CN110723857B - A high salt water concentration crystallization treatment system and process - Google Patents
A high salt water concentration crystallization treatment system and process Download PDFInfo
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- 238000002425 crystallisation Methods 0.000 title claims abstract description 68
- 230000008025 crystallization Effects 0.000 title claims abstract description 68
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 title claims abstract description 55
- 238000000034 method Methods 0.000 title claims abstract description 19
- 150000003839 salts Chemical class 0.000 title claims description 23
- 239000007788 liquid Substances 0.000 claims abstract description 95
- 238000001556 precipitation Methods 0.000 claims abstract description 92
- 239000013078 crystal Substances 0.000 claims abstract description 56
- 239000010865 sewage Substances 0.000 claims abstract description 17
- 238000001223 reverse osmosis Methods 0.000 claims abstract description 15
- 238000001704 evaporation Methods 0.000 claims abstract description 11
- 230000008020 evaporation Effects 0.000 claims abstract description 11
- 238000005189 flocculation Methods 0.000 claims abstract description 9
- 238000000108 ultra-filtration Methods 0.000 claims abstract description 9
- 230000016615 flocculation Effects 0.000 claims abstract description 8
- 238000005185 salting out Methods 0.000 claims description 40
- 238000000926 separation method Methods 0.000 claims description 21
- 238000010438 heat treatment Methods 0.000 claims description 9
- 239000012535 impurity Substances 0.000 claims description 8
- 125000004122 cyclic group Chemical group 0.000 claims description 3
- 239000002893 slag Substances 0.000 claims description 3
- 238000005086 pumping Methods 0.000 claims 1
- 239000002244 precipitate Substances 0.000 abstract description 2
- 239000000463 material Substances 0.000 description 18
- 239000002245 particle Substances 0.000 description 8
- 239000012267 brine Substances 0.000 description 7
- HPALAKNZSZLMCH-UHFFFAOYSA-M sodium;chloride;hydrate Chemical compound O.[Na+].[Cl-] HPALAKNZSZLMCH-UHFFFAOYSA-M 0.000 description 7
- 238000004062 sedimentation Methods 0.000 description 6
- 238000005265 energy consumption Methods 0.000 description 5
- 238000004519 manufacturing process Methods 0.000 description 5
- 238000004064 recycling Methods 0.000 description 5
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- 230000006835 compression Effects 0.000 description 4
- 238000007906 compression Methods 0.000 description 4
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- 239000000243 solution Substances 0.000 description 4
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- 239000002994 raw material Substances 0.000 description 3
- 239000007787 solid Substances 0.000 description 3
- CDBYLPFSWZWCQE-UHFFFAOYSA-L Sodium Carbonate Chemical compound [Na+].[Na+].[O-]C([O-])=O CDBYLPFSWZWCQE-UHFFFAOYSA-L 0.000 description 2
- FAPWRFPIFSIZLT-UHFFFAOYSA-M Sodium chloride Chemical compound [Na+].[Cl-] FAPWRFPIFSIZLT-UHFFFAOYSA-M 0.000 description 2
- 230000018044 dehydration Effects 0.000 description 2
- 238000006297 dehydration reaction Methods 0.000 description 2
- 238000002474 experimental method Methods 0.000 description 2
- 238000001914 filtration Methods 0.000 description 2
- 238000002203 pretreatment Methods 0.000 description 2
- 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
- ZLMJMSJWJFRBEC-UHFFFAOYSA-N Potassium Chemical compound [K] ZLMJMSJWJFRBEC-UHFFFAOYSA-N 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
- 230000009286 beneficial effect Effects 0.000 description 1
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- 229910052700 potassium Inorganic materials 0.000 description 1
- 239000011591 potassium Substances 0.000 description 1
- 230000003134 recirculating effect Effects 0.000 description 1
- 229910052708 sodium Inorganic materials 0.000 description 1
- 239000011734 sodium Substances 0.000 description 1
- 229910000029 sodium carbonate Inorganic materials 0.000 description 1
- 239000011780 sodium chloride Substances 0.000 description 1
- 229910052938 sodium sulfate Inorganic materials 0.000 description 1
- 235000011152 sodium sulphate Nutrition 0.000 description 1
- 239000000725 suspension Substances 0.000 description 1
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F9/00—Multistage treatment of water, waste water or sewage
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/02—Treatment of water, waste water, or sewage by heating
- C02F1/04—Treatment of water, waste water, or sewage by heating by distillation or evaporation
- C02F1/041—Treatment of water, waste water, or sewage by heating by distillation or evaporation by means of vapour compression
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/02—Treatment of water, waste water, or sewage by heating
- C02F1/04—Treatment of water, waste water, or sewage by heating by distillation or evaporation
- C02F1/043—Details
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/40—Devices for separating or removing fatty or oily substances or similar floating material
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- C—CHEMISTRY; METALLURGY
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- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/441—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by reverse osmosis
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- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/444—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by ultrafiltration or microfiltration
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- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F1/00—Treatment of water, waste water, or sewage
- C02F1/52—Treatment of water, waste water, or sewage by flocculation or precipitation of suspended impurities
- C02F1/5281—Installations for water purification using chemical agents
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- C02F2001/5218—Crystallization
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- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
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- C02F2209/02—Temperature
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- C02F2301/00—General aspects of water treatment
- C02F2301/04—Flow arrangements
- C02F2301/046—Recirculation with an external loop
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- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2301/00—General aspects of water treatment
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Abstract
Description
技术领域technical field
本发明涉及污水排放技术领域,具体涉及一种高盐水浓缩结晶处理系统及工艺。The invention relates to the technical field of sewage discharge, in particular to a high salt water concentration and crystallization treatment system and process.
背景技术Background technique
近年来,为节约浓缩成本,不少企业、MVR生产企业和多效浓缩企业都对污水零排放的浓缩结晶进行了研究及生产实验,在研究和生产实验的过程中,都得到同一个结果:混盐的结晶颗粒偏细,浓缩液为悬浊液,液固分离困难,生产过程管道及换热器堵塞严重,晶体脱水困难,使得零排放不能持续而良性地实施和运行。In recent years, in order to save the cost of concentration, many companies, MVR production companies and multi-effect concentration companies have carried out research and production experiments on concentrated crystallization with zero discharge of sewage. During the process of research and production experiments, they all obtained the same result: The crystal particles of the mixed salt are too fine, the concentrated liquid is a turbid liquid, the liquid-solid separation is difficult, the pipelines and heat exchangers in the production process are seriously blocked, and the crystal dehydration is difficult, so that the zero discharge cannot be implemented and operated in a sustainable and benign manner.
由于反渗透浓水浓缩结晶晶体本身就具有结晶体颗粒不大、结晶晶体的机械强度差的缺陷,使得在MVR在生产过程中,料液靠强制循环泵强制循环,由于分离器没有促进晶体和溶液分离的装置或缺少有效分离装置,使得结晶体与溶液分离不彻底,再加上循环泵的进口设在分离器的底部,在循环的过程中,结晶体随着料液在循环管道里不断循环,晶体在循环的过程中不断受到循环泵叶轮的高速剪切,致使晶体不断破碎,造成结晶颗粒偏细或是形成悬浊的浓缩液,使得液固分离困难。Because the concentrated crystalline crystal of reverse osmosis concentrated water has the defects of small crystal particles and poor mechanical strength of the crystalline crystal, in the production process of MVR, the feed liquid is forced to circulate by the forced circulation pump, because the separator does not promote the crystal and solution. The separation device or the lack of an effective separation device makes the separation of the crystal and the solution incomplete. In addition, the inlet of the circulating pump is located at the bottom of the separator. During the circulation process, the crystal is continuously circulated in the circulation pipeline with the feed liquid, and the crystal is In the process of circulation, it is continuously subjected to high-speed shearing by the impeller of the circulating pump, which causes the crystals to be continuously broken, resulting in fine crystal particles or the formation of suspending concentrated liquid, which makes the liquid-solid separation difficult.
发明内容SUMMARY OF THE INVENTION
为了克服现有技术中存在的缺点和不足,本发明的目的在于提供一种高盐水浓缩结晶处理系统,该处理系统结构新颖,操作简单,使高盐水的晶体基本在第一沉淀结晶罐和第二沉淀结晶罐的罐体底部沉淀并结晶,避免了料液循环泵的叶轮对其剪切,保证了晶体的完整,并且结晶体还可以在沉淀室里继续成长成更大的结晶颗粒;同时通过蒸汽的循环和料液的循环,提高了原料的利用率。In order to overcome the shortcomings and deficiencies in the prior art, the purpose of the present invention is to provide a high-salt water concentration and crystallization treatment system, which has a novel structure and simple operation, so that the crystals of the high-salt water are basically in the first precipitation crystallizing tank and the second crystallizing tank. The bottom of the second precipitation crystallizing tank is precipitated and crystallized, which avoids shearing by the impeller of the material-liquid circulating pump, ensures the integrity of the crystal, and the crystal can continue to grow into larger crystal particles in the precipitation chamber; The circulation of steam and the circulation of material and liquid improves the utilization rate of raw materials.
本发明的目的在于提供一种高盐水浓缩结晶处理工艺,该处理工艺操作简单,能使得结晶体在第一沉淀结晶罐和第二沉淀结晶罐的罐体底部形成并长大,避免了料液循环泵的叶轮对其剪切,保证了晶体的完整,可适用于大规模处理。The purpose of the present invention is to provide a high-salt water concentration crystallization treatment process, which is simple to operate, and enables crystals to form and grow at the bottom of the tank body of the first precipitation crystallization tank and the second precipitation crystallization tank, avoiding the circulation of material and liquid The impeller of the pump shears it to ensure the integrity of the crystal, which is suitable for large-scale processing.
本发明的目的通过下述技术方案实现:一种高盐水浓缩结晶处理系统,按照处理使用顺序依次包括污水收集池、前处理装置、絮凝沉淀装置、超滤装置、反渗透装置、MVR蒸发浓缩装置,所述MVR蒸发浓缩装置按照处理使用顺序依次包括板式换热器、第一沉淀结晶罐、第二沉淀结晶罐和料液循环泵,所述第一沉淀结晶罐的蒸汽出口端、第二沉淀结晶罐的蒸汽出口端均通过蒸汽压缩机与板式换热器连通;所述板式换热器设置有进料端,板式换热器的进料端通过进料管道与反渗透装置的输出端连通。The object of the present invention is achieved through the following technical solutions: a high-salt water concentration and crystallization treatment system, which sequentially includes a sewage collection tank, a pretreatment device, a flocculation sedimentation device, an ultrafiltration device, a reverse osmosis device, and an MVR evaporation and concentration device according to the order of treatment and use. , the MVR evaporation and concentration device sequentially includes a plate heat exchanger, a first precipitation crystallization tank, a second precipitation crystallization tank and a material-liquid circulation pump according to the order of processing and use. The steam outlet end of the crystallization tank is connected with the plate heat exchanger through the steam compressor; the plate heat exchanger is provided with a feed end, and the feed end of the plate heat exchanger is communicated with the output end of the reverse osmosis device through a feed pipe .
本发明通过设置第一沉淀结晶罐和第二沉淀结晶罐对晶体进行沉淀结晶,且采用料液循环的方式,使得料液多次循环经过第一沉淀结晶罐和第二沉淀结晶罐,其中料液在第一沉淀结晶罐中溢流至第二沉淀结晶罐,分别在两个罐体的底部沉淀有混盐晶体,避免了晶体经过离心泵或循环泵时被叶轮所剪切而损坏晶体的完整性,使得晶体在罐体的底部长大,保证了晶体的完整度,进而实现料液中盐成分的易于分离。其中,所述的高盐水中包括有硫酸钠、碳酸钠、氯化钠等盐成分,通过本发明的二级沉淀分离方法,将高盐水中的盐成分沉淀并结晶于罐体底部形成混盐结晶体。In the present invention, the crystal is precipitated and crystallized by arranging the first precipitation and crystallization tank and the second precipitation and crystallization tank, and the method of material liquid circulation is adopted, so that the material liquid is circulated through the first precipitation and crystallization tank and the second precipitation and crystallization tank for many times, wherein the material The liquid overflows from the first precipitation and crystallization tank to the second precipitation and crystallization tank, and the mixed salt crystals are precipitated at the bottom of the two tanks respectively, which avoids the crystals being sheared by the impeller when they pass through the centrifugal pump or the circulating pump, which will damage the crystals. Integrity, make the crystal grow at the bottom of the tank, ensure the integrity of the crystal, and then realize the easy separation of the salt component in the feed liquid. Wherein, the high salt water includes salt components such as sodium sulfate, sodium carbonate, sodium chloride, etc., through the secondary precipitation separation method of the present invention, the salt components in the high salt water are precipitated and crystallized at the bottom of the tank to form mixed salt Crystals.
另一方面,每次循环中,部分料液在第一沉淀结晶罐和第二沉淀结晶罐中蒸发,并通过罐体蒸汽出口端流通至蒸汽压缩机中进行压缩,经过压缩的料液蒸汽的热能增加,并再次流入至板式换热器中以提供热能,为料液在板式换热器中的预加热提供热能,减少外界对板式换热器提供热能的能耗,节约能耗。On the other hand, in each cycle, part of the feed liquid is evaporated in the first precipitation crystallization tank and the second precipitation crystallization tank, and is circulated to the steam compressor through the steam outlet end of the tank for compression. The heat energy increases, and flows into the plate heat exchanger again to provide heat energy, which provides heat energy for the preheating of the material liquid in the plate heat exchanger, reduces the external energy consumption for providing heat energy to the plate heat exchanger, and saves energy consumption.
优选的,所述板式换热器还设置有循环料液进口端和循环料液出口端,所述第一沉淀结晶罐的中上部设置有第一进料端和第一料液出口端,所述第二沉淀结晶罐的中上部设置有第二进料端和第二料液出口端;Preferably, the plate heat exchanger is also provided with a circulating feed liquid inlet end and a circulating feed liquid outlet end, and a first feed end and a first feed liquid outlet end are provided in the upper middle and upper part of the first precipitation and crystallization tank, so The middle and upper part of the second precipitation crystallization tank is provided with a second feed end and a second feed liquid outlet end;
所述板式换热器的循环料液进口端通过供料管道与所述第一沉淀结晶罐的第一进料端连通,所述第二沉淀结晶罐的第二进料端通过连接管道与所述第一沉淀结晶罐的第一料液出口端连通,所述第二沉淀结晶罐的第二料液出口端通过第一循环管道与所述料液循环泵的进口端连通,所述料液循环泵的出口端通过第二循环管道与所述板式换热器的循环料液进口端连通。The inlet end of the circulating feed liquid of the plate heat exchanger is communicated with the first feed end of the first precipitation and crystallization tank through the feeding pipeline, and the second feed end of the second precipitation and crystallization tank is connected to the other through the connecting pipeline. The first material and liquid outlet end of the first precipitation and crystallization tank is communicated, and the second material and liquid outlet end of the second precipitation and crystallization tank is communicated with the inlet end of the material and liquid circulating pump through the first circulation pipeline. The outlet end of the circulation pump is communicated with the inlet end of the circulating feed liquid of the plate heat exchanger through the second circulation pipeline.
本发明通过上述的部件,使得料液在板式换热器、第一沉淀结晶罐、第二沉淀结晶罐、料液循环泵之间实现循环,进而循环地经过第一沉淀结晶罐和第二沉淀结晶罐,使得料液中的盐成分在罐体的底部沉淀并结晶,经过多次循环,混盐结晶体在罐体的底部生成并长大,避免了晶体经过离心泵或循环泵时被叶轮所剪切而损坏晶体的完整性,使得晶体在罐体的底部长大,保证了晶体的完整度,并实现料液中盐成分的易于分离。其中,所述供料管道上设置有供料泵,以将板式换热器中的料液泵进第一沉淀结晶罐内。Through the above-mentioned components, the present invention makes the feed liquid circulate among the plate heat exchanger, the first precipitation crystallization tank, the second precipitation crystallization tank, and the feed liquid circulating pump, and then circulates through the first precipitation crystallization tank and the second precipitation crystallization tank. The crystallizing tank makes the salt components in the feed liquid precipitate and crystallize at the bottom of the tank body. After many cycles, the mixed salt crystals are formed and grown at the bottom of the tank body, avoiding the crystals passing through the centrifugal pump or circulating pump. The integrity of the crystal is damaged by shearing, so that the crystal grows at the bottom of the tank, which ensures the integrity of the crystal and realizes the easy separation of the salt component in the feed liquid. Wherein, a feeding pump is arranged on the feeding pipeline to pump the feed liquid in the plate heat exchanger into the first precipitation and crystallization tank.
优选的,所述板式换热器还设置有循环蒸汽进口端,所述第一沉淀结晶罐的上部设置有第一蒸汽出口端,所述第二沉淀结晶罐的上部设置有第二蒸汽出口端;Preferably, the plate heat exchanger is further provided with a circulating steam inlet end, the upper part of the first precipitation and crystallization tank is provided with a first steam outlet end, and the upper part of the second precipitation and crystallization tank is provided with a second steam outlet end ;
所述第一沉淀结晶罐的第一蒸汽出口端通过第一蒸汽管道与所述蒸汽压缩机的进口端连通,所述第二沉淀结晶罐的第二蒸汽出口端通过第二蒸汽管道与所述蒸汽压缩机的进口端连通,蒸汽压缩机的出口端通过循环蒸汽管道与所述板式换热器的循环蒸汽进口端连通。The first steam outlet end of the first precipitation and crystallization tank is communicated with the inlet end of the steam compressor through a first steam pipe, and the second steam outlet end of the second precipitation and crystallization tank is communicated with the steam compressor through a second steam pipe. The inlet end of the steam compressor is communicated, and the outlet end of the steam compressor is communicated with the circulating steam inlet end of the plate heat exchanger through a circulating steam pipeline.
本发明通过上述的部件,使得料液中的蒸汽通过第一蒸汽出口端、第一蒸汽管道、第二蒸汽出口端、第二蒸汽管道流通至蒸汽压缩机进行压缩,经过压缩的料液蒸汽的热能增加,并再次流入至板式换热器中以提供热能,为料液在板式换热器中的预加热提供热能,减少外界对板式换热器提供热能的能耗,节约能耗,实现了资源的循环利用。其中,第一蒸汽管道和第二蒸汽管道的末端连接有蒸汽汇流管道,将蒸汽汇流至蒸汽压缩机的进口端。In the present invention, through the above-mentioned components, the steam in the feed liquid flows to the steam compressor through the first steam outlet end, the first steam pipe, the second steam outlet end and the second steam pipe for compression, and the compressed feed liquid steam is compressed. The heat energy increases, and flows into the plate heat exchanger again to provide heat energy, providing heat energy for the preheating of the material liquid in the plate heat exchanger, reducing the external energy consumption for providing heat energy to the plate heat exchanger, saving energy, and realizing Recycling of resources. Wherein, the ends of the first steam pipe and the second steam pipe are connected with a steam confluence pipe to confluence the steam to the inlet end of the steam compressor.
优选的,所述板式换热器还设置有冷凝水出口端,所述冷凝水出口端通过冷凝水管道连接有冷凝水储存罐,所述冷凝水管道上设置有第一阀门。Preferably, the plate heat exchanger is further provided with a condensed water outlet end, and the condensed water outlet end is connected with a condensed water storage tank through a condensed water pipeline, and the condensed water pipeline is provided with a first valve.
本发明经蒸汽压缩机压缩过的料液蒸汽的热能增加,并再次流入至板式换热器中以提供热能,而料液蒸汽提供热能后,自身热能降低,冷却并冷凝为冷凝水,通过冷凝水出口端、冷凝水管道流向并储存于冷凝水储存罐中,收集冷凝水并可再次用于蒸汽压缩机和料液循环泵的冷却,提高了系统中的物料循环利用率,减少外界对蒸汽压缩机和料液循环泵进行冷却所消耗的能量,节约能耗,实现了资源的循环利用。In the present invention, the heat energy of the feed liquid vapor compressed by the steam compressor increases, and flows into the plate heat exchanger again to provide heat energy. After the feed liquid vapor provides heat energy, its own heat energy is reduced, cooled and condensed into condensed water. The water outlet end and the condensed water pipeline flow and are stored in the condensed water storage tank. The condensed water is collected and can be reused for cooling of the steam compressor and the material-liquid circulation pump, which improves the material recycling rate in the system and reduces the external influence on the steam. The energy consumed by the compressor and the liquid circulating pump for cooling saves energy consumption and realizes the recycling of resources.
其中,设置的第一阀门,能便于控制冷凝水的流速。Wherein, the set first valve can easily control the flow rate of the condensed water.
优选的,所述供料管道上设置有供料泵,能将板式换热器中的料液泵至第一沉淀结晶罐中,提高料液循环过程的动力,避免混盐晶体在板式换热器中沉积,实用性高。Preferably, the feeding pipeline is provided with a feeding pump, which can pump the feed liquid in the plate heat exchanger to the first precipitation crystallization tank, so as to improve the power of the circulation process of the feed liquid and avoid the mixed salt crystals in the plate heat exchange. Deposition in the device, high practicability.
优选的,所述第一沉淀结晶罐和第二沉淀结晶罐内部均设置有螺旋导流叶片,将热量较高的料液导流至罐体的底部,使得结晶体在罐体的底部与母液及蒸汽分离,结晶体下沉至底部继续长大,蒸汽上升溢流至蒸汽压缩机进行压缩并再次利用。Preferably, both the first precipitation and crystallization tank and the second precipitation and crystallization tank are provided with spiral guide vanes, which guide the feed liquid with higher heat to the bottom of the tank body, so that the crystal body is at the bottom of the tank body with the mother liquor and the mother liquid. The steam is separated, the crystals sink to the bottom and continue to grow, and the steam rises and overflows to the steam compressor for compression and reuse.
本发明的另一目的通过下述技术方案实现:一种应用上述的高盐水浓缩结晶处理系统的处理工艺,包括如下步骤:Another object of the present invention is achieved through the following technical solutions: a process for applying the above-mentioned high brine concentration crystallization treatment system, comprising the steps:
(1)将工厂污水收集至污水收集池中,经由前处理装置进行除油除渣处理,然后经过絮凝沉淀装置、超滤装置、反渗透装置进行除杂处理;其中,所述絮凝沉淀装置是脱除污水中的悬浮物,超滤装置的过滤精度为10nm,过滤污水中的细小杂质,反渗透装置采用离子膜,过滤精度为0.1nm,能过滤掉90%以上的溶解盐,除去大量杂质,使得进入MVR蒸发浓缩装置的高盐水料液能沉积形成完整的晶体。(1) The factory sewage is collected in the sewage collection tank, and the oil and slag removal treatment is carried out through the pretreatment device, and then the impurity removal treatment is carried out through the flocculation sedimentation device, the ultrafiltration device and the reverse osmosis device; wherein, the flocculation sedimentation device is a To remove suspended solids in sewage, the ultrafiltration device has a filtration accuracy of 10nm, which can filter fine impurities in sewage. The reverse osmosis device adopts an ion membrane with a filtration accuracy of 0.1nm, which can filter out more than 90% of dissolved salts and remove a large amount of impurities. , so that the high brine feed liquid entering the MVR evaporation and concentration device can be deposited to form a complete crystal.
(2)将步骤(1)除杂处理后的料液通过板式换热器的进料端进入板式换热器中升温加热,再依次流入第一沉淀结晶罐、第二沉淀结晶罐进行沉淀分离,分离后的料液经过料液循环泵泵入至板式换热器进行再次升温加热,进行循环沉淀分离;(2) the feed liquid after the impurity removal treatment in step (1) enters the plate heat exchanger through the feed end of the plate heat exchanger for heating and heating, and then flows into the first precipitation crystallization tank and the second precipitation crystallization tank for precipitation separation , and the separated feed liquid is pumped into the plate heat exchanger through the feed liquid circulation pump to heat up again for recirculating precipitation and separation;
同时,升温加热的料液在第一沉淀结晶罐、第二沉淀结晶罐中蒸发,蒸发后的蒸汽经由蒸汽压缩机压缩处理后循环至板式换热器中对料液提供热能;At the same time, the heated feed liquid is evaporated in the first precipitation crystallization tank and the second precipitation crystallization tank, and the evaporated steam is compressed and processed by the steam compressor and circulated to the plate heat exchanger to provide heat energy to the feed liquid;
经过多次循环沉淀分离后,高盐水浓缩结晶于第一沉淀结晶罐和第二沉淀结晶罐的底部,得到混盐结晶体。After several cycles of precipitation and separation, the high brine is concentrated and crystallized at the bottom of the first precipitation crystallization tank and the second precipitation crystallization tank to obtain mixed salt crystals.
优选的,所述步骤(2)中,料液在板式换热器中升温至85-100℃后进入至第一沉淀结晶罐、第二沉淀结晶罐进行循环沉淀分离。Preferably, in the step (2), the feed liquid is heated to 85-100° C. in the plate heat exchanger and then enters the first precipitation crystallization tank and the second precipitation crystallization tank for cyclic precipitation and separation.
现有的水处理工艺流程中,经反渗透处理的浓水中主要含钠、钾等可溶性盐及部分COD,随着液体水分的蒸发,浓液中的盐分因饱和析出,由于液体中的物质成分复杂,所产生的盐为混盐,混盐晶体的颗粒偏小,大概在60-80目,其结晶体机械强度一般,容易受外力作用破碎成小颗粒,因而目前在MVR处理工艺里,晶体在循环过程中不断受到循环泵叶轮的高速剪切,致使晶体不断破碎,形成细小颗粒的晶体,使得浓缩液形成悬浮液,难以进行固液分离,同时使得生产过程管道及换热器堵塞严重,晶体脱水困难。In the existing water treatment process, the concentrated water treated by reverse osmosis mainly contains soluble salts such as sodium and potassium and part of COD. It is complex, the salt produced is mixed salt, and the particles of mixed salt crystals are relatively small, about 60-80 mesh. The mechanical strength of the crystal is average, and it is easily broken into small particles by external force. During the circulation process, it is continuously subjected to high-speed shearing by the impeller of the circulating pump, which causes the crystals to break continuously and form fine-grained crystals, which makes the concentrated liquid form a suspension, which is difficult to separate solid-liquid. Dehydration is difficult.
因而本发明通过设置第一沉淀结晶罐和第二沉淀结晶罐,料液经由板式换热器升温加热后进入第一沉淀结晶罐和第二沉淀结晶罐进行沉淀分离,同时升温加热后的料液有部分蒸汽挥发,形成二次蒸汽,并经由蒸汽压缩机对二次蒸汽进行压缩,二次蒸汽的热能增加,并再次进入板式换热器中为板式换热器提供热能,利用二次蒸汽压缩后的热能对循环至板式换热器中的料液进行加热,提高了蒸汽热能的循环利用率。而蒸汽提供为料液的加热提供热能后,自身热能降低,冷却并冷凝为冷凝水,通过冷凝水出口端、冷凝水管道流向并储存于冷凝水储存罐中,收集冷凝水并可再次用于蒸汽压缩机和料液循环泵的冷却,提高了系统中的物料循环利用率,减少外界对蒸汽压缩机和料液循环泵进行冷却所消耗的能量,节约能耗,实现了资源的循环利用。Therefore, in the present invention, by setting the first precipitation crystallization tank and the second precipitation crystallization tank, the feed liquid enters the first precipitation crystallization tank and the second precipitation crystallization tank for precipitation and separation after being heated and heated through the plate heat exchanger. Part of the steam volatilizes to form secondary steam, and the secondary steam is compressed by the steam compressor, the heat energy of the secondary steam increases, and enters the plate heat exchanger again to provide heat energy for the plate heat exchanger, using the secondary steam compression The latter heat energy heats the material and liquid circulated to the plate heat exchanger, which improves the circulation utilization rate of steam heat energy. After the steam provides heat energy for the heating of the material liquid, its own heat energy is reduced, cooled and condensed into condensed water, which flows through the condensed water outlet end and the condensed water pipeline and is stored in the condensed water storage tank. The condensed water is collected and can be used again. The cooling of the steam compressor and the material-liquid circulation pump improves the material circulation utilization rate in the system, reduces the energy consumed by the external cooling of the steam compressor and the material-liquid circulation pump, saves energy consumption, and realizes the recycling of resources.
而经由第一沉淀结晶罐和第二沉淀结晶罐沉淀结晶处理后,料液在罐体的底部沉淀分离,并形成高盐水结晶体,高盐水的晶体基本留在第一沉淀结晶罐和第二沉淀结晶罐的罐体底部,避免了料液循环泵的叶轮对它的剪切,保证了晶体的完整,并且结晶体还可以在沉淀室里继续成长成更大的结晶颗粒。After precipitation and crystallization through the first precipitation and crystallization tank and the second precipitation and crystallization tank, the feed liquid is precipitated and separated at the bottom of the tank to form high brine crystals, and the high brine crystals basically stay in the first precipitation and crystallization tank and the second precipitation. The bottom of the crystallizing tank avoids the shearing of it by the impeller of the material-liquid circulating pump, ensuring the integrity of the crystal, and the crystal can continue to grow into larger crystal particles in the precipitation chamber.
其中,第一沉淀结晶罐和第二沉淀结晶罐的罐体内部设置螺旋导流叶片,能将新泵入的过热液体导流到室底部,随后晶体在第一沉淀结晶罐底部与母液及水蒸汽分离,晶体下沉至底部继续长大,母液上升至溢流口溢流至第二沉淀结晶罐,水蒸气则上升溢出水面再次被压缩机压缩再利用,提高了原料的利用率。Among them, spiral guide vanes are arranged inside the tanks of the first precipitation and crystallization tank, which can guide the newly pumped superheated liquid to the bottom of the chamber, and then the crystals are mixed with the mother liquor and water at the bottom of the first precipitation and crystallization tank. The steam is separated, the crystal sinks to the bottom and continues to grow, the mother liquor rises to the overflow port and overflows to the second precipitation and crystallization tank, and the water vapor rises and overflows the water surface and is compressed and reused by the compressor again, which improves the utilization rate of raw materials.
本发明的有益效果在于:本发明的高盐水浓缩结晶处理系统结构新颖,操作简单,使高盐水的晶体基本在第一沉淀结晶罐和第二沉淀结晶罐的罐体底部沉淀并结晶,避免了料液循环泵的叶轮对其剪切,保证了晶体的完整,并且结晶体还可以在沉淀室里继续成长成更大的结晶颗粒;同时通过蒸汽的循环和料液的循环,提高了原料的利用率。The beneficial effects of the present invention are as follows: the high-salt water concentration and crystallization treatment system of the present invention has a novel structure and simple operation, so that the crystals of the high-salt water are basically precipitated and crystallized at the bottoms of the first precipitation and crystallization tanks and the second precipitation and crystallization tanks, thereby avoiding the need for The impeller of the material-liquid circulation pump shears it to ensure the integrity of the crystals, and the crystals can continue to grow into larger crystal particles in the precipitation chamber; at the same time, through the circulation of steam and material and liquid, the utilization of raw materials is improved. Rate.
本发明高盐水浓缩结晶处理工艺操作简单,能使得结晶体在第一沉淀结晶罐和第二沉淀结晶罐的罐体底部形成并长大,避免了料液循环泵的叶轮对其剪切,保证了晶体的完整,实现了污水的零排放及资源循环利用,处理过程不需添加任何沉淀助剂,即可得到结晶良好的结晶体,可适用于大规模处理。The high-salt water concentration and crystallization treatment process of the invention is simple to operate, can make the crystals form and grow at the bottom of the first precipitation crystallization tank and the second precipitation crystallization tank, avoid the impeller of the material-liquid circulating pump to shear it, and ensure the The integrity of the crystals realizes zero discharge of sewage and recycling of resources. The treatment process does not need to add any precipitation aids to obtain well-crystallized crystals, which are suitable for large-scale treatment.
附图说明Description of drawings
图1是本发明的结构框图;Fig. 1 is the structural block diagram of the present invention;
图2是本发明所述MVR蒸发浓缩装置的结构示意图;Fig. 2 is the structural representation of the MVR evaporation and concentration device of the present invention;
附图标记为:1—污水收集池、2—前处理装置、3—絮凝沉淀装置、4—超滤装置、5—反渗透装置、6—MVR蒸发浓缩装置、61—板式换热器、611—进料管道、62—第一沉淀结晶罐、621—供料管道、6211—供料泵、622—连接管道、623—第一蒸汽管道、63—第二沉淀结晶罐、631—第一循环管道、632—第二蒸汽管道、633—蒸汽汇流管道、64—料液循环泵、641—第二循环管道、65—蒸汽压缩机、651—循环蒸汽管道、66—冷凝水管道、67—第一阀门、68—冷凝水储存罐、69—螺旋导流叶片。The reference numerals are: 1—sewage collection tank, 2—pretreatment device, 3—flocculation sedimentation device, 4—ultrafiltration device, 5—reverse osmosis device, 6—MVR evaporation and concentration device, 61—plate heat exchanger, 611 -Feeding pipeline, 62-The first precipitation crystallizing tank, 621-Feeding pipeline, 6211-Feeding pump, 622-Connecting pipeline, 623-The first steam pipeline, 63-The second precipitation crystallizing tank, 631-The first circulation Pipes, 632—the second steam pipe, 633—the steam confluence pipe, 64—the liquid circulation pump, 641—the second circulation pipe, 65—the steam compressor, 651—the circulating steam pipe, 66—the condensed water pipe, 67—the first One valve, 68—condensate storage tank, 69—spiral guide vane.
具体实施方式Detailed ways
为了便于本领域技术人员的理解,下面结合实施例及附图1-2对本发明作进一步的说明,实施方式提及的内容并非对本发明的限定。In order to facilitate the understanding of those skilled in the art, the present invention will be further described below with reference to the embodiments and accompanying drawings 1-2, and the content mentioned in the embodiments does not limit the present invention.
实施例1Example 1
见附图1-2,一种高盐水浓缩结晶处理系统,按照处理使用顺序依次包括污水收集池1、前处理装置2、絮凝沉淀装置3、超滤装置4、反渗透装置5、MVR蒸发浓缩装置6,所述MVR蒸发浓缩装置6按照处理使用顺序依次包括板式换热器61、第一沉淀结晶罐62、第二沉淀结晶罐63和料液循环泵64,所述第一沉淀结晶罐62的蒸汽出口端、第二沉淀结晶罐63的蒸汽出口端均通过蒸汽压缩机65与板式换热器61连通;所述板式换热器61设置有进料端,板式换热器61的进料端通过进料管道611与反渗透装置5的输出端连通。Referring to the accompanying drawings 1-2, a high-salt water concentration and crystallization treatment system includes
所述板式换热器61还设置有循环料液进口端和循环料液出口端,所述第一沉淀结晶罐62的中上部设置有第一进料端和第一料液出口端,所述第二沉淀结晶罐63的中上部设置有第二进料端和第二料液出口端;The
所述板式换热器61的循环料液进口端通过供料管道621与所述第一沉淀结晶罐62的第一进料端连通,所述第二沉淀结晶罐63的第二进料端通过连接管道622与所述第一沉淀结晶罐62的第一料液出口端连通,所述第二沉淀结晶罐63的第二料液出口端通过第一循环管道631与所述料液循环泵64的进口端连通,所述料液循环泵64的出口端通过第二循环管道641与所述板式换热器61的循环料液进口端连通。The inlet end of the circulating feed liquid of the
所述板式换热器61还设置有循环蒸汽进口端,所述第一沉淀结晶罐62的上部设置有第一蒸汽出口端,所述第二沉淀结晶罐63的上部设置有第二蒸汽出口端;The
所述第一沉淀结晶罐62的第一蒸汽出口端通过第一蒸汽管道623与所述蒸汽压缩机65的进口端连通,所述第二沉淀结晶罐63的第二蒸汽出口端通过第二蒸汽管道632与所述蒸汽压缩机65的进口端连通,蒸汽压缩机65的出口端通过循环蒸汽管道651与所述板式换热器61的循环蒸汽进口端连通。The first steam outlet end of the first precipitation and
所述板式换热器61还设置有冷凝水出口端,所述冷凝水出口端通过冷凝水管道66连接有冷凝水储存罐68,所述冷凝水管道66上设置有第一阀门67。The
所述供料管道621上设置有供料泵6211。A
所述第一沉淀结晶罐62和第二沉淀结晶罐63内部均设置有螺旋导流叶片69。
实施例2Example 2
一种应用上述的高盐水浓缩结晶处理系统的处理工艺,包括如下步骤:A process for applying the above-mentioned high brine concentration crystallization treatment system, comprising the steps:
1将工厂污水收集至污水收集池1中,经由前处理装置2进行除油除渣处理,然后经过絮凝沉淀装置3、超滤装置4、反渗透装置5进行除杂处理;1. Collect factory sewage into
2将步骤1除杂处理后的料液通过板式换热器61的进料端进入板式换热器61中升温加热,再依次流入第一沉淀结晶罐62、第二沉淀结晶罐63进行沉淀分离,分离后的料液经过料液循环泵64泵入至板式换热器61进行再次升温加热,进行循环沉淀分离;2. The feed liquid after the impurity removal treatment in
同时,升温加热的料液在第一沉淀结晶罐62、第二沉淀结晶罐63中蒸发,蒸发后的蒸汽经由蒸汽压缩机65压缩处理后循环至板式换热器61中对料液提供热能;At the same time, the heated feed liquid is evaporated in the first
经过多次循环沉淀分离后,高盐水浓缩结晶于第一沉淀结晶罐62和第二沉淀结晶罐63的底部,得到混盐结晶体。After several cycles of precipitation and separation, the high brine is concentrated and crystallized at the bottom of the first
优选的,所述步骤2中,料液在板式换热器61中升温至85-100℃后进入至第一沉淀结晶罐62、第二沉淀结晶罐63进行循环沉淀分离;具体地,所述升温温度为85℃、90℃、95℃或100℃。Preferably, in the
上述实施例为本发明较佳的实现方案,除此之外,本发明还可以其它方式实现,在不脱离本发明构思的前提下任何显而易见的替换均在本发明的保护范围之内。The above-mentioned embodiment is a preferred implementation scheme of the present invention. In addition, the present invention can also be implemented in other ways, and any obvious replacements are within the protection scope of the present invention without departing from the concept of the present invention.
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Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101891330A (en) * | 2010-07-23 | 2010-11-24 | 深圳市能源环保有限公司 | Power plant wastewater treatment system and method |
CN103991997A (en) * | 2014-05-30 | 2014-08-20 | 中国石油集团东北炼化工程有限公司吉林设计院 | Strong brine evaporating and crystallizing system |
CN104341072A (en) * | 2014-11-12 | 2015-02-11 | 湖北加德科技股份有限公司 | Energy-saving waste-water continuous evaporating crystallizing system |
CN104445786A (en) * | 2014-12-15 | 2015-03-25 | 宁波摩尔森膜环保科技有限公司 | Process and device for treating high-concentration salt-containing wastewater |
CN110330165A (en) * | 2019-06-05 | 2019-10-15 | 中国石油天然气集团有限公司 | Strong brine zero-emission and sub-prime crystallizing treatment process and processing system |
Family Cites Families (4)
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CN204848322U (en) * | 2015-04-12 | 2015-12-09 | 中山中珠环保科技有限公司 | High salt solution processing system |
CN205099370U (en) * | 2015-11-08 | 2016-03-23 | 黄生根 | High concentration contains salt waste water evaporation crystallization process device |
CN205275243U (en) * | 2015-12-04 | 2016-06-01 | 武汉宏澳绿色能源工程有限责任公司 | Evaporation plant of board -like forced circulation's of MVR landfill leachate reverse osmosis dope |
CN108409018A (en) * | 2018-05-15 | 2018-08-17 | 上海奕茂环境科技有限公司 | The online desalination of dangerous waste incineration flue gas washes and reclaiming system and method |
-
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Patent Citations (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN101891330A (en) * | 2010-07-23 | 2010-11-24 | 深圳市能源环保有限公司 | Power plant wastewater treatment system and method |
CN103991997A (en) * | 2014-05-30 | 2014-08-20 | 中国石油集团东北炼化工程有限公司吉林设计院 | Strong brine evaporating and crystallizing system |
CN104341072A (en) * | 2014-11-12 | 2015-02-11 | 湖北加德科技股份有限公司 | Energy-saving waste-water continuous evaporating crystallizing system |
CN104445786A (en) * | 2014-12-15 | 2015-03-25 | 宁波摩尔森膜环保科技有限公司 | Process and device for treating high-concentration salt-containing wastewater |
CN110330165A (en) * | 2019-06-05 | 2019-10-15 | 中国石油天然气集团有限公司 | Strong brine zero-emission and sub-prime crystallizing treatment process and processing system |
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