TW201306930A - Porous polymer membrane for discharge water treatment - Google Patents

Porous polymer membrane for discharge water treatment Download PDF

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TW201306930A
TW201306930A TW101125798A TW101125798A TW201306930A TW 201306930 A TW201306930 A TW 201306930A TW 101125798 A TW101125798 A TW 101125798A TW 101125798 A TW101125798 A TW 101125798A TW 201306930 A TW201306930 A TW 201306930A
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membrane
film
polymer
porous
porous polymer
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TW101125798A
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Junsuke Morita
Akina Taji
Tooru Kitagawa
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Toyo Boseki
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F3/00Biological treatment of water, waste water, or sewage
    • C02F3/02Aerobic processes
    • C02F3/12Activated sludge processes
    • C02F3/1236Particular type of activated sludge installations
    • C02F3/1268Membrane bioreactor systems
    • C02F3/1273Submerged membrane bioreactors
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D69/00Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
    • B01D69/02Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor characterised by their properties
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D69/00Semi-permeable membranes for separation processes or apparatus characterised by their form, structure or properties; Manufacturing processes specially adapted therefor
    • B01D69/06Flat membranes
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D71/00Semi-permeable membranes for separation processes or apparatus characterised by the material; Manufacturing processes specially adapted therefor
    • B01D71/06Organic material
    • B01D71/30Polyalkenyl halides
    • B01D71/301Polyvinylchloride
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

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  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Biodiversity & Conservation Biology (AREA)
  • Microbiology (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Separation Using Semi-Permeable Membranes (AREA)

Abstract

The object of the present invention is to provide a flat film of a porous polymer membrane for MBR method having a structure of that can keep sufficient strength suitable for using in a discharge water treatment for a long term and also has high membrane performance. The solution means of the present invention is a porous polymer membrane. The porous polymer membrane is a flat membrane immersed in an actived sludge to obtain a filtration from the actived sludge, and is characterized by satisfying conditions of (A) to (E) as follows: (A) the pure water flux is 20 to 50mL/cm<SP>2</SP>/min/bar; (B) the bubble point in pure water is 0.08 to 0.3MPa; (C) the porous polymer membrane comprises a polyvinyl chloride and / or a chlorinated polyvinyl chloride; (D) in the observation of a surface of the porous polymer membrane contacted with a liquid to be treated through a 5000 times electron microscope, it is found that the porous polymer membrane has 25 to 45% of aperture ratio of the membrane surface, 0.2 to 1.0 μ m average fine-pore diameter, and 0.5 to 5 numbers of fine-pores occurred in 1 μ m<SP>2</SP>; (E) in the observation of a membrane cross section of the porous polymer membrane through a 5000 times electron microscope, it is found that the structure becomes gradually loosen from the surface contacted with a liquid to be treated to the inner layer portion; and the porosity of a polymer network of the inner layer portion is 1 to 3 times with respect to that of surface nearby the portion contacted with the liquid to be treated.

Description

排水處理用高分子多孔質膜 Polymer porous membrane for drainage treatment

本發明係關於一種適合以膜分離活性污泥法(MBR,membrane Bio-reactor,薄膜生物反應器)進行排水處理之平膜的高分子多孔質膜。 The present invention relates to a polymer porous membrane suitable for a flat membrane which is subjected to a wastewater treatment by a membrane separation activated sludge method (MBR).

近年來,在世界人口增加、工業化、都市化、生活水平提升的背景下,生活用水與工業用水所必要的質、量正逐漸提高。 In recent years, in the context of increasing world population, industrialization, urbanization, and rising living standards, the quality and quantity necessary for domestic and industrial water use are gradually increasing.

一般而言,水資源的確保除了利用過去從自然所得到之天然水以外,還有利用蒸發法與逆滲透法從海水得到淡水之方法,或者利用逆滲透現象從含有鹽分之鹵水得到淡水之方法。然而,天然存在的淡水資源有限,且由於近年天候異常的影響,可利用性可說有越來越狹隘的傾向。此外,為了使用蒸發法與逆滲透來製造淡水,由於需要用於加熱或加壓之能量,而使能利用的地域受限。 In general, water resources are ensured by the use of natural water obtained from nature in the past, as well as the method of obtaining fresh water from seawater by evaporation and reverse osmosis, or by using reverse osmosis to obtain fresh water from brine containing salt. . However, natural freshwater resources are limited, and due to the impact of weather anomalies in recent years, availability is increasingly narrow. Further, in order to produce fresh water using an evaporation method and reverse osmosis, since the energy for heating or pressurization is required, the area in which utilization is enabled is limited.

至於其它方法,還有污水再利用之方向。過去的污水處理係藉由活性污泥分解處理污水中的有機成分,再經過沉澱過濾等放流處理水,但在完全除去大腸桿菌等菌群上有困難。然而,膜分離活性污泥法因使用分離膜過濾經過以活性污泥處理過的水,而可能完全去除上述有害菌群,且有設備精巧與容易管理運作等多項優點,而成為近年非常引人注目的技術。經過以膜分離活性污泥法分離過的水不僅可利用做為生活景觀維持水或中水(Reclaimed water),藉由配合逆滲透法亦能得到自來水。相對於對海水使用逆滲透法有對抗鹽分濃度之高壓的必要,將以膜分離活性污泥法所得到的處理水利用做為原水,有 著能安全且低能量地造水之特徵。 As for other methods, there is also the direction of sewage reuse. In the past, sewage treatment was carried out by decomposing the organic components in the sewage by activated sludge, and then discharging the treated water by precipitation filtration or the like, but it was difficult to completely remove the bacteria such as Escherichia coli. However, the membrane separation activated sludge method is very attractive in recent years because it uses a separation membrane to filter water treated with activated sludge, and may completely remove the above-mentioned harmful microflora, and has many advantages such as exquisite equipment and easy management operation. Attention technology. The water separated by the membrane separation activated sludge method can be used not only as a living landscape to maintain water or reclaimed water, but also by tapping the reverse osmosis method. It is necessary to use the treated water obtained by the membrane separation activated sludge method as the raw water, as opposed to the use of the reverse osmosis method for seawater to have a high pressure against the salt concentration. A feature that makes water safe and low-energy.

因此,膜分離活性污泥法做為解決未來預想之水量不足之方法而備受矚目。而為了進一步改良此方法,以低成本完成高效率的系統,需要在維持著膜的分離性能的同時,還能確保透水性能。下面指出使用於膜分離活性污泥法的膜所要求的一般特性。 Therefore, the membrane separation activated sludge method has attracted attention as a method for solving the shortage of water expected in the future. In order to further improve this method, it is necessary to maintain a high-efficiency system at a low cost, while maintaining the separation performance of the membrane while ensuring water permeability. The general characteristics required for the membrane used in the membrane separation activated sludge process are indicated below.

首先,膜分離活性污泥法因係將無覆蓋物的膜浸漬於活性污泥中使用,與其它技術領域的分離膜相比係更嚴酷的使用形態。因此,要求足堪使用之物理強度。更具體來說,為了即便在活性污泥中受到各種夾雑物的衝撃,或在過濾時膜間壓力差(TMP)上昇等,膜也不會產生破損或變形,性能也不會降低,必須有高強度與不易拉伸的膜特性。 First, the membrane separation activated sludge method uses a membrane without a covering to be immersed in activated sludge, and is more severely used than a separation membrane of other technical fields. Therefore, the physical strength required is sufficient. More specifically, in order to be damaged by various kinds of inclusions in the activated sludge, or when the pressure difference between the membranes (TMP) increases during filtration, the membrane is not damaged or deformed, and the performance is not lowered. High strength and film properties that are not easily stretched.

其次,膜若長期在浸漬於活性污泥的狀態下使用,由於活性污泥產生的分泌物與其遺骸、污泥中所含的夾雜物等會堵塞住孔,讓透水性能降低,而為了對應於此則會產生提高幫浦壓力的必要。此稱之為積垢(fouling),為在使用膜時最大的問題,而對於此問題,能進行藉由使用次氯酸鈉或鹽酸等藥劑來洗淨膜來解決積垢,讓膜回到新鮮的狀態之操作。因此,膜對此等藥劑不會劣化的抗藥液性同樣是重要的。 Next, if the membrane is used in a state of being immersed in activated sludge for a long period of time, the secretions generated by the activated sludge and the remains contained in the sludge, etc., may block the pores, thereby lowering the water permeability, and corresponding to This will create the need to increase the pressure on the pump. This is called fouling, which is the biggest problem when using a film. For this problem, it is possible to clean the membrane by using a drug such as sodium hypochlorite or hydrochloric acid to solve the fouling and return the membrane to a fresh state. Operation. Therefore, it is also important that the film is resistant to liquid chemicals in which the agents do not deteriorate.

然而,此等藥劑的洗淨操作有著在當下無法運作過濾、藥劑成本與作業工序、藥劑的排液處理等,在經濟面與生態環境面的許多問題。因此,減少藥劑的洗淨操作、如何來防止積垢、更能長時間使用成為了最大的課題。 However, the cleaning operation of these chemicals has many problems in the economical and ecological environment, such as the inability to operate the filtration at present, the cost of the medicine, the operation process, and the liquid discharge treatment of the medicine. Therefore, it has become the biggest problem to reduce the cleaning operation of the drug, how to prevent fouling, and to use it for a long time.

考慮到如此之透水性問題的MBR用膜,已提案使用氯化聚氯乙烯或聚偏二氟乙烯系樹脂來做為膜原料(參照專利文獻 1、2)。具體來說,在專利文獻1中,係把聚酯不織布含浸於將氯化聚氯乙烯溶解於四氫呋喃再於其中進一步添加異丙醇與蔗糖酯而成的溶液後,經過乾燥產生相分離形成微孔體。另外,在專利文獻2中,係製作包含耐藥品性優良之聚偏二氟乙烯、聚甲基丙烯酸甲酯、與聚乙烯吡咯烷酮的接枝共聚物、N,N-二甲基乙醯胺、聚乙烯醇的製膜原料液,將其塗布在聚酯不織布,經過含浸於水凝固浴中,得到形成了多孔樹脂層的多孔基材。 In view of such a water permeable membrane for MBR, it has been proposed to use chlorinated polyvinyl chloride or polyvinylidene fluoride resin as a film material (refer to the patent literature). 1, 2). Specifically, in Patent Document 1, a polyester nonwoven fabric is impregnated with a solution obtained by dissolving chlorinated polyvinyl chloride in tetrahydrofuran and further adding isopropanol and sucrose ester, and drying to form a phase separation to form a microparticle. Hole body. Further, in Patent Document 2, a polyvinylidene fluoride, a polymethyl methacrylate, a graft copolymer with polyvinylpyrrolidone, and N,N-dimethylacetamide, which are excellent in chemical resistance, are produced. A film forming raw material liquid of polyvinyl alcohol is applied to a polyester nonwoven fabric and impregnated into a water coagulation bath to obtain a porous substrate in which a porous resin layer is formed.

然而,使用上述過去之氯化聚氯乙烯的膜,無法說已將開孔率提高到極限,又親水化的程度、特別是在維持長時間使用時的親水性上有問題。另一方面,若是以氯化聚氯乙烯以外之材料做為具耐藥品性的原料則會限制製膜方法,要以設備投資少、能容易製膜的乾式方法來製膜實際上不可能。例如聚偏二氟乙烯系樹脂的平膜在耐藥品性與微孔密度的點上優良,而由溶媒、非溶媒的選擇關係,能以濕式方法或熱誘導式相分離法製膜。依照濕式法,由於有在膜表面形成皮層、在膜內部形成大空隙的傾向,而不易得到充分的性能與強度。而依照熱誘導式相分離法,由於會因溫度變化形成膜孔,而必須要嚴密的溫度管理,使得設備投資增加,高溫作業的災害風險亦高。此外,因相對於聚氯乙烯系樹脂,聚合物價格非常高,而有讓工業生產上的成本變高之問題。 However, the use of the above-mentioned conventional chlorinated polyvinyl chloride film cannot be said to have increased the opening ratio to the limit, and the degree of hydrophilization, particularly the hydrophilicity at the time of maintaining long-term use. On the other hand, if a material other than chlorinated polyvinyl chloride is used as a raw material having chemical resistance, the film forming method is limited, and it is practically impossible to form a film by a dry method in which equipment investment is small and film formation can be easily performed. For example, a flat film of a polyvinylidene fluoride-based resin is excellent in chemical resistance and micropore density, and a solvent or a non-solvent can be selected by a wet method or a thermally induced phase separation method. According to the wet method, since a skin layer is formed on the surface of the film and a large void is formed inside the film, sufficient performance and strength are not easily obtained. According to the heat-induced phase separation method, since the membrane pores are formed due to temperature changes, strict temperature management is required, resulting in an increase in equipment investment and a high disaster risk in high-temperature operation. Further, since the price of the polymer is very high with respect to the polyvinyl chloride resin, there is a problem that the cost in industrial production becomes high.

〔先行技術文獻〕 [prior technical literature] 〔專利文獻〕 [Patent Document]

專利文獻1 日本特開昭58-88011號公報 Patent Document 1 Japanese Patent Laid-Open No. 58-88011

專利文獻2 日本特開2006-205067號公報 Patent Document 2 Japanese Patent Laid-Open Publication No. 2006-205067

本發明有鑑於如此之過去技術的現狀,以提供能維持足以承受適合長期使用於排水處理的強度,並且具優良的膜性能之構造的MBR用平膜之高分子多孔質膜為其目的。 In view of the current state of the art, the present invention has an object of providing a polymer porous film for a flat film of MBR capable of maintaining a structure suitable for long-term use in drainage treatment and having excellent film properties.

本發明人為達成上述目的而專注研究的結果,發現在選擇能承受長時間使用之強度的膜基材與膜原料的基礎上,藉由採用在維持高表面開孔率與孔徑的同時不易附著污泥之表面特性且讓內層部適度鬆散之構造等,而能提供可長時間維持高的膜性能與強度之MBR用平膜的高分子多孔質膜,乃至完成本發明。 As a result of intensive research to achieve the above object, the present inventors have found that on the basis of selecting a film substrate and a film material which can withstand the strength for a long period of use, it is difficult to adhere to the film while maintaining a high surface opening ratio and a pore diameter. The polymer porous film of the MBR flat film which can maintain high film performance and strength for a long period of time can be provided to the surface of the mud, and the structure of the inner layer is appropriately loosened.

即,本發明具有以下(1)~(8)之構成。 That is, the present invention has the following configurations (1) to (8).

(1)一種高分子多孔質膜,其係用於浸漬於活性污泥中,並自活性污泥液中得到濾液的平膜之高分子多孔質膜,其特徵為滿足下述A)~E)之條件:A)純水通量為20~50mL/cm2/min/bar;B)在純水中的起泡點為0.08~0.3MPa;C)高分子多孔質膜係由聚氯乙烯及/或氯化聚氯乙烯所構成;D)在以5000倍電子顯微鏡觀察高分子多孔質膜的與被處理液接觸之表面時,膜表面開孔率為25~45%,平均細孔徑為0.2~1.0μm,於1平方微米內存在的細孔數為0.5~5個細孔;E)在以5000倍電子顯微鏡觀察高分子多孔質膜的膜截面時,從與被處理液接觸之表面往內層部分係成為逐漸稀疏的構 造,相對於在與被處理液接觸的表面附近部分,內層部分的高分子網絡之空隙率為1~3倍。 (1) A polymer porous membrane which is a polymer porous membrane which is immersed in an activated sludge and obtains a flat membrane of a filtrate from an activated sludge liquid, and is characterized in that it satisfies the following A) to E Conditions: A) pure water flux is 20~50mL/cm 2 /min/bar; B) foaming point in pure water is 0.08~0.3MPa; C) polymer porous membrane system is made of polyvinyl chloride And/or chlorinated polyvinyl chloride; D) when the surface of the porous polymer membrane is in contact with the liquid to be treated by a 5,000-fold electron microscope, the membrane surface opening ratio is 25 to 45%, and the average pore diameter is 0.2 to 1.0 μm, the number of pores present in 1 square micrometer is 0.5 to 5 pores; E) when the membrane cross section of the porous membrane of the polymer is observed by a 5,000-fold electron microscope, the surface in contact with the liquid to be treated The inner layer portion has a gradually sparse structure, and the void ratio of the polymer network in the inner layer portion is 1 to 3 times with respect to the portion near the surface in contact with the liquid to be treated.

(2)如(1)之高分子多孔質膜,其特徵係滿足下述F)~H)之條件:F)浸漬於60℃的熱水4週再予以乾燥後所測定得到的純水通量之保持率為80%以上;G)膜的厚度為80~150μm;H)於縱向、橫向上二者之每15mm寬的降伏強度均為17~52N,且降伏伸長率均為1~5%。 (2) The porous polymer membrane according to (1), which is characterized by satisfying the following conditions F) to H): F) pure water passing after being immersed in hot water at 60 ° C for 4 weeks and then dried. The retention of the amount is above 80%; G) the thickness of the film is 80~150μm; H) the tensile strength of each 15mm width in the longitudinal and transverse directions is 17~52N, and the elongation at break is 1~5 %.

(3)如(1)或(2)記載之高分子多孔質膜,其特徵為高分子多孔質膜係由:用以形成網目狀網絡構造之高分子材料所構成之膜原料、與用以支持它之不織布所構成之膜基材來形成。 (3) The porous polymer membrane according to (1) or (2), wherein the polymer porous membrane is composed of a membrane material composed of a polymer material for forming a mesh network structure, and is used for It is formed by supporting a film substrate composed of a non-woven fabric.

(4)如(3)記載之高分子多孔質膜,其特徵為膜基材係滿足下述I)~K)之條件:I)纖維徑為5~12μm;J)厚度為80~150μm,且每1μm厚的單位面積重量為0.4~0.8g/m2;K)於縱向、橫向上二者之每15mm寬的降伏強度均為15~50N,且降伏伸長率均為1~5%。 (4) The porous polymer membrane according to (3), wherein the membrane substrate satisfies the following conditions I) to K): I) a fiber diameter of 5 to 12 μm; and J) a thickness of 80 to 150 μm. And the weight per unit area of the thickness of 1 μm is 0.4-0.8 g/m 2 ; K) the tensile strength of each 15 mm width in the longitudinal direction and the lateral direction is 15 to 50 N, and the elongation at break is 1 to 5%.

(5)如(1)至(4)中任一項所記載之高分子多孔質膜,其特徵為高分子多孔質膜的表面係經以羥丙基纖維素親水化處理的。 (5) The porous polymer membrane according to any one of (1) to (4), wherein the surface of the porous polymer membrane is hydrophilized by hydroxypropylcellulose.

(6)一種製造方法,其係包含將由不織布所構成的膜基材含漬於含有高分子材料、溶劑、及非溶劑之高分子溶液中並予以乾燥之步驟的製造(1)至(5)項中任一項之高分子多孔質膜之方法,其特徵為:高分子材料係聚氯乙烯及/或氯化聚氯乙烯, 而非溶劑係包含異丙醇與丁醇,且前述非溶劑中的異丙醇/丁醇之重量百分率為20~80%。 (6) A manufacturing method comprising the steps (1) to (5) of a step of containing a film substrate composed of a nonwoven fabric in a polymer solution containing a polymer material, a solvent, and a non-solvent and drying the polymer substrate. The method for producing a porous polymer membrane according to any one of the preceding claims, wherein the polymer material is polyvinyl chloride and/or chlorinated polyvinyl chloride, The non-solvent comprises isopropanol and butanol, and the weight percentage of isopropanol/butanol in the aforementioned non-solvent is 20-80%.

(7)如(6)之製造方法,其特徵為在高分子溶液中的高分子濃度為5~20重量%,且溶劑/非溶劑的重量比為1~3。 (7) The production method according to (6), wherein the polymer concentration in the polymer solution is 5 to 20% by weight, and the solvent/non-solvent weight ratio is 1 to 3.

(8)如(6)或(7)之製造方法,其特徵為乾燥時的溫度為10~40℃、相對濕度為50~90%。 (8) The production method according to (6) or (7), characterized in that the temperature at the time of drying is 10 to 40 ° C and the relative humidity is 50 to 90%.

本發明之高分子多孔質膜因膜原料係由聚氯乙烯及/或氯化聚氯乙烯形成,在具有能承受長時間使用之強度的同時,因表面開孔率、平均細孔徑、細孔數、膜截面的構造、與高分子網絡的空隙率被控制在特定範圍,而使透水性等膜性能極高。 The polymer porous membrane of the present invention is formed of polyvinyl chloride and/or chlorinated polyvinyl chloride, and has a surface open porosity, an average pore diameter, and a fine pore, while having a strength capable of withstanding long-term use. The number, the structure of the cross section of the film, and the porosity of the polymer network are controlled to a specific range, and the film performance such as water permeability is extremely high.

〔實施發明之形態〕 [Formation of the Invention]

本發明的高分子多孔質膜能使用於浸漬在活性污泥中、並自活性污泥液中得到澄清濾液之膜分離活性污泥法(MBR)。MBR法乃是一種將排水引導至活性污泥中,把以有機物為主的排水中之污濁物質捕捉至反應槽中大量繁殖的微生物、也就是活性污泥中,將其藉由代謝或呼吸消耗掉,或就這樣附著著以污泥排出,藉由如此進行,排水中的有機物被活性污泥分解,另一方面,使用膜進行過濾,僅取出澄清的水之技術。 The porous polymer membrane of the present invention can be used as a membrane separation activated sludge method (MBR) for immersing in activated sludge and obtaining a clear filtrate from an activated sludge liquid. The MBR method is to introduce the drainage into the activated sludge, and capture the pollutants in the organic-based drainage into the microorganisms in the reaction tank, that is, the activated sludge, which is consumed by metabolism or respiration. In this way, the sludge is discharged, and the organic matter in the drainage is decomposed by the activated sludge, and the membrane is used for filtration, and only the clarified water is taken out.

一般水處理膜依照分隔能力有下面3種類。首先是具有奈米尺寸以下的分子等級之分離能力的逆滲透(RO)膜與NF膜,由於能分離溶解於水中的鹽,而能用於海水淡水化、鹵水的鹽分去除、與軟水化等。其次係具有數奈米至數百奈米的分隔能力之UF膜,能使用做為於淨水場除去病毒與細菌等的過濾 膜,或使用做為淨水器或血液淨化用膜。接著是具有數百奈米至數微米之分隔能力的MF膜。而MBR所使用的膜係屬於UF膜~MF膜之範圍,扮演將活性污泥中的夾雑物及細菌與淨水分離的角色。 Generally, the water treatment film has the following three types according to the separation ability. First, a reverse osmosis (RO) membrane and an NF membrane having a molecular level separation ability of a nanometer size or less can be used for saltwater desalination, salinity removal of brine, softening, etc. by separating salts dissolved in water. . Next, it is a UF membrane with a separation capacity of several nanometers to several hundred nanometers, which can be used as a filter for removing viruses and bacteria in a water purification field. Membrane, or used as a water purifier or membrane for blood purification. This is followed by an MF film having a separation ability of several hundred nanometers to several micrometers. The membrane used in MBR belongs to the range of UF membrane to MF membrane, and plays a role in separating the inclusions and bacteria in the activated sludge from the purified water.

在自活性污泥分離淨水時,過去方法係以沈澱法來分離。然而,若採用此方法因分離上需要長時間,就不可欠缺要設置必須有廣大面積之沈澱池。而為了除去並處理沈澱槽的顆粒,便不可避免的會有大腸桿菌等活性污泥所含有的細菌與污泥成分混入處理水之風險。另一方面,使用分離膜之MBR法由於取決於膜的孔徑能幾乎完全固液分離,除了能顯著減少上述的風險,因為能省去沈澱槽,對處理設備或施設的精巧化、省空間化亦有大幅貢獻。然而,如先前所述,由於使用膜而發生最大的問題-積垢。在使用的同時,細菌的代謝物與遺骸、代謝物-糖與多肽會附著於膜表面將膜堵塞,於MBR中若能有對此積垢的耐性高之膜,則能讓設備管理變容易,對處理能力提升與成本降低亦能有大幅貢獻。而本發明之膜即如上述般,減少在使用膜時的問題-積垢,成功提昇透水性等膜性能。 In the separation of purified water from activated sludge, the past method was separated by precipitation. However, if this method is required for separation for a long time, it is not necessary to provide a sedimentation tank having a large area. In order to remove and treat the particles of the sedimentation tank, there is a risk that bacteria and sludge components contained in the activated sludge such as Escherichia coli will be mixed into the treated water. On the other hand, the MBR method using a separation membrane can almost completely reduce the above-mentioned risk because the pore diameter of the membrane can be almost completely separated, because the precipitation tank can be omitted, and the processing equipment or the device can be refined and space-saving. It also contributed a lot. However, as previously described, the biggest problem - fouling - occurs due to the use of the membrane. At the same time of use, bacterial metabolites and remains, metabolites, sugars and peptides will adhere to the surface of the membrane to block the membrane. If MBR has a membrane with high resistance to this scale, it will make equipment management easier. It can also contribute significantly to the improvement of processing capacity and cost reduction. On the other hand, the film of the present invention, as described above, reduces the problem of fouling during use of the film, and successfully improves the film properties such as water permeability.

本發明之多孔質膜係將由不織布構成之膜基材,與由形成網目狀網絡構造之高分子材料構成之膜原料複合而構成。構成膜基材之不織布不僅支持著膜原料保持膜的形態,還扮演吸收施加到膜之應力的角色。構成膜原料的高分子材料藉由在與膜基材適度纏絡的同時,取得適當的多孔構造,而能具有做為分離膜之機能。 The porous film of the present invention comprises a film substrate composed of a nonwoven fabric and a film material composed of a polymer material having a mesh network structure. The non-woven fabric constituting the film substrate not only supports the form of the film material holding film but also plays the role of absorbing the stress applied to the film. The polymer material constituting the film material can have a function as a separation membrane by appropriately entanglement with the film substrate and obtaining an appropriate porous structure.

不織布只要是由不溶於有機溶劑或水的高分子材料所構成,具有保持膜成分且保持施加到膜之應力的能力者即無限 定。不織布較佳係由烴系、烯烴系、縮合系之聚合物所構成,例如由聚乙烯、聚烯烴、聚乙烯醇、聚對酞酸乙二酯、耐綸、聚醯亞胺、聚四氟乙烯、聚氯乙烯等所構成。 The non-woven fabric is composed of a polymer material that is insoluble in an organic solvent or water, and has an ability to retain the film component and maintain the stress applied to the film. set. The nonwoven fabric is preferably composed of a hydrocarbon-based, olefin-based or condensed polymer, such as polyethylene, polyolefin, polyvinyl alcohol, polyethylene terephthalate, nylon, polyimine, polytetrafluoroethylene. It is composed of ethylene, polyvinyl chloride, and the like.

不織布的厚度較佳為80~150μm。不織布因使用做為透水膜基材,若過厚即可能對水的透過造成阻礙,但是若過薄則強度不夠充分而恐怕不堪長期使用。 The thickness of the non-woven fabric is preferably 80 to 150 μm. Non-woven fabrics are used as a water-permeable film substrate. If they are too thick, they may hinder the penetration of water. However, if they are too thin, the strength is insufficient and they may not be used for a long time.

為了確保不織布的強度,已知用接著劑將纖維彼此固定之方法。做為固定之方法,為將黏結劑成分形成為鞘部分之芯鞘構造纖維之方法,或製成不織布後含浸於接著劑成分之方法等任一方法均可,較佳為配合黏結劑纖維製成不織布後,藉由以熱予以熔接,將纖維彼此連結之方法。適當組合拉伸絲與未拉伸絲製作出不織布後,施加溫度與壓力。此時未拉伸絲因與拉伸絲相比在低溫較軟,而扮演著黏結劑的角色。雖已知有藉壓花保持強度之方法,但壓花部分在形成膜時恐怕會成為缺陷。 In order to secure the strength of the nonwoven fabric, a method of fixing the fibers to each other with an adhesive is known. As a method of fixing, a method of forming a binder component into a core sheath structure fiber of a sheath portion, or a method of impregnating a binder component after a nonwoven fabric, or the like may be preferably used in combination with a binder fiber. After the nonwoven fabric is formed, the fibers are joined to each other by welding by heat. After a suitable combination of the drawn yarn and the undrawn yarn to form a nonwoven fabric, temperature and pressure are applied. At this time, the undrawn yarn plays a role as a binder because it is soft at a low temperature compared with the drawn yarn. Although a method of maintaining strength by embossing is known, the embossed portion may become a defect when forming a film.

不織布的製成方法亦存在如熔噴法(melt blown)、熱壓法(thermal bond)、造紙法等各種方法,任一種方法均可。但是,纖維徑與單位面積重量在確保透水性上係重要的。纖維徑較佳為5~12μm,更佳為7~10μm。纖維徑若過小則強度變小,不堪長期使用,若過粗則因整體的溶媒平衡變少而不具充分強度,其恐怕同樣不堪長期使用。每1μm厚的單位面積重量較佳為0.4~0.8g/m2,較佳為0.5~0.7g/m2。單位面積重量以小者為佳,但因若過小則會使強度變小,不堪做為膜來長期使用,而若過大則會使空隙變少,恐怕使透水性變差。 There are various methods such as a melt blown, a thermal bond, and a papermaking method, and any of them can be used. However, the fiber diameter and the basis weight are important in ensuring water permeability. The fiber diameter is preferably 5 to 12 μm, more preferably 7 to 10 μm. If the fiber diameter is too small, the strength becomes small, and it is unbearable for long-term use. If it is too thick, the overall solvent balance is small and does not have sufficient strength, and it is also unbearable for long-term use. The basis weight per 1 μm thick is preferably 0.4 to 0.8 g/m 2 , preferably 0.5 to 0.7 g/m 2 . The weight per unit area is preferably small, but if it is too small, the strength is made small, and it is not used as a film for a long period of time, and if it is too large, the voids are reduced, and the water permeability may be deteriorated.

在對不織布施加力時,起初為彈性的變形,若力量放鬆則回到原樣,但若超越某個點進一步施加力使之變形時,即便力 量放鬆了也不會回到原樣。前者稱為彈性變形,後者稱為塑性變形。而上述的點稱為降伏點,該力稱為降伏強度,伸展稱為降伏伸長率。不織布為支持膜的構件,其強度與伸長率特性為支配膜強度的重要特性。若降伏強度低,因會在對膜施加力時立即產生塑性變形而無法回到原樣,故以高者為佳。但是若過高,則因在技術上變得難以得到可維持透水性之便宜不織布,故不織布在縱向、橫向二者之每15mm寬的降伏強度較佳為15~50N,更佳為15~45N。又,降伏伸長率若大,則因不織布的伸展變大,在形成膜時網絡破損之風險變高,受水壓或過濾時的壓力變成變形的狀態,而恐怕無法得到充分的透水量。但是,若完全沒有伸展,則在對膜施加衝撃時無法吸收而有造成破損的可能性。從而,不織布的降伏伸長率較佳為1~5%,更佳為1~3%。此外,將所得到的片材的長度方向設為縱向。 When applying force to the non-woven fabric, it is initially elastic. If the force is relaxed, it will return to the original, but if a force is applied beyond a certain point to deform it, even force The amount is relaxed and will not return to the original. The former is called elastic deformation, and the latter is called plastic deformation. The above point is called the drop point, the force is called the fall strength, and the stretch is called the fall elongation. The non-woven fabric is a member supporting the film, and its strength and elongation characteristics are important characteristics that govern the strength of the film. If the drop strength is low, the plastic deformation immediately occurs when a force is applied to the film, and it is impossible to return to the original state, so that it is preferable. However, if it is too high, it is technically difficult to obtain an inexpensive non-woven fabric capable of maintaining water permeability. Therefore, the lodging strength per 15 mm width of the non-woven fabric in the longitudinal direction and the lateral direction is preferably 15 to 50 N, more preferably 15 to 45 N. . Further, if the elongation at break is large, the elongation of the nonwoven fabric becomes large, and the risk of breakage of the network at the time of film formation becomes high, and the pressure at the time of water pressure or filtration becomes a state of deformation, and there is a fear that a sufficient amount of water permeability cannot be obtained. However, if it is not stretched at all, it is not absorbed when the film is applied and there is a possibility of damage. Therefore, the elongation at break of the nonwoven fabric is preferably from 1 to 5%, more preferably from 1 to 3%. Further, the longitudinal direction of the obtained sheet was set to the longitudinal direction.

構成膜原料的高分子材料係使用聚氯乙烯及/或氯化聚氯乙烯,藉由相分離法形成具有亞微米尺寸之孔的高分子網絡,據以成膜。 The polymer material constituting the film material is formed by forming a polymer network having pores having a submicron size by phase separation using polyvinyl chloride and/or chlorinated polyvinyl chloride.

相分離已知有在將高分子材料與溶媒混合而製成溶液後,塗布於不織布的基材,在空氣中進行乾燥之方法(乾式法)、引導至凝固浴中使之凝固的方法(濕式法)、使溫度急劇變化之方法(熱誘導式相分離法)等。使用任一種方法均可,但將經塗布高分子溶液之基材在氣相中進行乾燥的乾式法,由於製膜管理的容易性與不需要複雜的設備複雑而為較佳者。 Phase separation is a method in which a polymer material and a solvent are mixed to form a solution, and then applied to a nonwoven fabric substrate, dried in air (dry method), and guided to a coagulation bath to be solidified (wet) Method (method)), a method of rapidly changing the temperature (heat-induced phase separation method), and the like. Any method may be used, but the dry method in which the substrate of the coated polymer solution is dried in the gas phase is preferred because of the ease of film formation management and the need for complicated equipment reclamation.

溶解高分子材料之溶媒必須為能溶解構成膜之高分子但不溶解不織布者,可使用大致在150℃以下揮發或是水溶性者。具體而言適合者有四氫呋喃、甲苯、DMF、NMR、DMAC, 可使用單獨一種亦可混合多種。在進行乾式製膜時,因係在氣相中使溶媒揮發以製膜,故較佳使用四氫呋喃與其混合溶媒。 The solvent for dissolving the polymer material must be one which can dissolve the polymer constituting the film but does not dissolve the non-woven fabric, and can be used to volatilize or water-soluble at approximately 150 ° C or lower. Specifically suitable for tetrahydrofuran, toluene, DMF, NMR, DMAC, A single type or a mixture of a plurality of types can be used. In the case of dry film formation, since the solvent is volatilized in the gas phase to form a film, tetrahydrofuran and a mixed solvent thereof are preferably used.

非溶劑以水或醇類為適。醇類中特別以乙醇、丙醇、丁醇為適當者。此等可使用單獨一種,亦可多種混合。 The non-solvent is preferably water or an alcohol. Among the alcohols, ethanol, propanol and butanol are particularly suitable. These may be used alone or in combination.

溶液中的高分子濃度較佳為5~20重量%,更佳為6~18重量%,最佳為7~15重量%。若高分子濃度過低,則膜的網絡構造未充分發展,膜部分本身不堪長期使用,若濃度過高則溶液無法浸透至不織布的內部,恐怕無法扮演做為膜的機能。溶劑與非溶劑的比(溶劑/非溶劑)較佳為1~3,更佳為1.5~2.8,最佳為2~2.6。非溶劑的比例若過高則會損害高分子的溶解能力,無法製成均勻溶液,恐怕無法達成充分的含浸。若過低則恐怕無法扮演促進相分離的角色。 The concentration of the polymer in the solution is preferably from 5 to 20% by weight, more preferably from 6 to 18% by weight, most preferably from 7 to 15% by weight. If the polymer concentration is too low, the network structure of the film is not sufficiently developed, and the film portion itself cannot be used for a long period of time. If the concentration is too high, the solution cannot penetrate into the interior of the non-woven fabric, and it may not function as a film. The ratio of the solvent to the non-solvent (solvent/non-solvent) is preferably from 1 to 3, more preferably from 1.5 to 2.8, most preferably from 2 to 2.6. If the ratio of the non-solvent is too high, the solubility of the polymer is impaired, and a uniform solution cannot be obtained, and sufficient impregnation may not be achieved. If it is too low, I am afraid that it cannot play a role in promoting separation.

構成膜的高分子材料為疏水性。因此,在膜開始使用時不僅難以讓水通過,由於疏水性相互作用,容易產生在使用中活性污泥菌生成之代謝成分與糖、遺骸等會被吸附於膜上使膜堵塞,也就是積垢之問題。避免此問題的方法之一,即較佳使膜親水化。 The polymer material constituting the film is hydrophobic. Therefore, it is not only difficult to pass water when the membrane is used, but due to the hydrophobic interaction, it is easy to cause the metabolic components formed by the activated sludge bacteria and the sugar, the remains, etc. to be adsorbed on the membrane to block the membrane, that is, the product. The problem of scale. One of the ways to avoid this problem is to preferably hydrophilize the membrane.

親水化的處理方法可舉出:將親水化劑添加至高分子溶液之方法、於製成膜後添加親水化劑之方法、對膜進行表面處理之方法等。親水化劑為在一分子內同時具有疏水部與親水部之化學物質,只要是能固定在膜表面或內部網絡者即不受限,可舉出:糖類、纖維素衍生物、界面活性劑等。具體來說,可舉出羥丙基纖維素、蔗糖脂肪酸酯、十二基硫酸鈉等。而在製成膜後施以親水化之方法可舉出:浸漬於由上述親水化劑所形成之溶液後,施加溫度或予以乾燥來固定之方法。又,亦可用直 接法將膜本身磺化或賦予硫酸基。另外,亦可考慮照射電子線、電漿、或紫外線後,使表面氧化等、或賦予羧酸等方法。 The method of treating the hydrophilization includes a method of adding a hydrophilizing agent to a polymer solution, a method of adding a hydrophilizing agent after forming a film, a method of surface-treating a film, and the like. The hydrophilizing agent is a chemical substance having a hydrophobic portion and a hydrophilic portion in one molecule, and is not limited as long as it can be immobilized on the surface or internal network of the film, and examples thereof include sugars, cellulose derivatives, surfactants, and the like. . Specific examples thereof include hydroxypropylcellulose, sucrose fatty acid ester, and sodium dodecyl sulfate. Further, a method of hydrophilizing after forming a film may be a method of immersing in a solution formed of the hydrophilizing agent, applying a temperature, or drying and fixing the solution. Also, you can use straight The membrane itself sulfonates or imparts a sulfate group. Further, a method of irradiating an electron beam, a plasma, or an ultraviolet ray, or oxidizing a surface or imparting a carboxylic acid may be considered.

雖說能採取如上述之各種膜的親水化之方法,但由降低成本的觀點來看,較佳為塗布羥丙基纖維素或添加蔗糖脂肪酸酯。更進一步在本發明中由對實際排液的耐積垢之觀點來看,以塗布羥丙基纖維素為適當。 Although a method of hydrophilizing various membranes as described above can be employed, it is preferred to coat hydroxypropylcellulose or to add sucrose fatty acid ester from the viewpoint of cost reduction. Further, in the present invention, it is suitable to apply hydroxypropylcellulose from the viewpoint of resistance to fouling of actual discharge.

下面敘述本發明之高分子多孔質膜的製成方法之一例。首先,讓將形成膜之高分子溶解而成之溶液含浸於不織布。含浸之方法可使用浸漬法、使用模具之含浸等任意方法。 An example of a method for producing the porous polymer membrane of the present invention will be described below. First, a solution obtained by dissolving a polymer forming a film is impregnated into a nonwoven fabric. The method of impregnation may be carried out by any method such as dipping, impregnation using a mold, or the like.

將高分子溶液含浸於不織布後,引導至乾燥區。此時,必須注意不要讓乾燥風直接吹到膜。其原因是因為經由風吹到膜會促進膜表面更新,使得僅有膜表面急劇進行相分離,結果使表面的開孔率變低,而恐怕會使得透水性降低。又,本發明人戮力研究之結果,發現此種表面開孔率低的膜耐積垢性能已不佳。 After impregnating the non-woven fabric with the polymer solution, it is guided to the drying zone. At this point, care must be taken not to let dry wind blow directly onto the membrane. The reason for this is because the film surface is promoted to be renewed by the wind, so that only the surface of the film is rapidly phase-separated, and as a result, the opening ratio of the surface is lowered, and the water permeability may be lowered. Further, as a result of intensive studies by the present inventors, it has been found that such a film having a low surface opening ratio has poor fouling resistance.

於乾燥區溫度與濕度的控制相當重要。較佳的溫度為10~40℃,更佳為15~30℃,最佳為18~25℃。溫度若過高則會促進自膜表面乾燥,膜表面迅速進行相分離的結果,恐怕使表面的開孔率降低。而溫度若過低則會在膜表面發生結露,使膜的相分離機構之控制變難。另外,較佳的相對濕度為40~85%,更佳為50~85%,最佳為60~85%。濕度若過低,膜表面迅速進行相分離的結果,恐怕無法確保充分的開孔率。而濕度若過高則會使膜表面孔的孔徑分布變大,可能讓起泡點降低且分隔性能惡化,恐怕也會在膜表面發生結露。較佳亦對浸漬之高分子溶液的溫度進行控制。藉由調整到較佳為相對於乾燥區的溫度 -15~+15℃,更佳為-10℃~+10℃,最佳為-5℃~+5℃,能良好的製膜。 Control of temperature and humidity in the drying zone is important. The preferred temperature is 10 to 40 ° C, more preferably 15 to 30 ° C, and most preferably 18 to 25 ° C. If the temperature is too high, the surface of the film is dried, and the surface of the film is rapidly phase-separated. As a result, the opening ratio of the surface may be lowered. If the temperature is too low, dew condensation occurs on the surface of the film, making it difficult to control the phase separation mechanism of the film. Further, the preferred relative humidity is 40 to 85%, more preferably 50 to 85%, and most preferably 60 to 85%. If the humidity is too low and the surface of the film is rapidly phase-separated, it may not be possible to ensure a sufficient opening ratio. If the humidity is too high, the pore size distribution of the pores on the surface of the membrane becomes large, which may lower the bubble point and deteriorate the separation performance, and condensation may occur on the surface of the membrane. It is also preferred to control the temperature of the impregnated polymer solution. By adjusting to a temperature preferably relative to the drying zone -15~+15°C, more preferably -10°C~+10°C, optimally -5°C~+5°C, good film formation.

又,上述的乾式製膜中,為了展現良好的膜表面開孔率,必須組合使用具有適當的蒸氣壓之溶媒與非溶劑。溶媒可選擇四氫呋喃或其混合溶媒。非溶劑可選擇異丙醇、丁醇、及彼等之混合溶媒,較佳可使用異丙醇與1-丁醇的2種類之混合溶媒。本發明人戮力研究之結果,發現以二者混合之溶媒,能展現良好的膜表面開孔率,與兼顧透水性及起泡點。本發明中,藉由使用上述2種非溶劑能發揮本發明的目標性能。非溶劑中1-丁醇的混合重量,相對於全非溶劑量(異丙醇與1-丁醇的總重量),較佳為20~80%,更佳為22~70%,最佳為25~60%。 Further, in the above dry film formation, in order to exhibit a good film surface opening ratio, it is necessary to use a solvent having a suitable vapor pressure and a non-solvent in combination. The solvent may be selected from tetrahydrofuran or a mixed solvent thereof. The non-solvent may be selected from isopropanol, butanol, and a mixed solvent thereof. It is preferred to use a mixed solvent of two types of isopropyl alcohol and 1-butanol. As a result of the inventors' research, it was found that a solvent mixed with the two can exhibit a good open cell surface porosity and a combination of water permeability and foaming point. In the present invention, the target properties of the present invention can be exhibited by using the above two kinds of non-solvents. The mixed weight of 1-butanol in the non-solvent is preferably from 20 to 80%, more preferably from 22 to 70%, based on the total non-solvent amount (total weight of isopropanol and 1-butanol), preferably 25~60%.

本發明中,如此製作之高分子多孔質膜,其與被處理液接觸之表面在5000倍電子顯微鏡下,表面的平均細孔徑為0.2~1μm,較佳為0.3~0.9μm,更佳為0.4~0.8μm,表面開孔率為25~45%,較佳為28~45%,於表面的1平方微米內存在的細孔數為0.5~5個,較佳為0.7~3個,更佳為0.8~2個。上述的表面之平均細孔徑係考慮到分隔性能與透水性,表面開孔率係考慮到長期使用之強度與過濾效率,細孔數係由細孔徑與開孔率定義。 In the present invention, the surface of the polymer porous film thus produced which is in contact with the liquid to be treated has an average pore diameter of 0.2 to 1 μm, preferably 0.3 to 0.9 μm, more preferably 0.4 under a 5,000-fold electron microscope. ~0.8μm, the surface opening ratio is 25~45%, preferably 28~45%, and the number of pores present in the 1 square micrometer of the surface is 0.5~5, preferably 0.7~3, preferably It is 0.8~2. The average pore diameter of the above surface is considered to be the separation property and the water permeability, and the surface opening ratio is considered in consideration of the strength and filtration efficiency for long-term use, and the number of pores is defined by the pore diameter and the opening ratio.

本發明之高分子多孔質膜,在以5000倍電子顯微鏡觀察其膜截面時,較佳為從與被處理液接觸之表面往內層部分係成為逐漸稀疏的構造,構成膜之高分子材料係構成網絡上的3次元針目,於膜基材的不織布適度纏絡。此時,網絡的密度若過高,則會阻礙透水性能,而若過低,則長期使用時膜成分會自基材脫離,而恐怕不能發揮做為膜的機能。而表現此性質的即 是相對於膜的與被處理液接觸之表面附近,內層部分的高分子網絡之空隙率。該空隙率為1~3倍,較佳為1~2倍。圖1(a)及(b)顯示藉由本發明所得到的膜之截面構造的範例,可確認到從膜表面附近往內層部分係成為逐漸稀疏的構造,及與膜基材纏絡並構成良好的網絡。在膜表面部分具有分隔能力,於內層部分不會阻礙通過表面的水之透過,為能有效率的進行過濾之膜構造。 When the cross-section of the film is observed by a 5,000-fold electron microscope, the polymer porous film of the present invention preferably has a structure that gradually becomes sparse from the surface in contact with the liquid to be treated, and the polymer material constituting the film is formed. The three-dimensional needles on the network are formed, and the non-woven fabric of the film substrate is moderately entangled. At this time, if the density of the network is too high, the water permeability is hindered, and if it is too low, the film component may be detached from the substrate during long-term use, and the function as a film may not be exhibited. And this property is It is the porosity of the polymer network of the inner layer portion in the vicinity of the surface of the film which is in contact with the liquid to be treated. The void ratio is 1 to 3 times, preferably 1 to 2 times. 1(a) and 1(b) show an example of a cross-sectional structure of a film obtained by the present invention, and it has been confirmed that a structure which is gradually thinned from the vicinity of the surface of the film to the inner layer portion and which is entangled with the film substrate Good network. The membrane surface portion has a partitioning ability, and the inner layer portion does not hinder the permeation of water passing through the surface, and is a membrane structure capable of efficiently filtering.

膜的初期性能係以純水通量與起泡點作評價。純水通量係在單位時間每單位面積純水能通過之水的體積,起泡點係顯示膜的最大孔徑之指標,表示分隔性能。純水通量(單位:mL/cm2/min/bar)為20~50,較佳為25~45。純水通量若過小,則在供實用時為了確保必要的出水量,必須要增加膜的片數、提高幫浦的壓力,在經濟上、能量上有大問題。另一方面,若過大,則膜的細孔徑有必要加大,讓分隔性能變差,可能不能發揮做為膜的充分機能。起泡點為0.08~0.3,較佳為0.09~0.25,更佳為0.1~0.2。起泡點若過小,因分隔性能不夠(細孔徑變得過大),污泥成分有可能混進過濾水,若過大則因無法確保充分的透水量之可能性變高,恐怕使過濾的效率惡化。 The initial performance of the film was evaluated as pure water flux and bubble point. The pure water flux is the volume of water through which pure water can pass per unit area per unit time, and the bubble point is an index indicating the maximum pore diameter of the membrane, indicating the separation performance. The pure water flux (unit: mL/cm 2 /min/bar) is 20 to 50, preferably 25 to 45. If the pure water flux is too small, in order to ensure the necessary amount of water, it is necessary to increase the number of membranes and increase the pressure of the pump, which is economically and energy-intensive. On the other hand, if it is too large, the pore diameter of the film needs to be increased to deteriorate the partitioning performance, and it may not be sufficient to function as a film. The bubble point is 0.08 to 0.3, preferably 0.09 to 0.25, more preferably 0.1 to 0.2. If the bubble point is too small, the separation performance is insufficient (the pore diameter becomes too large), and the sludge component may be mixed with the filtered water. If it is too large, the possibility of ensuring sufficient water permeability is high, and the filtration efficiency may be deteriorated. .

本發明之多孔質膜在浸漬於60℃的熱水4週再乾燥後所測定之純水通量的保持率較佳為80%以上。為了持續耐積垢性(fouling resistance),期望賦予膜的親水性即便經過長時間使用亦不會脫落,戮力研究的結果,可知在浸漬於60℃的熱水後乾燥,相對於失去親水性之膜展現出不充分的透水性,能持續親水性之膜則能展現出充分的透水性,並能確認為所期望的膜特性。純水通量的保持率更佳為85%以上,還要更佳為90%以上。 The retention rate of the pure water flux measured by the porous membrane of the present invention after being immersed in hot water at 60 ° C for 4 weeks is preferably 80% or more. In order to maintain the fouling resistance, it is desirable that the hydrophilicity imparted to the film does not fall off even after a long period of use. As a result of the investigation, it is known that the hydrophilicity after immersion in hot water at 60 ° C is relative to the loss of hydrophilicity. The film exhibits insufficient water permeability, and the film which can maintain hydrophilicity can exhibit sufficient water permeability and can be confirmed as a desired film property. The retention rate of pure water flux is more preferably 85% or more, and even more preferably 90% or more.

本發明之高分子多孔質膜的膜厚較佳為80~150μm。膜因係藉膜基材之不織布保持形狀,故與膜基材為大致相同厚度。厚度若過厚則會提高通水時的阻力而恐怕使透水性降低,若過薄則膜強度可能變得不充分。 The film thickness of the polymer porous film of the present invention is preferably 80 to 150 μm. Since the film retains its shape by the non-woven fabric of the film substrate, it is substantially the same thickness as the film substrate. If the thickness is too thick, the resistance at the time of water passing is increased, and the water permeability may be lowered. If the thickness is too thin, the film strength may be insufficient.

膜的強伸度特性基本上同樣受膜基材之不織布所支配。若降伏強度低,則因在力施加到膜上時立即導致塑性變形乃至無法回復原狀,故以高者為佳。本發明的膜在縱向、橫向上二者之每15mm寬的降伏強度較佳均為15~52N,更佳為18~45N。又,若降伏伸長率大,因膜的伸展變大,讓膜的網絡構造破損的風險變高,恐怕在水壓或過濾時的壓力下變成變形之狀態,而無法得到充分的透水量。但是,若完全沒有伸展,則在對膜施加衝撃時無法吸收而有造成破損的可能。從而,本發明之膜的降伏伸長率較佳為1~5%,更佳為1~3%。此外,所得到之片材的長度方向為縱向。 The tensile properties of the film are essentially also governed by the nonwoven fabric of the film substrate. If the strength of the drop is low, the plastic deformation is caused immediately when the force is applied to the film, and the original shape is not restored. The film of the present invention preferably has a drop strength of 15 to 52 N, more preferably 18 to 45 N, in both the longitudinal direction and the transverse direction. Further, when the elongation at break is large, the elongation of the film is increased, and the risk of damage to the network structure of the film is increased, and it is likely to be deformed under pressure at the time of water pressure or filtration, and a sufficient amount of water permeability cannot be obtained. However, if it is not stretched at all, it may not be absorbed when the film is applied and may be damaged. Therefore, the film of the present invention preferably has an elongation at break of from 1 to 5%, more preferably from 1 to 3%. Further, the longitudinal direction of the obtained sheet was a longitudinal direction.

〔實施例〕 [Examples]

藉由以下實施例來顯示本發明之高分子多孔質膜的優異效果,但本發明非受限於此。另外,實施例中所測定的特性值之評價方法記載於下。 The excellent effects of the porous polymer membrane of the present invention are shown by the following examples, but the present invention is not limited thereto. In addition, the evaluation method of the characteristic value measured by the Example is described below.

(1)純水通量 (1) Pure water flux

將所製作的多孔質膜剪裁為φ90mm的圓形,設置於過濾裝置(東洋濾紙株式會社製UHP-90K略去攪拌器)後,施加0.5bar水壓,由從裝置出口於1分鐘內收集的透水量,以下式求取純水通量。而在過濾所使用的水係25℃之RO水,從施加水壓起經過30秒設為收集開始時間。另外,從膜面起的水面高度係調整為3cm±1cm。 The produced porous film was cut into a circular shape of φ90 mm, and placed in a filter device (UHP-90K, manufactured by Toyo Filter Co., Ltd.), and then applied with a water pressure of 0.5 bar, and collected from the outlet of the device for 1 minute. The amount of water permeation, the following formula to obtain pure water flux. On the other hand, the RO water of 25 ° C in the water used for filtration was set as the collection start time after 30 seconds from the application of the water pressure. Further, the height of the water surface from the film surface was adjusted to 3 cm ± 1 cm.

(純水通量〔mL/cm2/min/bar〕)=(Q〔mL/min〕)/(A〔cm2〕)/(P〔bar〕) (pure water flux [mL/cm 2 /min/bar]) = (Q [mL / min]) / (A [cm 2 ]) / (P [bar])

(Q:1分鐘的透水量、A:有效膜面積=48cm2、P:水壓=0.5bar) (Q: water permeability per minute, A: effective membrane area = 48 cm 2 , P: water pressure = 0.5 bar)

(2)純水通量的保持率 (2) Purity of pure water flux

將製作之膜浸漬於60℃的熱水裡4週後,予以風乾1晚。之後,依照上述(1)的方法,測定純水通量,除以浸漬於熱水之前的通量,算出純水通量的保持率(以百分比表示)。其中,風乾時的溫濕度係在溫度20~30℃、濕度40~70%之範圍。 The produced film was immersed in hot water at 60 ° C for 4 weeks, and then air-dried for 1 night. Thereafter, according to the method of the above (1), the pure water flux was measured, and the flux before the immersion in hot water was divided, and the retention rate (in percent) of the pure water flux was calculated. Among them, the temperature and humidity during air drying are in the range of 20 to 30 ° C and 40 to 70% humidity.

(3)起泡點 (3) bubble point

將所製作的膜設置在(1)所用的裝置,以從膜面起高5cm的方式注入RO水,在裝置內的洩壓閥開啟的狀態下,從裝置出口(膜下面)施加氮氣壓,取氣泡連續由膜面冒出到水中之壓力做為起泡點〔MPa〕。其中,不妨礙在膜上面觀察氣泡地設置能支持膜的構件,設計成膜不會受到來自下面的壓力而從裝置脫落。又,氮氣壓的上昇速度設為每1分鐘0.02MPa。 The produced membrane was placed in the apparatus used in (1), RO water was injected in such a manner that the membrane surface was 5 cm high, and nitrogen pressure was applied from the outlet of the apparatus (below the membrane) in a state where the pressure relief valve in the apparatus was opened. The pressure at which the bubble continuously emerges from the film surface into the water is taken as the bubble point [MPa]. Among them, the member capable of supporting the film was not hindered from observing the bubble on the film, and the film was designed to be detached from the device without being subjected to pressure from the lower surface. Further, the rate of increase in the nitrogen pressure was set to 0.02 MPa per minute.

(4)膜的表面開孔率 (4) Surface open porosity of the film

由製作之膜表面的掃描電子顯微鏡(SEM)相片,依以下順序算出表面開孔率。準備膜表面的5000倍SEM相片,以影像加工軟體,讓膜表面孔部分變黒、膜高分子部分變白,進行二值化處理。其中對從膜孔深處見到的高分子部分適當塗黑。之後,使用影像解析軟體(Image-J),算出膜的表面開孔率。此外,為了降低雜訊,將計測尺寸的最小值設為10。「Area Fraction〔%〕」相當於膜的表面開孔率。 From the scanning electron microscope (SEM) photograph of the surface of the produced film, the surface open ratio was calculated in the following order. A 5000-times SEM photograph of the surface of the film was prepared, and the soft body was processed by the image, and the pore portion of the film surface was changed, and the polymer portion of the film was whitened, and binarization treatment was performed. Among them, the polymer portion seen from the depth of the film hole is appropriately blackened. Thereafter, the image analysis software (Image-J) was used to calculate the surface opening ratio of the film. In addition, in order to reduce noise, the minimum value of the measurement size is set to 10. "Area Fraction [%]" corresponds to the surface opening ratio of the film.

(5)膜表面的平均細孔徑 (5) Average pore diameter of the membrane surface

與(4)相同,使用影像解析軟體(Image-J),算出膜表面的平均細孔徑。從以影像解析軟體算出的「Average Size〔pixel2〕」、與於解析使用之SEM影像的比例尺資料〔pixel/μm〕,求出膜孔的平均細孔面積〔μm2〕,將細孔假設為圓形,算出平均細孔徑(直徑)〔μm〕。 The average pore diameter of the film surface was calculated using the image analysis software (Image-J) in the same manner as in (4). From the "Average Size [pixel 2 ]" calculated by the image analysis software and the scale data [pixel/μm] of the SEM image used for analysis, the average pore area [μm 2 ] of the film pore was determined, and the pore size was assumed. In the case of a circle, the average pore diameter (diameter) [μm] was calculated.

(6)膜表面的細孔數 (6) The number of pores on the surface of the membrane

與(4)相同,使用影像解析軟體(Image-J)算出膜表面的細孔數。由從影像解析軟體算出的「count〔個〕」、於解析使用之SEM影像的全視野面積〔pixel2〕與比例尺資料〔pixel/μm〕算出細孔數〔個/μm2〕。 Similarly to (4), the number of pores on the surface of the film was calculated using an image analysis software (Image-J). The number of pores (number/μm 2 ) was calculated from the "count" calculated from the image analysis software, the total field of view area (pixel 2 ) and the scale data [pixel/μm] of the SEM image used for analysis.

(7)觀察膜表面至內層部之構造 (7) Observing the structure of the film surface to the inner layer

對所製作之膜的截面使用掃描電子顯微鏡(SEM),以5000倍拍攝從膜表面部分依序到膜裏面部分,確認膜截面全體的構造。 Using a scanning electron microscope (SEM) on the cross section of the produced film, the film surface portion was sequentially printed to the inside of the film at 5000 times, and the structure of the entire film cross section was confirmed.

(8)膜截面的高分子網絡之空隙率 (8) Void ratio of the polymer network of the film cross section

從以SEM拍攝之膜的截面相片,使用影像解析軟體(W inROOF體驗版),算出膜的高分子網絡之空隙率。其中在算出時,以不含計算膜基材部分之範圍的方式選擇計算範圍。分別對與被處理液接觸之表面附近部分(從膜表面起厚0.5μm~5μm之部分)及內層部(膜中央部分)計算,求取相對於表面附近部分之內層部的高分子網絡之空隙率的比率(以百分比表示)。 From the cross-sectional photograph of the film taken by SEM, the image analysis software (W inROOF experience version) was used to calculate the void ratio of the polymer network of the film. In the calculation, the calculation range is selected so as not to calculate the range of the film substrate portion. Calculate the polymer network in the vicinity of the surface in contact with the liquid to be treated (the portion from 0.5 μm to 5 μm thick from the surface of the film) and the inner portion (the central portion of the film) to obtain the inner layer portion of the portion near the surface. The ratio of void ratios (expressed as a percentage).

(9)膜的總厚度 (9) Total thickness of the film

關於膜的總厚度係使用厚度計測量任意5點,取其平均值。 Regarding the total thickness of the film, any five points were measured using a thickness gauge, and the average value thereof was taken.

(10)膜的降伏強度及降伏伸長率 (10) Falling strength and elongation at break of the film

膜的降伏強度與降伏伸長率係以下面順序算出。將製作之 膜裁切為寬15mm(長度約60mm)的帶狀,以檢測間距為40mm之方式設置Tensilon拉伸測定器。將測力器條件設為100kgf、範圍10%,以20mm/min的拉伸速度實施拉伸試驗,得到應力-應變曲線。由所得到的曲線將彈性變形部分與塑性變形部分的接線以直線描出,以兩者的交點為降伏點,求取該點對應之強度與降伏伸長率。分別對膜的縱向、橫向測定5片試料,取其平均值做為降伏強度〔N/15mm〕與降伏伸長率〔%〕。 The fall strength and the elongation at break of the film were calculated in the following order. Will be made The film was cut into a strip shape having a width of 15 mm (about 60 mm in length), and a Tensilon tensile tester was set in such a manner that the detection pitch was 40 mm. The dynamometer conditions were set to 100 kgf and the range was 10%, and a tensile test was performed at a tensile speed of 20 mm/min to obtain a stress-strain curve. From the obtained curve, the wiring of the elastically deformed portion and the plastically deformed portion is drawn in a straight line, and the intersection point of the two is taken as the falling point, and the corresponding strength and the elongation at break of the point are obtained. Five samples were measured in the longitudinal direction and the transverse direction of the film, and the average value was taken as the drop strength [N/15 mm] and the elongation at break [%].

(11)膜基材的厚度 (11) Thickness of film substrate

膜基材的厚度係對用於膜的基材使用厚度計任意測量5點取其平均值。另外,亦實施浸漬於僅能從製膜後的膜溶解出膜成分之溶媒中,將膜成分除去露出膜基材後再進行測定之方法。 The thickness of the film substrate was measured by arbitrarily measuring 5 points using the thickness of the substrate for the film. Further, a method of immersing in a solvent which can dissolve a film component only from a film after film formation, and removing the film component to expose the film substrate is also carried out.

(12)膜基材的纖維徑 (12) Fiber diameter of the film substrate

膜基材的纖維徑係以SEM拍攝基材,由所拍攝的基材纖維與比例尺資料所算出。對10根纖維進行計算,將其平均值做為膜基材的纖維徑〔μm〕。 The fiber diameter of the film substrate was photographed by SEM, and the fiber diameter and scale data of the film were taken. Ten fibers were counted, and the average value was taken as the fiber diameter [μm] of the film substrate.

(13)每單位厚度之膜基材的單位面積重量 (13) Unit weight per unit thickness of the film substrate

膜基材的單位面積重量係裁取10平方公分的基材以電子天秤秤量,由此結果算出每1m2的重量,得到基材的單位面積重量後,除以膜基材的厚度,求出每1μm厚的單位面積重量〔g/m2/μm〕。 The weight per unit area of the film base material was measured by weighing 10 square centimeters of the substrate on an electronic scale, and the weight per 1 m 2 was calculated to obtain the basis weight of the substrate, and then the thickness of the film substrate was determined. Weight per unit area [g/m 2 /μm] per 1 μm thick.

(14)膜基材的降伏強度及降伏伸長率 (14) Falling strength and elongation at break of the film substrate

膜基材的降伏強度與降伏伸長率係使用Tensilon拉伸測定器測定。除了使用膜基材取代膜以外,與(11)同樣地進行算出。 The drop strength and the elongation at break of the film substrate were measured using a Tensilon tensile tester. The calculation was performed in the same manner as (11) except that the film substrate was used instead of the film.

(15)實液測試(積垢程度) (15) Solid liquid test (degree of fouling)

使用實際的污泥液調查膜的積垢特性。裝置係使用宮本製作所製作的浸漬型膜分離活性污泥法測試裝置(Model IMF-5)。以使裝置槽內的MLSS濃度為10,000mg/L左右之方式調整活性污泥液,設置將所製作之膜貼於兩面之匣式濾膜。以膜面積每1m2為0.6m3/日的過濾速度用蠕動幫浦進行減壓過濾運轉。在過濾運轉中不設置運轉停止時間地連續運轉,由匣式濾膜下部進行連續曝氣。進續在此運轉2週,藉由監測膜間壓力差的上昇來判定積垢程度。以2週內的壓力差上昇是否超過25kPa為標準。 The fouling characteristics of the membrane were investigated using actual sludge fluid. The apparatus was an impregnated membrane separation activated sludge method test apparatus (Model IMF-5) manufactured by Miyamoto Seisakusho Co., Ltd. The activated sludge liquid was adjusted so that the MLSS concentration in the apparatus tank was about 10,000 mg/L, and the 匣 type filter which attached the film to the both surfaces was provided. The filtration filtration operation was performed with a peristaltic pump at a filtration rate of a membrane area of 0.6 m 3 /day per 1 m 2 . Continuous operation is performed without setting the operation stop time during the filtration operation, and continuous aeration is performed from the lower portion of the 匣 type filter membrane. The operation was continued for 2 weeks, and the degree of fouling was determined by monitoring the rise in the pressure difference between the membranes. It is based on whether the pressure difference rise within 2 weeks exceeds 25 kPa.

(實施例1~4及比較例1~4) (Examples 1 to 4 and Comparative Examples 1 to 4)

首先將膜基材裁切為特定大小後,邊注意不要捲入皺褶邊固定於製膜用框架。接著,將膜基材靜靜地浸漬於由形成膜之高分子、溶劑、非溶劑構成之溶液(製膜原料液)中,放置1分鐘。之後,將含浸於製膜原料液之基材慢慢的拉起後,放置在調整到特定溫度、濕度之乾燥區(恆溫恆濕箱中)10分鐘,來形成膜。接著對如此進行所製作的膜施加羥丙基纖維素(HPC)塗布。 After the film substrate is first cut to a specific size, it is fixed to the film forming frame while being careful not to be wound into the wrinkles. Next, the film substrate was immersed in a solution (film-forming material liquid) composed of a polymer, a solvent, and a non-solvent which form a film, and left for 1 minute. Thereafter, the substrate impregnated with the film forming raw material liquid was slowly pulled up, and then placed in a drying zone (in a constant temperature and humidity chamber) adjusted to a specific temperature and humidity for 10 minutes to form a film. Next, the film thus produced was applied with hydroxypropylcellulose (HPC).

(實施例5、6) (Examples 5 and 6)

使用將基材輥設置於退繞用自由輥,經過放入了製膜原料液的含浸浴,通過乾燥區,以捲取機捲取之連續製膜裝置來進行製膜。將膜基材通過含浸浴所耗費時間調整為1分鐘,慢慢的捲取。此時乾燥區亦在特定的溫度、濕度預備。對如此進行所製作的膜實施HPC塗布處理。 The film roll was placed on the unwinding free roll, and the film was formed by passing through the impregnation bath in which the film forming material liquid was placed, and passing through the drying zone to a continuous film forming apparatus which was taken up by a winder. It took time for the film substrate to pass through the impregnation bath to 1 minute, and it was slowly taken up. At this time, the drying zone is also prepared at a specific temperature and humidity. The film thus produced was subjected to HPC coating treatment.

HPC塗布係依以下要領進行。首先,在乙醇:RO水=60/40(重量比)的混合溶液中,以使HPC成為0.6重量%之方式 加以溶解,來調製HPC溶液,將在上面製作的膜慢慢浸入HPC溶液中(以不會混進氣泡的方式,從端部開始)。在室溫下浸漬30分鐘的後膜取出,除去剩餘的附著液,輕輕水洗。之後,慢慢浸入60℃的RO水,靜置30分鐘。取出膜,予以風乾結束處理。又,在風乾時的溫濕度係在溫度20~30℃、濕度40~70%之範圍。 HPC coating is carried out according to the following methods. First, in a mixed solution of ethanol:RO water=60/40 (weight ratio), in order to make HPC 0.6% by weight The solution was dissolved to prepare a HPC solution, and the film prepared above was slowly immersed in the HPC solution (starting from the end in such a manner that bubbles were not mixed). After immersing for 30 minutes at room temperature, the film was taken out, and the remaining adhering liquid was removed, and washed gently with water. Thereafter, the RO water at 60 ° C was slowly immersed and allowed to stand for 30 minutes. The film was taken out and air-dried to finish the treatment. Moreover, the temperature and humidity during air drying are in the range of 20 to 30 ° C and a humidity of 40 to 70%.

(比較例5) (Comparative Example 5)

製作與實施例2相同組成之由高分子、溶劑與非溶劑所構成的溶液後,以相對於已溶解的高分子濃度為10重量%的方式添加蔗糖脂肪酸酯(第一工業藥品製DK ESTER SS),攪拌至成為均勻的溶液為止。將基材浸漬於此液來製作膜。除了不作HPC塗布以外,膜的製成方法與實施例2相同。 After the solution of the polymer, the solvent, and the non-solvent having the same composition as in Example 2 was prepared, sucrose fatty acid ester (the first industrial drug manufactured by DK ESTER) was added so as to be 10% by weight based on the dissolved polymer concentration. SS), stir until a homogeneous solution. The substrate was immersed in this liquid to prepare a film. The film was produced in the same manner as in Example 2 except that the coating was not performed by HPC.

實施例1~6及比較例1~5的膜基材、製造方法及評價結果之細節分別示於表1~3。 The details of the film substrate, the production method, and the evaluation results of Examples 1 to 6 and Comparative Examples 1 to 5 are shown in Tables 1 to 3, respectively.

由表2的結果明顯可知,實施例1~6能得到具有優良的強伸度特性(高降伏強度與小降伏伸長率),並具有高透水性能與良好的起泡點之膜。此外,於膜構造面能實現高的膜表面開孔率與細孔數、適度鬆散的中間層構造,藉由此等膜構造與對膜的HPC塗布處理之相乘效果,可得到在實際的污泥液之過濾測試的優良結果(壓力差上昇小)。另一方面,比較例1因膜表面開孔率低,有實際的污泥液容易積垢之問題,比較例2的起泡點為低值,無法稱為分離能力充分,於初期被觀察到污泥滲漏。而比較例3的強度不充分,在減壓過濾中發現膜變形,於使用時破損與性能降低的風險高,比較例4因厚度過厚而透水性低落,預料過濾效率會惡化。比較例5因為改變了親水化配方,在浸漬熱水後的純水通量保持率低,疑似親水化劑脫落,結果變成實際的污泥液容易積垢。 As is apparent from the results of Table 2, Examples 1 to 6 were able to obtain a film having excellent tensile properties (high relief strength and small elongation at break) and having high water permeability and good foaming point. In addition, a high membrane surface opening ratio and a fine pore number and a moderately loose intermediate layer structure can be realized on the membrane structural surface, whereby the multiplication effect of the membrane structure and the HPC coating treatment on the membrane can be obtained in practice. Excellent results of the filtration test of the sludge liquid (the pressure difference rises little). On the other hand, in Comparative Example 1, since the open porosity of the film surface was low, there was a problem that the actual sludge liquid was likely to be fouled, and the bubble point of Comparative Example 2 was low, which was not sufficient as the separation ability, and was observed at the initial stage. Sludge leaking. On the other hand, the strength of Comparative Example 3 was insufficient, and the film was found to be deformed under reduced pressure filtration, and the risk of breakage and performance was high at the time of use. In Comparative Example 4, the thickness was too large and the water permeability was lowered, and the filtration efficiency was expected to deteriorate. In Comparative Example 5, since the hydrophilization formulation was changed, the pure water flux retention rate after immersion in hot water was low, and it was suspected that the hydrophilizing agent fell off, and as a result, the actual sludge liquid was easily fouled.

〔產業利用性〕 [Industry Utilization]

本發明的高分子多孔質膜因在具有能承受長期使用的充分強度的同時,透水性、耐積垢性等膜性能優良,故極適合排水處理。 The porous polymer membrane of the present invention is excellent in membrane properties such as water permeability and fouling resistance because it has sufficient strength for long-term use, and is therefore highly suitable for drainage treatment.

圖1(a)及(b)顯示膜表面附近的5000倍之掃描電子顯微鏡相片,圖1(a)、圖1(b)分別顯示實施例2、3的膜的相片。 Fig. 1 (a) and (b) show scanning electron micrographs at 5000 times in the vicinity of the surface of the film, and Figs. 1(a) and 1(b) show photographs of the films of Examples 2 and 3, respectively.

Claims (8)

一種高分子多孔質膜,其係用於浸漬於活性污泥中,並自活性污泥液中得到濾液的平膜之高分子多孔質膜,其特徵為滿足下述A)~E)之條件:A)純水通量為20~50mL/cm2/min/bar;B)在純水中的起泡點為0.08~0.3MPa;C)高分子多孔質膜係由聚氯乙烯及/或氯化聚氯乙烯所構成;D)在以5000倍電子顯微鏡觀察高分子多孔質膜的與被處理液接觸之表面時,膜表面開孔率為25~45%,平均細孔徑為0.2~1.0μm,於1平方微米內存在的細孔數為0.5~5個細孔;E)在以5000倍電子顯微鏡觀察高分子多孔質膜的膜截面時,從與被處理液接觸之表面往內層部分係成為逐漸稀疏的構造,相對於在與被處理液接觸的表面附近部分,內層部分的高分子網絡之空隙率為1~3倍。 A porous polymer membrane for immersing in an activated sludge and obtaining a flat porous membrane of a filtrate from an activated sludge liquid, which is characterized by satisfying the following conditions A) to E) : A) pure water flux is 20~50mL/cm 2 /min/bar; B) foaming point in pure water is 0.08~0.3MPa; C) polymer porous membrane system is made of polyvinyl chloride and/or When chlorochlorinated polyvinyl chloride is used; D) when the surface of the porous polymer membrane is in contact with the liquid to be treated by a 5,000-fold electron microscope, the membrane surface opening ratio is 25 to 45%, and the average pore diameter is 0.2 to 1.0. Μm, the number of pores present in 1 square micron is 0.5 to 5 pores; E) when observing the membrane cross section of the porous polymer membrane with a 5000-fold electron microscope, from the surface in contact with the liquid to be treated to the inner layer The part is a gradually sparse structure, and the porosity of the polymer network of the inner layer portion is 1 to 3 times with respect to the portion near the surface in contact with the liquid to be treated. 如申請專利範圍第1項之高分子多孔質膜,其係滿足下述F)~H)之條件:F)浸漬於60℃的熱水4週再予以乾燥後所測定得到的純水通量之保持率為80%以上;G)膜的厚度為80~150μm;H)於縱向、橫向上二者之每15mm寬的降伏強度均為17~52N,且降伏伸長率均為1~5%。 The porous polymer membrane of the first aspect of the patent application satisfies the following conditions F) to H): F) pure water flux measured after being immersed in hot water at 60 ° C for 4 weeks and then dried. The retention rate is 80% or more; G) the thickness of the film is 80 to 150 μm; H) the relief strength per 15 mm width in both the longitudinal direction and the lateral direction is 17 to 52 N, and the elongation at break is 1 to 5%. . 如申請專利範圍第1或2項之高分子多孔質膜,其中高分子多孔質膜係由:用以形成網目狀網絡構造之高分子材料所構成之膜原料、與用以支持它之不織布所構成之膜基材 來形成。 The polymer porous membrane according to claim 1 or 2, wherein the polymer porous membrane is composed of a membrane material composed of a polymer material for forming a mesh network structure, and a non-woven fabric for supporting the same. Membrane substrate To form. 如申請專利範圍第3項之高分子多孔質膜,其中膜基材係滿足下述I)~K)之條件:I)纖維徑為5~12μm;J)厚度為80~150μm,且每1μm厚的單位面積重量為0.4~0.8g/m2;K)於縱向、橫向上二者之每15mm寬的降伏強度均為15~50N,且降伏伸長率均為1~5%。 The porous membrane of the polymer of claim 3, wherein the membrane substrate satisfies the following conditions I) to K): I) the fiber diameter is 5 to 12 μm; J) the thickness is 80 to 150 μm, and each 1 μm The thickness per unit area is 0.4-0.8 g/m 2 ; K) the tensile strength of each 15 mm width in both the longitudinal direction and the transverse direction is 15 to 50 N, and the elongation at break is 1 to 5%. 如申請專利範圍第1至4項中任一項之高分子多孔質膜,其中高分子多孔質膜的表面係經以羥丙基纖維素親水化處理的。 The porous polymer membrane according to any one of claims 1 to 4, wherein the surface of the porous polymer membrane is hydrophilized by hydroxypropylcellulose. 一種製造方法,其係包含將由不織布所構成的膜基材含漬於含有高分子材料、溶劑、及非溶劑之高分子溶液中並予以乾燥之步驟的製造如申請專利範圍第1至5項中任一項之高分子多孔質膜之方法,其特徵為:高分子材料係聚氯乙烯及/或氯化聚氯乙烯,而非溶劑係包含異丙醇與丁醇,且前述非溶劑中的異丙醇/丁醇之重量百分率為20~80%。 A manufacturing method comprising the steps of: coating a film substrate composed of a non-woven fabric on a polymer solution containing a polymer material, a solvent, and a non-solvent, and drying the same as in the first to fifth patent claims; The method for producing a porous polymer membrane according to any one of the preceding claims, wherein the polymer material is polyvinyl chloride and/or chlorinated polyvinyl chloride, and the non-solvent comprises isopropanol and butanol, and the non-solvent The weight percentage of isopropanol/butanol is 20 to 80%. 如申請專利範圍第6項之製造方法,其中在高分子溶液中的高分子濃度為5~20重量%,且溶劑/非溶劑的重量比為1~3。 The manufacturing method of claim 6, wherein the polymer concentration in the polymer solution is 5 to 20% by weight, and the solvent/non-solvent weight ratio is 1 to 3. 如申請專利範圍第6或7項之製造方法,其中乾燥時的溫度為10~40℃、相對濕度為50~90%。 The manufacturing method of claim 6 or 7, wherein the drying temperature is 10 to 40 ° C and the relative humidity is 50 to 90%.
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