the impurity-containing ammonia wastewater collection tank 25 to achieve primary purification. The metal ion compound can permeate the adsorbed metal ions through the reducing agent 24 and the desorption backwashing device 21 to form the metal compound 23, and is introduced into the metal compound collecting tank 22.
除雜質含氨廢水6經加壓泵P2加壓引入加溫熱交換器30中加熱,吸收蒸發氨所需要的熱能,可使用熱泵熱端輸出溫度約40℃~80℃的熱能,再經過噴霧蒸發器41將除雜質含氨廢水6霧化以增加蒸發表面積,讓除雜質含氨廢水6中氨能快速蒸發氣化,透過氣液分離槽40讓大部份氨氣44及水氣45的氣體,由氣液分離槽氣相出口42引出,而液相由氣液分離槽液相出口43引出,形成脫氨廢水2。 In addition to the impurity ammonia-containing wastewater 6 is pressurized by the pressure pump P2 and introduced into the heating heat exchanger 30 to absorb the heat energy required for evaporating ammonia, and the heat energy of the heat pump can be used to output a heat of about 40 ° C to 80 ° C, and then sprayed. The evaporator 41 atomizes the impurity-containing ammonia wastewater 6 to increase the evaporation surface area, so that the ammonia in the impurity-containing ammonia wastewater 6 can be quickly evaporated and vaporized, and the gas-liquid separation tank 40 is passed through the gas-liquid separation tank 40 to allow most of the ammonia gas 44 and the water gas 45. The gas is taken out from the vapor-liquid outlet 42 of the gas-liquid separation tank, and the liquid phase is taken out from the liquid-liquid outlet 43 of the gas-liquid separation tank to form the deamination wastewater 2.
純水3透過純水補充閥52引入冷凝循環吸收槽50,藉由循環冰水輸送泵P4抽取,經冷卻熱交換器60形成0℃~20℃冰水,對氨有吸附及冷凝形成吸氨循環冰水4。透過吸氨循環冰水4循環而形成文氏管51作用下,可讓氣液分離槽40中蒸發的氣體快速牽引吸入冷凝循環吸收槽50冷凝及吸 附。吸氨循環冰水4中氨含量會逐漸上升,氨濃度可由濃度計Q加以測量,當濃度達到市售標準氨水時,可由高濃度純化氨水輸出泵P5引出導入高濃度純化氨水收集槽53中暫存準備出貨。 The pure water 3 is introduced into the condensing circulation absorption tank 50 through the pure water replenishing valve 52, and is extracted by the circulating ice water pump P4, and formed into ice water of 0 ° C to 20 ° C through the cooling heat exchanger 60 to adsorb and condense ammonia to form ammonia. Circulating ice water 4. By forming the venturi 51 through the ammonia circulation circulating ice water 4 cycle, the vaporized gas in the gas-liquid separation tank 40 can be quickly drawn into the condensation circulation absorption tank 50 to condense and suck. Attached. The ammonia content in the ammonia-suppressing ice water 4 will gradually increase. The ammonia concentration can be measured by the concentration meter Q. When the concentration reaches the commercially available standard ammonia water, it can be extracted from the high-concentration purified ammonia water output pump P5 and introduced into the high-concentration purified ammonia water collection tank 53. Save and prepare for shipment.
針對氣液分離槽40中脫氨廢水2可以由脫氨廢水輸出泵P3引出到脫氨廢水收集槽80中,進一步回收再利用或經簡易處理排放,達到有效回收再利用目的及無害化處理模式。 The deamination wastewater 2 in the gas-liquid separation tank 40 can be taken out from the deamination wastewater output pump P3 to the deamination wastewater collection tank 80, and further recycled or discharged through simple treatment to achieve effective recycling and harmless treatment mode. .
針對加溫及冷卻需求,可利用熱泵70熱端輸出40℃~80℃及冷端輸出0℃~20℃來進行能源交換運作。 For heating and cooling requirements, the energy exchange operation can be performed by using the hot pump 70 hot end output 40 ° C ~ 80 ° C and the cold end output 0 ° C ~ 20 ° C.
Claims (6)
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|---|---|---|---|---|
| TWI627990B (en) * | 2017-04-20 | 2018-07-01 | 亞氨科技股份有限公司 | Ammonia removing apparatus and system for low concentration ammonia water and ammonia water producing system thereof |
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| CN113371732B (en) * | 2021-07-15 | 2024-01-05 | 安徽东至广信农化有限公司 | Ammonia recovery device in o-phenylenediamine synthesis |
| CN117945483A (en) * | 2022-10-27 | 2024-04-30 | 中国石油化工股份有限公司 | Method and system for simultaneously treating ammonia-containing waste gas and ammonia nitrogen waste liquid containing metal ions |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1884105A (en) * | 2006-07-10 | 2006-12-27 | 重庆工学院 | Atomization flash-evaporation ammonia-removing process for ammonia and nitrogen-containing wastewater |
| CN201148353Y (en) * | 2007-11-06 | 2008-11-12 | 金川集团有限公司 | Apparatus for reclaiming ammonia from ammonia-containing waste water |
| CN102190341A (en) * | 2010-03-09 | 2011-09-21 | 天华化工机械及自动化研究设计院 | Stripping ammonia-removing method based on flash evaporation and heat pump technologies |
| CN202148224U (en) * | 2011-04-18 | 2012-02-22 | 中国水利水电科学研究院 | Ammonia-nitrogen wastewater treatment device and system |
-
2014
- 2014-04-29 TW TW103115246A patent/TWI572559B/en active
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN1884105A (en) * | 2006-07-10 | 2006-12-27 | 重庆工学院 | Atomization flash-evaporation ammonia-removing process for ammonia and nitrogen-containing wastewater |
| CN201148353Y (en) * | 2007-11-06 | 2008-11-12 | 金川集团有限公司 | Apparatus for reclaiming ammonia from ammonia-containing waste water |
| CN102190341A (en) * | 2010-03-09 | 2011-09-21 | 天华化工机械及自动化研究设计院 | Stripping ammonia-removing method based on flash evaporation and heat pump technologies |
| CN202148224U (en) * | 2011-04-18 | 2012-02-22 | 中国水利水电科学研究院 | Ammonia-nitrogen wastewater treatment device and system |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| TWI627990B (en) * | 2017-04-20 | 2018-07-01 | 亞氨科技股份有限公司 | Ammonia removing apparatus and system for low concentration ammonia water and ammonia water producing system thereof |
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