KR20210082711A - Pervaporation membrane separation process for concentration of the organic compound and treatment of wastewater from specific organic compound containing wastewater - Google Patents
Pervaporation membrane separation process for concentration of the organic compound and treatment of wastewater from specific organic compound containing wastewater Download PDFInfo
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- 150000002894 organic compounds Chemical class 0.000 title claims abstract description 66
- 239000012528 membrane Substances 0.000 title claims abstract description 62
- 239000002351 wastewater Substances 0.000 title claims abstract description 55
- 238000005373 pervaporation Methods 0.000 title claims abstract description 50
- 238000000926 separation method Methods 0.000 title claims abstract description 38
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims abstract description 43
- 238000004065 wastewater treatment Methods 0.000 claims abstract description 15
- KFZMGEQAYNKOFK-UHFFFAOYSA-N Isopropanol Chemical compound CC(C)O KFZMGEQAYNKOFK-UHFFFAOYSA-N 0.000 claims description 69
- SECXISVLQFMRJM-UHFFFAOYSA-N N-Methylpyrrolidone Chemical compound CN1CCCC1=O SECXISVLQFMRJM-UHFFFAOYSA-N 0.000 claims description 51
- ZMXDDKWLCZADIW-UHFFFAOYSA-N N,N-Dimethylformamide Chemical compound CN(C)C=O ZMXDDKWLCZADIW-UHFFFAOYSA-N 0.000 claims description 24
- 238000000034 method Methods 0.000 claims description 21
- 239000012466 permeate Substances 0.000 claims description 18
- IAZDPXIOMUYVGZ-UHFFFAOYSA-N Dimethylsulphoxide Chemical compound CS(C)=O IAZDPXIOMUYVGZ-UHFFFAOYSA-N 0.000 claims description 16
- 230000008569 process Effects 0.000 claims description 12
- OKKJLVBELUTLKV-UHFFFAOYSA-N Methanol Chemical compound OC OKKJLVBELUTLKV-UHFFFAOYSA-N 0.000 claims description 9
- FXHOOIRPVKKKFG-UHFFFAOYSA-N N,N-Dimethylacetamide Chemical compound CN(C)C(C)=O FXHOOIRPVKKKFG-UHFFFAOYSA-N 0.000 claims description 8
- LFQSCWFLJHTTHZ-UHFFFAOYSA-N Ethanol Chemical compound CCO LFQSCWFLJHTTHZ-UHFFFAOYSA-N 0.000 claims description 6
- 239000007791 liquid phase Substances 0.000 claims description 4
- 229910021536 Zeolite Inorganic materials 0.000 claims description 3
- 239000000919 ceramic Substances 0.000 claims description 3
- HNPSIPDUKPIQMN-UHFFFAOYSA-N dioxosilane;oxo(oxoalumanyloxy)alumane Chemical compound O=[Si]=O.O=[Al]O[Al]=O HNPSIPDUKPIQMN-UHFFFAOYSA-N 0.000 claims description 3
- BDERNNFJNOPAEC-UHFFFAOYSA-N propan-1-ol Chemical compound CCCO BDERNNFJNOPAEC-UHFFFAOYSA-N 0.000 claims description 3
- 239000002210 silicon-based material Substances 0.000 claims description 3
- 239000010457 zeolite Substances 0.000 claims description 3
- 238000010790 dilution Methods 0.000 abstract description 6
- 239000012895 dilution Substances 0.000 abstract description 6
- 239000012141 concentrate Substances 0.000 abstract description 3
- 239000000243 solution Substances 0.000 description 16
- 230000035699 permeability Effects 0.000 description 12
- 239000012527 feed solution Substances 0.000 description 9
- 238000004519 manufacturing process Methods 0.000 description 5
- 239000002904 solvent Substances 0.000 description 4
- 239000000126 substance Substances 0.000 description 4
- 230000018044 dehydration Effects 0.000 description 3
- 238000006297 dehydration reaction Methods 0.000 description 3
- 238000010586 diagram Methods 0.000 description 3
- 238000004064 recycling Methods 0.000 description 3
- 239000004065 semiconductor Substances 0.000 description 3
- HBBGRARXTFLTSG-UHFFFAOYSA-N Lithium ion Chemical compound [Li+] HBBGRARXTFLTSG-UHFFFAOYSA-N 0.000 description 2
- -1 NMP Chemical class 0.000 description 2
- 239000000356 contaminant Substances 0.000 description 2
- 238000004821 distillation Methods 0.000 description 2
- 230000000694 effects Effects 0.000 description 2
- 238000005516 engineering process Methods 0.000 description 2
- 239000007788 liquid Substances 0.000 description 2
- 229910001416 lithium ion Inorganic materials 0.000 description 2
- 230000001988 toxicity Effects 0.000 description 2
- 231100000419 toxicity Toxicity 0.000 description 2
- 239000012808 vapor phase Substances 0.000 description 2
- 241000208340 Araliaceae Species 0.000 description 1
- 235000005035 Panax pseudoginseng ssp. pseudoginseng Nutrition 0.000 description 1
- 235000003140 Panax quinquefolius Nutrition 0.000 description 1
- 239000007864 aqueous solution Substances 0.000 description 1
- 239000012159 carrier gas Substances 0.000 description 1
- 239000006182 cathode active material Substances 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 238000004140 cleaning Methods 0.000 description 1
- 239000012459 cleaning agent Substances 0.000 description 1
- 230000007547 defect Effects 0.000 description 1
- 230000001419 dependent effect Effects 0.000 description 1
- 238000001035 drying Methods 0.000 description 1
- 238000005265 energy consumption Methods 0.000 description 1
- 238000001704 evaporation Methods 0.000 description 1
- 230000008020 evaporation Effects 0.000 description 1
- 235000008434 ginseng Nutrition 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 230000008676 import Effects 0.000 description 1
- 239000000463 material Substances 0.000 description 1
- 230000007246 mechanism Effects 0.000 description 1
- 230000010534 mechanism of action Effects 0.000 description 1
- 244000005700 microbiome Species 0.000 description 1
- 239000011259 mixed solution Substances 0.000 description 1
- 239000003960 organic solvent Substances 0.000 description 1
- 239000000575 pesticide Substances 0.000 description 1
- 239000000047 product Substances 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 229920005989 resin Polymers 0.000 description 1
- 239000011347 resin Substances 0.000 description 1
- 238000001291 vacuum drying Methods 0.000 description 1
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Classifications
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D69/00—Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
- B01D69/10—Supported membranes; Membrane supports
- B01D69/108—Inorganic support material
-
- 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
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
- C02F1/448—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis by pervaporation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/36—Pervaporation; Membrane distillation; Liquid permeation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/36—Pervaporation; Membrane distillation; Liquid permeation
- B01D61/362—Pervaporation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D61/00—Processes of separation using semi-permeable membranes, e.g. dialysis, osmosis or ultrafiltration; Apparatus, accessories or auxiliary operations specially adapted therefor
- B01D61/36—Pervaporation; Membrane distillation; Liquid permeation
- B01D61/363—Vapour permeation
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D69/00—Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
- B01D69/10—Supported membranes; Membrane supports
-
- 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
-
- 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
- C02F1/44—Treatment of water, waste water, or sewage by dialysis, osmosis or reverse osmosis
-
- 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
- C02F1/58—Treatment of water, waste water, or sewage by removing specified dissolved compounds
-
- C—CHEMISTRY; METALLURGY
- C02—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F—TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
- C02F2101/00—Nature of the contaminant
- C02F2101/30—Organic compounds
Abstract
Description
본 발명은 특정한 유기화합물 함유 폐수로부터 그 유기화합물의 농축 및 폐수처리를 위한 투과증발막 분리공정에 관한 것으로, 보다 상세하게는 NMP와 같은 특정한 유기화합물이 함유된 폐수로부터 탈수하여 그 특정한 유기화합물을 농축하는 동시에, 폐수를 처리할 수 있는 투과증발막 분리공정에 관한 것이다.The present invention relates to a pervaporation membrane separation process for concentration and wastewater treatment of organic compounds from wastewater containing specific organic compounds, and more particularly, dehydration from wastewater containing specific organic compounds such as NMP to obtain the specific organic compounds. It relates to a pervaporation membrane separation process capable of treating wastewater at the same time as concentration.
일반적으로 유기용매 등의 용도로 널리 사용되고 있는 특정한 유기화합물 중에서 N-메틸피롤리돈(NMP)은 다양한 화학반응의 매체로 유용하며, LCD및 반도체 제조과정의 세정제, 석유화학 산업의 추출제, 고가의 농약용제, 이차전지의 제조공정에도 사용된다. 특히 리튬이온전지의 양극활물질 제조공정에 중요한 용매로 사용되는 NMP는 전량 수입에 의존하고 있으며, BASF와 ISP의 독과점에 따라 높은 가격을 유지하고 있다. 이로 인해 대부분의 리튬이온전지 제조업체들은 양극제조 과정 중 건조과정에서 공기 중에 배기되는 NMP를 회수한 후 재사용하는 방식을 이용하고 있다. 국내에서는 주로 NMP의 친수성을 이용해 습식 스크러버에서 회수하는 방법을 사용하고 있으며, 이 방식으로 회수된 NMP의 순도는 약 60% 수준이다. N-methylpyrrolidone (NMP) is useful as a medium for various chemical reactions among specific organic compounds widely used for purposes such as organic solvents, as a cleaning agent in LCD and semiconductor manufacturing processes, as an extractant in the petrochemical industry, and at high cost. It is also used as a pesticide solvent in the manufacturing process of secondary batteries. In particular, NMP, which is used as an important solvent in the manufacturing process of cathode active materials for lithium-ion batteries, is entirely dependent on imports, and maintains high prices due to the monopoly of BASF and ISPs. For this reason, most lithium-ion battery manufacturers are using the method of recovering the NMP exhausted from the air during the drying process during the cathode manufacturing process and then reusing it. In Korea, a method of recovering from a wet scrubber using the hydrophilicity of NMP is mainly used, and the purity of NMP recovered in this way is about 60%.
한편, 반도체 소자가 초고집적화 되면서 제조 공정 수는 증가되어 왔으며, 각 공정 후에는 많은 잔류물 또는 오염물이 표면에 남게 되어 이것을 제거하는 세정공정에 이소프로필알코올(IPA)을 쓰고 있다. 기존 공정에서는 물을 이용하여 이를 제거하였으나, 물의 표면 장력에 의해 제품의 불량이 발생하여 쉽게 증발하는 성질을 가지고 있는 IPA를 이용하여 반도체 웨이퍼 표면의 오염물을 제거하게 된다. 이러한 IPA 폐수는 기존 증류법을 통한 증발농축으로 가공하는데 많은 비용이 소요되기 때문에 해당 폐수를 재활용하는데 있어 경제성이 크게 떨어지며, IPA가 가지는 독성 때문에 미생물이 사멸되어 기존의 생물학적 처리방법으로는 처리하기가 힘들다. 따라서 이를 효율적으로 농축 및 가공하여 자원을 재활용할 수 있는 기술이 필요한 실정이다. On the other hand, as semiconductor devices are highly integrated, the number of manufacturing processes has increased. After each process, many residues or contaminants are left on the surface, so isopropyl alcohol (IPA) is used in the cleaning process to remove them. In the existing process, water was used to remove it, but the surface tension of water causes product defects to occur, and thus contaminants on the surface of the semiconductor wafer are removed using IPA, which evaporates easily. Since it takes a lot of cost to process such IPA wastewater through evaporation and concentration through the existing distillation method, the economic feasibility of recycling the wastewater is greatly reduced, and the toxicity of IPA kills microorganisms, making it difficult to treat with the existing biological treatment method. . Therefore, there is a need for a technology capable of efficiently concentrating and processing them to recycle resources.
또한, 디메틸아세트아미드(DMAC) 및 디메틸포름아미드(DMF)는 생선 비린내가 나는 무색 액체로 극성 및 비극성물질에 잘 녹으며, 수지류에 대한 용해성이 뛰어난 성질 때문에 합성섬유, 필름제조 및 섬유코팅 등에 사용된다. 디메틸술폭시드(DMSO) 또한 각종 수지의 용매로 사용되며, 이들 용매가 가지고 있는 독성 때문에 그 폐수의 배출에 있어서 큰 제한을 받고 있다. 따라서 이를 재활용하고 처리하는데 있어서도 보다 효율적이고 안전한 기술이 필요하다. In addition, dimethylacetamide (DMAC) and dimethylformamide (DMF) are colorless liquids with a fishy smell, and are well soluble in polar and non-polar substances. used Dimethyl sulfoxide (DMSO) is also used as a solvent for various resins, and due to the toxicity of these solvents, the discharge of wastewater is greatly restricted. Therefore, there is a need for more efficient and safe technology in recycling and disposing of it.
이에 따라 NMP와 같은 유기화합물/물의 혼합용액으로부터 물을 선택적으로 분리하거나 또는 유기화합물을 수용액으로부터 선택적으로 분리하기 위한 선행연구들이 있었지만(특허문헌 1, 2, 3), 대개 증류공정을 이용하거나 역삼투분리막을 이용한 NMP 처리방법 또는 진공건조를 이용한 NMP 회수방법인바, 투과증발막 분리공정을 이용하여 폐수 내 NMP를 회수하는 방법에 대해서는 공지된바 없다. Accordingly, there have been prior studies for selectively separating water from a mixed solution of an organic compound/water such as NMP or for selectively separating an organic compound from an aqueous solution (Patent Documents 1, 2, 3), but mostly using a distillation process or reverse ginseng Since it is a NMP treatment method using a permeation membrane or a NMP recovery method using vacuum drying, a method for recovering NMP in wastewater using a pervaporation membrane separation process is not known.
따라서 본 발명자는, 농축하여 재활용하거나 또는 폐수처리하기에 적합하지 않은 농도의 NMP와 같은 특정의 유기화합물을 함유하는 폐수로부터 그 특정의 유기화합물을 농축하고, 동시에 처리수의 유기화합물의 농도를 폐수처리에 적정한 농도로 분리할 수 있는 투과증발막 분리공정을 개발하여 본 발명을 완성하기에 이르렀다. Therefore, the present inventor concentrates the specific organic compound from wastewater containing a specific organic compound such as NMP at a concentration not suitable for concentrating and recycling or wastewater treatment, and simultaneously adjusting the concentration of the organic compound in the treated water to the wastewater. The present invention was completed by developing a pervaporation membrane separation process capable of separating at a concentration suitable for treatment.
본 발명은 상기와 같은 문제점을 감안하여 안출된 것으로, 본 발명의 목적은 NMP와 같은 특정한 유기화합물을 함유하는 폐수로부터 그 특정한 유기화합물을 선택적으로 분리, 70.0~99.0 중량%까지 유기화합물을 고농도로 농축하여 재활용할 수 있고, 동시에 분리된 0.5 중량% 이하 낮은 농도의 유기화합물 함유 투과수는 희석 및 별도의 수처리 없이 폐수처리장에서 그대로 처리할 수 있는 투과증발막 분리공정을 제공하고자 하는 것이다.The present invention has been devised in view of the above problems, and an object of the present invention is to selectively separate a specific organic compound from wastewater containing a specific organic compound such as NMP, and to concentrate the organic compound up to 70.0 to 99.0% by weight. An object of the present invention is to provide a pervaporation membrane separation process that can be concentrated and recycled, and the separated permeate containing organic compounds with a low concentration of 0.5 wt% or less can be treated as it is in a wastewater treatment plant without dilution and separate water treatment.
상기한 바와 같은 목적을 달성하기 위한 본 발명은, 특정한 유기화합물을 함유하는 폐수로부터 투과증발막에 의하여 수분을 탈수, 및 그 특정한 유기화합물을 70.0~99.0 중량%의 농도로 농축하는 것을 특징으로 하는 투과증발막 분리공정을 제공한다.The present invention for achieving the above object is characterized in that moisture is dehydrated from wastewater containing a specific organic compound by a pervaporation membrane, and the specific organic compound is concentrated to a concentration of 70.0 to 99.0 wt% A pervaporation membrane separation process is provided.
상기 투과증발막 분리공정은 (I) 승온된 특정한 유기화합물 함유 폐수를 투과증발막 모듈에 공급하는 단계; (II) 분리막에 의해 투과된 수분을 액체상으로 응축하는 단계; (III) 응축된 수분을 처리수 탱크 또는 폐수처리시설로 이송하는 단계; 및 (IV) 수분이 분리되어 농축된 그 특정한 유기화합물을 농축 탱크 또는 유입 탱크로 이송하는 단계;를 포함하는 것을 특징으로 한다.The pervaporation membrane separation process comprises the steps of: (I) supplying a specific organic compound-containing wastewater with an elevated temperature to the pervaporation membrane module; (II) condensing the water permeated by the separation membrane into a liquid phase; (III) transferring the condensed water to a treated water tank or a waste water treatment facility; and (IV) transferring the specific organic compound, wherein the water is separated and concentrated, to a concentration tank or an inlet tank.
상기 승온된 특정한 유기화합물 함유 폐수는 히터에 의하여 70~130℃로 유지된 것을 특징으로 한다.The elevated temperature of the specific organic compound-containing wastewater is characterized in that it is maintained at 70 ~ 130 ℃ by a heater.
상기 투과증발막 모듈에 공급하는 특정한 유기화합물 함유 폐수의 공급유량은 투과유량의 10배 이상인 것을 특징으로 한다. The supply flow rate of the specific organic compound-containing wastewater supplied to the pervaporation membrane module is 10 times or more of the permeate flow rate.
상기 투과증발막 모듈을 통해 농축용액으로 회수되는 특정한 유기화합물의 농도는 70~99.9 중량%인 것을 특징으로 한다.The concentration of the specific organic compound recovered as a concentrated solution through the pervaporation membrane module is characterized in that 70 ~ 99.9% by weight.
상기 (III) 단계에서 투과되어 탈수된 수분 내의 특정한 유기화합물의 농도는 0.5 중량% 이하인 것을 특징으로 한다.It is characterized in that the concentration of a specific organic compound in the water permeated and dehydrated in step (III) is 0.5 wt% or less.
상기 특정한 유기화합물은 N-메틸피롤리돈(NMP), 디메틸포름아미드(DMF), 디메틸아세트아미드(DMAC), 디메틸술폭시드(DMSO), 이소프로필알코올(IPA), 메탄올, 에탄올 또는 프로판올인 것을 특징으로 한다. The specific organic compound is N-methylpyrrolidone (NMP), dimethylformamide (DMF), dimethylacetamide (DMAC), dimethyl sulfoxide (DMSO), isopropyl alcohol (IPA), methanol, ethanol or propanol. characterized.
상기 투과증발막은 세라믹계 다공성 지지체에 제올라이트 또는 실리콘계 물질이 부착된 것을 특징으로 한다. The pervaporation membrane is characterized in that the zeolite or silicon-based material is attached to the ceramic-based porous support.
본 발명의 투과증발막 분리공정에 따르면, NMP와 같은 특정한 유기화합물을 함유하는 폐수로부터 탈수, 및 그 특정한 유기화합물을 선택적으로 분리함으로써 70.0~99.0 중량%까지 유기화합물을 고농도로 농축하여 재활용 할 수 있고, 동시에 0.5 중량% 이하의 낮은 농도의 유기화합물 함유 폐수는 별도의 희석 및 추가적인 수처리 없이 기존의 폐수처리장에서 처리할 수 있다.According to the pervaporation membrane separation process of the present invention, dehydration from wastewater containing a specific organic compound such as NMP, and selectively separating the specific organic compound can be recycled by concentrating the organic compound to a high concentration of 70.0 to 99.0 wt%. At the same time, wastewater containing organic compounds at a low concentration of 0.5 wt% or less can be treated in an existing wastewater treatment plant without separate dilution and additional water treatment.
도 1은 본 발명에 따라 특정한 유기화합물을 함유하는 폐수로부터 그 특정한 유기화합물을 선택적으로 분리 및 농축하는 투과증발막 분리공정도를 나타낸 블록 다이어그램.1 is a block diagram showing a pervaporation membrane separation process for selectively separating and concentrating a specific organic compound from wastewater containing a specific organic compound according to the present invention;
이하에서는 본 발명에 따라 특정한 유기화합물을 함유하는 폐수로부터 그 특정한 유기화합물을 70.0~99.0 중량%까지 농축하고, 동시에 그 특정한 유기화합물의 농도를 폐수처리에 적정한 농도로 분리하는 투과증발막 분리공정에 관하여 첨부된 도면과 함께 상세히 설명하기로 한다.Hereinafter, according to the present invention, the specific organic compound is concentrated to 70.0-99.0 wt% from wastewater containing a specific organic compound, and at the same time, the concentration of the specific organic compound is separated into a concentration suitable for wastewater treatment. It will be described in detail together with the accompanying drawings.
본 발명은 특정한 유기화합물을 함유하는 폐수로부터 투과증발막에 의하여 수분을 탈수, 및 그 특정한 유기화합물을 70.0~99.0 중량%의 농도로 농축하는 것을 특징으로 하는 투과증발막 분리공정을 제공하는데, 상기 투과증발막 분리공정은 (I) 승온된 특정한 유기화합물 함유 폐수를 투과증발막 모듈에 공급하는 단계; (II) 분리막에 의해 투과된 수분을 액체상으로 응축하는 단계; (III) 응축된 수분을 처리수 탱크 또는 폐수처리시설로 이송하는 단계; 및 (IV) 수분이 분리되어 농축된 그 특정한 유기화합물을 농축 탱크 또는 유입 탱크로 이송하는 단계;를 포함한다.The present invention provides a pervaporation membrane separation process characterized in that moisture is dehydrated from wastewater containing a specific organic compound by a pervaporation membrane, and the specific organic compound is concentrated to a concentration of 70.0 to 99.0 wt%, wherein the The pervaporation membrane separation process comprises the steps of (I) supplying a specific organic compound-containing wastewater that has been heated to a pervaporation membrane module; (II) condensing the water permeated by the separation membrane into a liquid phase; (III) transferring the condensed water to a treated water tank or a waste water treatment facility; and (IV) transferring the specific organic compound, wherein the water is separated and concentrated, to a concentration tank or an inlet tank.
도 1에는 본 발명에 따라 특정한 유기화합물을 함유하는 폐수로부터 그 특정한 유기화합물을 선택적으로 분리 및 농축하는 투과증발막 분리공정도를 블록 다이어그램으로 나타내었는바, 도 1에 나타낸 공정도를 바탕으로 본 발명의 일 구현예를 설명하기로 한다.1 is a block diagram showing a pervaporation membrane separation process for selectively separating and concentrating a specific organic compound from wastewater containing a specific organic compound according to the present invention. Based on the process diagram shown in FIG. 1, the present invention An embodiment will be described.
먼저, 특정한 유기화합물로서 NMP를 함유하는 폐수(용액)를 NMP 폐수 탱크(100)에 저장한다. 저장된 NMP를 함유하는 폐수는 라인필터(110)에서 이물질이 1차적으로 분리되고, 공급펌프(120)에 의해 이송된 NMP를 함유하는 폐수는 통상 히터(130)와 같은 가열수단에 의하여 승온된다. 이때, NMP를 함유하는 폐수 용액의 온도가 70℃미만이면 투과증발막 모듈의 투과량이 너무 작아지고, 그 온도가 130℃를 초과하면 에너지 소모가 너무 커지므로, NMP를 함유하는 폐수는 히터(130)에 의하여 승온되어 70~130℃로 유지하는 것이 바람직하다. First, wastewater (solution) containing NMP as a specific organic compound is stored in the
이어서 70~130℃로 승온된 NMP를 함유하는 폐수는 투과증발막 모듈(150)에 공급되는데, 여기서 유입 유량계(140)를 거치는 과정이 수반된다. 이때, 투과증발막 모듈(150)에 공급하는 NMP를 함유하는 폐수의 공급유량은 투과유량의 10배 이상으로 조절하는 것이 바람직하다. 만약 NMP를 함유하는 폐수를 투과증발막 모듈(150)에 10배 이하로 공급하면 투과증발막 모듈(150)을 투과하는 투과폐수의 유량이 낮아 분리 및 농축이 원활히 수행되지 않는다.Then, the wastewater containing NMP heated to 70 ~ 130 ℃ is supplied to the pervaporation membrane module 150, where it is accompanied by the process of going through the inflow flow meter (140). At this time, the supply flow rate of the wastewater containing NMP supplied to the pervaporation membrane module 150 is preferably controlled to be 10 times or more of the permeate flow rate. If the wastewater containing NMP is supplied to the pervaporation membrane module 150 at 10 times or less, the flow rate of the permeate wastewater passing through the pervaporation membrane module 150 is low, so that separation and concentration are not performed smoothly.
이렇게 투과증발막 모듈(150)에 공급된 NMP를 함유하는 폐수는 분리막 내에 물이 선택적으로 용해되고, 분리막 내에서 확산되어 증기상으로 투과하는 작용기전을 갖는다. 이러한 작용기전은 투과증발막 모듈(150)의 일단이 NMP 공급폐수와 접하고 있고, 다른 일단이 낮은 투과물의 증기압과 접하고 있는데, 낮은 증기압 조건은 진공을 걸어 주거나 불활성 담체가스를 흐르게 하여 만들 수 있는 바, 일반적으로 투과증발막 내부에 투과증발막 분리공정의 추진력(driving force)인 화학적 포텐셜의 구배가 발생하여 막을 통한 물질의 투과가 이루어지는 것이므로, 본 발명에서는 투과증발막 분리공정의 추진력을 유지하기 위하여 진공펌프(180)를 사용함으로써 진공이 유지되도록 한다. In this way, the wastewater containing NMP supplied to the pervaporation membrane module 150 has a mechanism in which water is selectively dissolved in the separation membrane, diffuses in the separation membrane, and permeates in the vapor phase. This mechanism of action is that one end of the pervaporation membrane module 150 is in contact with the NMP supply wastewater and the other end is in contact with the vapor pressure of the low permeate. The low vapor pressure condition can be made by applying a vacuum or allowing an inert carrier gas to flow. , in general, since a gradient of chemical potential, which is the driving force of the pervaporation membrane separation process, occurs inside the pervaporation membrane, and the material permeates through the membrane, in the present invention, in order to maintain the driving force of the pervaporation membrane separation process A vacuum is maintained by using the
다음으로, 투과증발막 모듈(150)을 투과한 증기상의 투과수는 통상의 응축기(170)에서 액체상으로 응축되고, 응축된 액상의 투과수는 투과수 유량계(200)를 거쳐 투과수 탱크(210)로 이송된다.
Next, the vapor-phase permeated water that has passed through the pervaporation membrane module 150 is condensed into a liquid phase in a
투과증발막 모듈(150)에 의해 수분이 탈수된 NMP 폐수는 다시 NMP 폐수 탱크(100)로 이송되어 특정 농도에 도달할 때까지 일련의 과정이 되풀이된다. 특정 농도에 도달된 NMP 폐수 탱크의 NMP는 농축 NMP 탱크(190)로 이송되고, 이때 라인필터(160)을 거쳐 혹시 있을지 모를 이물질을 제거한다. 이 투과증발막 분리공정을 통하여 얻어지는 NMP 용액의 농도는 70.0~99.0 중량%로 농축되므로 재활용할 수 있다. 아울러 0.5 중량% 이하의 낮은 농도의 NMP 함유 폐수는 별도의 희석 및 추가적인 수처리 없이 기존의 폐수처리장에서 처리할 수 있다.
The NMP wastewater dehydrated by the pervaporation membrane module 150 is transferred to the
또한, 상기 일 구현예의 투과증발막 분리공정에 사용되는 투과증발막으로서는 세라믹계 다공성 지지체에 제올라이트 또는 실리콘계 물질이 부착된 것일 수 있으나, 이에 제한되지 않는다.In addition, as the pervaporation membrane used in the separation process of the pervaporation membrane of the embodiment, a zeolite or a silicon-based material may be attached to a ceramic-based porous support, but is not limited thereto.
그리고 상기 일 구현에에서는 특정한 유기화합물을 함유하는 폐수 중의 유기화합물이 NMP인 것을 채택하였으나, 그 특정한 유기화합물은 NMP 이외에도 디메틸포름아미드(DMF), 디메틸아세트아미드(DMAC), 디메틸술폭시드(DMSO), 이소프로필알코올(IPA), 메탄올, 에탄올 또는 프로판올일 수 있다. And in the above embodiment, the organic compound in the wastewater containing a specific organic compound is NMP, but the specific organic compound is dimethylformamide (DMF), dimethylacetamide (DMAC), dimethyl sulfoxide (DMSO) in addition to NMP. , isopropyl alcohol (IPA), methanol, ethanol or propanol.
이하 구체적인 실시예를 상세히 설명한다.Hereinafter, specific examples will be described in detail.
(실시예 1)(Example 1)
NMP 함유 폐수의 NMP 농도를 60 중량%, 공급유량을 1.0 LPM(liter per minute)으로 고정하고, 공급용액의 온도를 90℃로 유지한 채 투과증발막 분리공정을 수행하였으며, 표 1에 투과증발막 분리공정에 의한 NMP 농도에 따른 투과용액의 수투과도와 유입농도에서 농축용액까지의 평균수투과도를 나타내었다. The NMP concentration of the NMP-containing wastewater was fixed at 60 wt %, the feed flow rate was fixed at 1.0 LPM (liter per minute), and the pervaporation membrane separation process was performed while maintaining the temperature of the feed solution at 90 ° C. The water permeability of the permeate solution according to the NMP concentration by the membrane separation process and the average water permeability from the inlet concentration to the concentrated solution were shown.
(℃)Feed solution temperature
(℃)
(중량%) NMP concentration of the concentrated solution
(weight%)
(kg/m2·hr)water permeability
(kg/m 2 hr)
(kg/m2·hr)Average water permeability
(kg/m 2 hr)
(실시예 2)(Example 2)
NMP 함유 폐수의 NMP 농도를 60 중량%, 공급유량을 2.0 LPM(liter per minute)으로 고정하고, 공급용액의 온도를 110℃로 유지한 채 투과증발막 분리공정을 수행하였으며, 표 2에 투과증발막 분리공정에 의한 NMP 농도에 따른 투과용액의 수투과도와 유입농도에서 농축용액까지의 평균수투과도를 나타내었다.The NMP concentration of the NMP-containing wastewater was fixed at 60 wt%, the feed flow rate was set to 2.0 LPM (liter per minute), and the pervaporation membrane separation process was performed while the temperature of the feed solution was maintained at 110 °C. The water permeability of the permeate solution according to the NMP concentration by the membrane separation process and the average water permeability from the inlet concentration to the concentrated solution were shown.
(℃)Feed solution temperature
(℃)
(중량%) NMP concentration of the concentrated solution
(weight%)
(kg/m2·hr)water permeability
(kg/m 2 hr)
(kg/m2·hr)Average water permeability
(kg/m 2 hr)
(실시예 3)(Example 3)
IPA 함유 폐수의 IPA 농도를 50 중량%, 공급유량을 1.0 LPM(liter per minute)으로 고정하고, 공급용액의 온도를 100℃로 유지한 채 투과증발막 분리공정을 수행하였으며, 표 3에 투과증발막 분리공정에 의한 시간에 따른 IPA 농도와 수투과도를 나타내었다.The IPA concentration of the IPA-containing wastewater was fixed at 50 wt% and the feed flow rate was set to 1.0 LPM (liter per minute), and the pervaporation membrane separation process was performed while maintaining the temperature of the feed solution at 100 ° C. IPA concentration and water permeability according to time by the membrane separation process were shown.
상기 표 1 내지 3에서 보는 바와 같이, 본 발명의 실시예 1 내지 3에 따른 투과증발막 분리공정에 의하면 공급용액의 온도가 높을수록 수투과도가 증가하고, 공급유량이 높을수록 수투과도가 증가하는 것을 알 수 있다. 또한 어느 경우에서나 투과용액의 NMP, IPA 농도가 모두 0.5 중량% 이하로 나타나 투과용액을 추가적인 수처리 없이 기존의 폐수처리장에서 처리할 수 있음을 확인하였다. As shown in Tables 1 to 3, according to the pervaporation membrane separation process according to Examples 1 to 3 of the present invention, the higher the temperature of the feed solution, the higher the water permeability, and the higher the feed flow rate, the higher the water permeability. it can be seen that Also, in all cases, the NMP and IPA concentrations of the permeate solution were all 0.5 wt% or less, confirming that the permeate solution could be treated in the existing wastewater treatment plant without additional water treatment.
따라서 본 발명의 투과증발막 분리공정에 따르면, NMP외 유기화합물 폐수로부터 NMP외 유기화합물을 선택적으로 분리 및 70.0~99.0 중량%이상 농축하여 재활용할 수 있고, 동시에 0.5 중량% 이하의 낮은 동도의 NMP외 유기화합물 투과용액은 별도의 희석 및 추가 수처리 없이 기존의 폐수처리장에서 그대로 처리할 수 있는 현저한 효과를 나타낸다.Therefore, according to the pervaporation membrane separation process of the present invention, organic compounds other than NMP can be selectively separated from the wastewater of organic compounds other than NMP and concentrated to 70.0-99.0% by weight or more, and recycled, and at the same time, NMP of low homogeneity of 0.5% by weight or less The organic compound permeation solution exhibits a remarkable effect that it can be treated as it is in the existing wastewater treatment plant without additional dilution and additional water treatment.
표 1 및 2에서 보는 바와 같이, 본 발명의 실시예 1, 2에 따른 증기투과막 분리공정에 의하면, 공급용액의 온도가 100~120℃일 때, IPA 함유 폐수로부터 농축된 IPA의 농도는 90.0~99.9 중량%까지 고농도를 나타내어 IPA를 재활용 할 수 있음을 확인하였으며, 또한 공급용액의 IPA 농도가 높을수록 농축용액의 IPA 농도가 증가하고 투과유량이 감소함을 알 수 있다. 한편, 공급용액의 IPA 농도에 상관없이 어느 경우에서나 투과용액의 IPA 농도가 0.2 중량%에 불과하므로 투과용액(투과수)을 그대로 폐수처리장으로 이송하여 폐수처리 할 수 있음도 확인하였다.As shown in Tables 1 and 2, according to the vapor permeation membrane separation process according to Examples 1 and 2 of the present invention, when the temperature of the feed solution is 100 to 120° C., the concentration of IPA concentrated from the IPA-containing wastewater is 90.0 It was confirmed that IPA can be recycled by showing a high concentration of ~99.9% by weight. In addition, it can be seen that the higher the IPA concentration of the feed solution, the higher the IPA concentration of the concentrated solution and the decrease of the permeate flow rate. On the other hand, it was also confirmed that the permeate solution (permeate water) could be transferred to a wastewater treatment plant as it is for wastewater treatment because the IPA concentration of the permeate solution was only 0.2% by weight in any case regardless of the IPA concentration of the feed solution.
따라서 본 발명의 증기투과막 분리공정에 따르면, NMP와 같은 특정한 유기화합물을 함유하는 폐수로부터 탈수, 및 그 특정한 유기화합물을 선택적으로 분리함으로써 70.0~99.0 중량%까지 유기화합물을 고농도로 농축하여 재활용 할 수 있고, 동시에 0.5 중량% 이하의 낮은 농도의 유기화합물 함유 폐수는 별도의 희석 및 추가적인 수처리 없이 기존의 폐수처리장에서 그대로 처리할 수 있는 현저한 효과를 나타낸다.Therefore, according to the vapor permeation membrane separation process of the present invention, dehydration from wastewater containing a specific organic compound such as NMP and selectively separating the specific organic compound can be recycled by concentrating the organic compound to a high concentration of 70.0 to 99.0 wt%. At the same time, wastewater containing organic compounds at a low concentration of 0.5% by weight or less exhibits a remarkable effect that it can be treated as it is in the existing wastewater treatment plant without separate dilution and additional water treatment.
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