WO2003026792A1 - Activated carbon fiber and process for producing the same - Google Patents
Activated carbon fiber and process for producing the same Download PDFInfo
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- WO2003026792A1 WO2003026792A1 PCT/JP2002/009919 JP0209919W WO03026792A1 WO 2003026792 A1 WO2003026792 A1 WO 2003026792A1 JP 0209919 W JP0209919 W JP 0209919W WO 03026792 A1 WO03026792 A1 WO 03026792A1
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- activated carbon
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- carbon fiber
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- D—TEXTILES; PAPER
- D01—NATURAL OR MAN-MADE THREADS OR FIBRES; SPINNING
- D01F—CHEMICAL FEATURES IN THE MANUFACTURE OF ARTIFICIAL FILAMENTS, THREADS, FIBRES, BRISTLES OR RIBBONS; APPARATUS SPECIALLY ADAPTED FOR THE MANUFACTURE OF CARBON FILAMENTS
- D01F9/00—Artificial filaments or the like of other substances; Manufacture thereof; Apparatus specially adapted for the manufacture of carbon filaments
- D01F9/08—Artificial filaments or the like of other substances; Manufacture thereof; Apparatus specially adapted for the manufacture of carbon filaments of inorganic material
- D01F9/12—Carbon filaments; Apparatus specially adapted for the manufacture thereof
- D01F9/14—Carbon filaments; Apparatus specially adapted for the manufacture thereof by decomposition of organic filaments
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- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J20/00—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof
- B01J20/02—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material
- B01J20/20—Solid sorbent compositions or filter aid compositions; Sorbents for chromatography; Processes for preparing, regenerating or reactivating thereof comprising inorganic material comprising free carbon; comprising carbon obtained by carbonising processes
Definitions
- the present invention relates to a novel activated carbon fiber and a method for producing the same.
- Activated carbon fibers have different characteristics from granular or powdered activated carbon in not only their appearance but also their pore structure. 'Activated carbon fibers with such characteristics are widely used for various applications including adsorbents.
- activated carbon fibers are fibrous as the name implies, they generally have a larger exposed surface per unit weight than granular or powdered activated carbon. For this reason, it exhibits characteristics that it is easier to make contact with the object to be processed and that the pressure loss during passage of the object fluid can be reduced.
- Activated carbon fiber has a large specific surface area and has many micropores, so it is very effective for removing the smell of powder.
- the substance causing the moldy odor is a macromolecule, it is difficult to be trapped in the micropores of the activated carbon fiber and is not suitable for the activated carbon fiber.
- a main object of the present invention is to provide an activated carbon fiber which is excellent in both the performance of removing and adsorbing trihalomethanes and the performance of removing and adsorbing substances causing moldy odor.
- an activated carbon fiber having a specific microstructure can achieve the above object, and have completed the present invention.
- the present invention relates to the following activated carbon fiber and a method for producing the same.
- V (0.1) is greater than 200 c c / g
- V (0.1) / V (0.2) The value of V (0.1) / V (0.2) is 0.92 to 0.99,
- V (0.2) / V (0.8) is 0.80 to 0.95
- a method for producing activated carbon fibers for adsorption of trihalomethanes and moldy odor-causing substances comprising: (1) 0.01 to 5% by weight of at least one metal component of vanadium, platinum and iron as an activated carbon precursor.
- V (0.1) is 200 cc / g or more
- V (0.2) is 0.92 to 0.99
- V (0.2) ZV (0.8) is 0.80 to 0.95 and
- the activated carbon fiber has a relative pressure PZP in the nitrogen adsorption isotherm at 77.4 K. V (P / Po)
- V (0.1) The value of V (0.1) is 200 c cZg or more,
- V (0.1) / V (0.2) The value of V (0.1) / V (0.2) is 0.92 to 0.99,
- V (0.2) ZV (0.8) is 0.80 to 0.95 and
- V (0.8) / V (1.0) is 0.80 to 0.90
- a method for removing trioctanemethane and fungi-causing substances by passing water to be treated through a tubular body filled with activated carbon fibers according to the above item 1.
- micropore refers to a pore having a pore diameter of less than 20 A
- mesopore refers to a pore having a pore diameter of 20 to 500 A
- macropore refers to a fine pore.
- the activated carbon fiber of the present invention has a nitrogen adsorption isotherm at 77.4 K at a relative pressure PZP. V (P / Po)
- V (0.1) (hereinafter referred to as “a value”) is 200 c cZg or more
- V (0.1) ZV (0.2) (hereinafter referred to as “b value”) is 0.92 to 0.99
- V (0.2) ZV (0.8) (hereinafter referred to as “c value”) is 0.80 to 0.95 and
- V (0.8) ZV (1.0) (hereinafter referred to as “d value”) is 0.80 to 0.90
- the nitrogen adsorption isotherm is created as follows. Cool the activated carbon fiber to 77.4 K (boiling point of nitrogen), introduce nitrogen gas, and measure the adsorption amount of nitrogen gas V [cc / g] by the volumetric method. At this time, the pressure P [mmHg] of the nitrogen gas to be introduced is gradually increased to the saturated vapor pressure P of the nitrogen gas. The value divided by [mmHg] is the relative pressure PZP.
- the nitrogen adsorption isotherm is created by plotting the amount of adsorption with respect to each relative pressure. In this nitrogen adsorption isotherm, let the amount of nitrogen gas adsorbed at each relative pressure (PZPo) be V (P / Po).
- the nitrogen gas adsorption amount when the relative pressure is 0.1 is expressed as V (0.1).
- the nitrogen adsorption isotherm can be obtained by taking the relative pressure (P / P.) On the horizontal axis and the nitrogen gas adsorption amount V (P / Po) on the vertical axis.
- a commercially available automatic gas adsorption amount measuring device can be used.
- trade name “AUTOSORB-6” manufactured by QUANT CHROME) or the like can be preferably used.
- the value a is set to 200 cc / g or more, preferably 220 cc / g or more. If the a value is less than 200 ccZg, it may generally be difficult to effectively adsorb and remove the substance to be adsorbed.
- the b value is 0.92 to 0.99, preferably 0.95 to 0.99. If the b value is less than 0.92, the number of micropores and mesopores having a pore diameter close to the pore diameter of the micropores becomes excessive, so that the desired adsorption performance may not be obtained. is there. On the other hand, if the b value exceeds 0.99, the number of micropores and mesopores having a pore diameter close to that of the micropores becomes too small, so that the adsorption performance may be reduced.
- the c value is set to 0.80 to 95, preferably 0.85 to 0.95. If the c value is less than 0.80, the mesopores having a pore diameter of about 20 to 100 A are excessive, and the effect of the present invention may not be obtained. If the c value exceeds 0.95, the number of mesopores in the vicinity of the pore diameter of 20 to 100 A becomes too small, so that the effect as the water purification material of the present invention may not be obtained.
- the d value is 0.80 to 0.90, preferably 0.82 to 0.90. If the d value is less than 0.80, the macropores and the mesopores having a pore diameter close to the macropore diameter become excessive, so that the desired adsorption performance may not be obtained. You. If the d-value exceeds 0, 90, the macropores and the mesopores having a pore diameter close to the macropore diameter become too small, so that the performance as the material for water purification and purification etc. of the present invention is reduced. The power may not be exerted.
- the activated carbon fiber of the present invention can be suitably used for conventional activated carbon fiber applications.
- it can be suitably used as a material for adsorbing and removing trihalomethanes and fungi-causing substances. Therefore, it can be used as a material for water purification and gas purification.
- the material of the present invention may be used as it is instead of a known adsorbent in a water purifier or the like.
- the present invention also includes a method for removing trihalomethanes and moldy odor-causing substances using the activated carbon fibers.
- the tubular body filled with the activated carbon fiber of the present invention by passing water to be treated through the tubular body filled with the activated carbon fiber of the present invention, trihalomethines and fungal odor-causing substances in the water to be treated can be adsorbed and removed.
- the amount of water passed, the amount of the material of the present invention, and the like may be in accordance with known methods and conditions.
- the activated carbon fiber of the present invention may be produced by any method as long as it has the above-mentioned a to d values.
- the following production method is preferable.
- the activated carbon fiber of the present invention in a method for producing an activated carbon fiber by melt-spinning, infusibilizing, and activating the activated carbon precursor, at least one metal component of vanadium, platinum, and iron is used as the activated carbon precursor. According to the method characterized by using a pitch containing 1 to 5% by weight, the activated carbon fiber of the present invention can be obtained more reliably.
- the metal component is at least one of vanadium, platinum and iron.
- the type of metal to be combined, the ratio thereof, and the like may be appropriately set according to the use of the activated carbon fiber, the purpose of use, and the like.
- the content of the metal component is adjusted so as to be 0.01 to 5% by weight, preferably 0.1 to 2% by weight in the activated carbon precursor. If the content of the metal component is less than 0.01% by weight, activated carbon fibers having the above a-values-d cannot be obtained due to weakening of the action of the metal during the activation reaction. There is. Conversely, if it exceeds 5% by weight, Since the metal component condenses and forms in the charcoal, the physical strength of the activated carbon fiber is remarkably reduced, which may make it impractical as a water purification material.
- the content of the metal component is not a content as a metal compound but a content in terms of a metal element, and is a value measured by an ICP emission spectrometry.
- the activated carbon precursor can be prepared, for example, by mixing a compound containing the metal component (metal compound) and pitch.
- the pitch is not particularly limited as long as it can be activated carbon by infusibilization, carbonization, and the like, and can be mixed with a metal compound.
- any of petroleum pitch, coal pitch, synthetic pitch and the like can be used.
- the optical properties may be either isotropic or anisotropic.
- an activated carbon precursor containing pitch and a metal component may be obtained by mixing and stirring a coal tar, which is a raw material for pitch, and a metal compound in a solvent, and then performing distillation under reduced pressure. it can.
- the metal compound is not particularly limited as long as these metal components are contained, and any of an inorganic compound and an organic compound can be used.
- the inorganic compound for example, inorganic salts such as chloride, nitrate, and acetate are used. Specifically, iron chloride, iron nitrate, iron acetate and the like can be exemplified.
- the organic compound an organic metal complex of the above metal component and acetylacetone / cyclopentene is used. Specifically, iron trisacetyl acetatonate, iron acetyl acetatonate, trissix pen penis genil iron and the like can be exemplified.
- the method of mixing the metal compound and the pitch is not limited as long as they can be uniformly mixed.
- the metal compound and the pitch may be mixed as they are, or both may be mixed in an appropriate solvent.
- the solvent is not particularly limited as long as it can dissolve both the metal compound and the pitch.
- Pitch to be used is selected from known solvents such as quinoline, benzene, dichloromethane, toluene, xylene, tetrahydrofuran, methanol, and ethanol. And the type of the metal compound may be appropriately selected.
- quinoline or the like can be used.
- the amount of the solvent used is not particularly limited as long as a uniform activated carbon precursor can be obtained, and may be appropriately set according to the type of the solvent, the metal compound, and the like to be used.
- the obtained activated carbon precursor After spinning the obtained activated carbon precursor, it is subjected to infusibilization treatment and / or carbonization treatment and then to activation treatment, whereby the activated carbon fiber of the present invention can be obtained.
- the spinning method, the infusibilization treatment, the carbonization treatment and the activation treatment are preferably carried out by the following methods.
- the spinning method can be performed according to a known melt spinning method.
- the melting temperature and the spinning temperature are generally set to a temperature equal to or higher than the softening point of the activated carbon precursor, and preferably set to a temperature higher by 30 to 100 ° C. than the softening point.
- the molten activated carbon precursor is sent to the nozzle of a spinning machine, and is discharged from a nozzle surface having many pores while forming fibers in an atmosphere controlled at a spinning temperature or lower.
- the activated carbon precursor is heated from a temperature below its melting point to about 400 ° C at a rate of 0.1 to 10 ° CZ in an inert gas atmosphere or an oxygen-containing gas atmosphere. Can be implemented.
- the activated carbon precursor is heated to about 800 to 1200 ° C. at a temperature increasing rate of 5 to 10 ° C.Z under an inert gas atmosphere such as nitrogen gas and argon gas. It can be implemented by maintaining the maximum temperature at that time for a maximum of about 10 minutes.
- the activation treatment is an activated carbon precursor that has been subjected to infusibilizing treatment and Z or carbonization treatment in a gas atmosphere in which water vapor, carbon dioxide, oxygen, a mixed gas thereof, and these gases are diluted with an inert gas such as nitrogen. Is held at a temperature of about 800 to 1200 ° C. for about 5 to 120 minutes.
- the activated carbon precursor to be subjected to the carbonization treatment or the activation treatment preferably contains 5% by weight or more of oxygen atoms.
- oxygen atoms are contained in an amount of 5% by weight or more, when the oxygen atoms are desorbed in the carbonization or activation reaction, the metal components interact with each other. The effect of appropriately perforating mesopores having a pore diameter close to the pore diameter of the pores is obtained.
- the content of oxygen atoms can be appropriately adjusted under infusibilizing conditions such as infusibilizing temperature and infusibilizing time.
- the nitrogen gas of the activated carbon fiber thus obtained is used.
- the nitrogen gas adsorption amount at relative pressure P / P Q is defined as V (P / Po)
- V (0.1) is greater than 200 c c / g
- V (0.1) / V (0.2) The value of V (0.1) / V (0.2) is 0.92 to 0.99,
- V (0.2) / V (0.8) is 0.80 to 0.95
- V (0.8) / V (1.0) is 0.80 to 0.90
- the method for measuring the nitrogen gas adsorption amount may be the same as described above.
- the present invention also includes a method for selecting activated carbon fibers for adsorbing trihalomethanes and fungi-causing substances. That is, a method for selecting activated carbon fibers for adsorbing trioctanes and moldy odor causing substances,
- V (0.1) is greater than 200 c c / g
- V (0.1) / V (0.2) The value of V (0.1) / V (0.2) is 0.92 to 0.99,
- V (0.2) / V (0.8) is 0.80 to 0.95
- V (0.8) / V (1.0) is 0.80 to 0.90
- the present invention encompasses a method characterized by selecting an activated carbon fiber that satisfies all conditions.
- This selection method can be applied to all activated carbon fibers, including activated carbon fibers produced by a method other than the above-mentioned production method.
- the method for measuring the nitrogen gas adsorption amount may be the same as described above.
- Activated carbon fibers satisfying all of the above conditions (a) and (b) exhibit an excellent effect as a material for adsorbing trihalomenes and fungal odor-causing substances.
- the size of the molecules of trihalomethanes is not so large that they cannot penetrate into the pores of Miku like the substances that cause moldy odor.
- the activated carbon fiber of the present invention exerts an excellent effect as an adsorbent capable of removing virtually all of low molecular substances represented by a odor of lime, macromolecules such as trichloromethanes, and substances causing a moldy odor. be able to. That is, the activated carbon fiber of the present invention having such characteristics is useful as an activated carbon fiber for adsorbing trioctane compounds and fungi-causing substances, and specifically, a water purification material and a gas purification material. Etc. can be suitably used.
- Figure 1 shows the nitrogen adsorption isotherms of the iron-containing activated carbon fiber of Example 1, the platinum-containing activated carbon fiber of Example 2, the metal-free activated carbon fiber of Comparative Example 1, and the iron-containing activated carbon fiber of Comparative Example 3. It is a figure showing a line.
- the amount of nitrogen gas adsorbed on the activated carbon fiber was measured using "AUTOSORB-6" (trade name, manufactured by QUANTCHROME).
- the spun pitch fibers are heated in the air from room temperature at a heating rate of 1 to 10 and held at the maximum temperature of 364 ° C for 4 minutes, and the infusibilizing treatment is performed over a total infusibilizing time of 65 minutes. Was done.
- the infusibilized pitch fiber was exposed to saturated steam at 850 ° C. for 60 minutes in a nitrogen atmosphere to perform an activation treatment to obtain an iron-containing activated carbon fiber.
- Table 1 shows a to d values of the obtained activated carbon fibers.
- Figure 1 shows the nitrogen adsorption isotherm.
- a coal tar pitch was obtained in the same manner as in Example 1, except that 5.7 g of acetyl acetonato platinum was used instead of 6 g of acetyl acetonato iron.
- the platinum content of this pitch was 2.60% by weight.
- the spun pitch fibers were heated from room temperature in the air at a rate of temperature increase of 2 ° C / min, and kept at 375 for 15 minutes for infusibility treatment.
- the infusibilized pitch fiber was exposed to saturated steam at 850 for 35 minutes in a nitrogen atmosphere to perform an activation treatment to produce a platinum-containing activated carbon fiber.
- Table 1 shows a to d values of the obtained activated carbon fibers.
- Figure 1 shows the nitrogen adsorption isotherm.
- Activated carbon fibers were produced in the same manner as in Example 1, except that no metal compound was mixed and the activation treatment time was 30 minutes.
- Table 1 shows a to d values of the obtained activated carbon fibers.
- Figure 1 shows the nitrogen adsorption isotherm.
- Activated iron-containing carbon fibers were produced in the same manner as in Example 1 except that the maximum temperature in the infusibilization treatment was changed to 26.4 t :. At this time, the oxygen atom content in the activated carbon precursor was 2.55%.
- Table 1 shows a to d values of the obtained activated carbon fibers.
- Figure 1 shows the nitrogen adsorption isotherm. Tatami mat
- JI SS-320 1 Acrylic container was filled with 8.4 g of a milled sample based on the “Test method for household water purifiers (continuous method)” so as to be 48 mm (diameter) ⁇ 30 mm (height). Then, raw water having a 2-methylisoborneol concentration of 5.5 ppt was passed at a flow rate of 3 L / min. Outlet concentration C and initial concentration C at this time. The flow rate at which the ratio CZCQ became 0.2 was defined as the filtration capacity.
- the above analyzer was performed by the purge trap method using the trade name “GCMS-QP 5050” (manufactured by Shimadzu Corporation). Table 2
- the activated carbon fiber of the present invention can exert excellent effects not only on the adsorption and removal performance of trioctane methanes but also on the adsorption and removal performance of the fungi-causing substance.
- Comparative Example 2 it was difficult to carry out a filtration ability test due to the remarkable powdering.
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Abstract
Description
明 細 書 Specification
活性炭素繊維及びその製造方法 Activated carbon fiber and method for producing the same
技 術 分 野 Technical field
本発明は、 新規な活性炭素繊維及びその製造方法に関する。 The present invention relates to a novel activated carbon fiber and a method for producing the same.
背 景 技 術 Background technology
活性炭素繊維は、 その外観形状のみならず、 細孔構造も粒状又は粉末状活性炭 と異なる特徴を有している。'かかる特徴をもつ活性炭素繊維は、 吸着材をはじめ とする様々な用途に幅広く利用されている。 Activated carbon fibers have different characteristics from granular or powdered activated carbon in not only their appearance but also their pore structure. 'Activated carbon fibers with such characteristics are widely used for various applications including adsorbents.
活性炭素繊維は、 その名の通り繊維状であることから、 一般に粒状又は粉末状 活性炭と比べ単位重量当たりの露出表面が大きい。 このため、 被処理物とより接 触しやすく、 また被処理物流体通過時の圧力損失を低く抑えられるという特性を 発揮する。 Since activated carbon fibers are fibrous as the name implies, they generally have a larger exposed surface per unit weight than granular or powdered activated carbon. For this reason, it exhibits characteristics that it is easier to make contact with the object to be processed and that the pressure loss during passage of the object fluid can be reduced.
特に飲料水の浄化に関し、 残留塩素 (いわゆる 「カルキ臭」 ) を除去するため に活性炭素繊維を吸着材とした浄水器が広く用いられている。 ところが、 近年で は、 河川水質の富栄養化が問題視され、 水道水中の有機塩素化合物 (いわゆる 「トリハロメタン類」 ) の除去、 さらには微生物に由来するとされる 「黴臭」 の 除去が 「カルキ臭」 の除去とともに要求されている。 Especially for drinking water purification, water purifiers using activated carbon fibers as adsorbents are widely used to remove residual chlorine (so-called “smelling smell”). However, in recent years, eutrophication of river water quality has been regarded as a problem, and removal of organochlorine compounds (so-called “trihalomethanes”) in tap water and removal of “fungus odor” which is considered to be derived from microorganisms have been called “calcium”. It is required with the removal of "odor".
活性炭素繊維は、 比表面積が大きく、 多くのミクロ細孔を有することから、 力 ルキ臭の除去には非常に有効である。 他方、 黴臭の除去については、 黴臭原因物 質が巨大分子であるため、 活性炭素繊維のミクロ細孔内に捕捉されにくく、 活性 炭素繊維に不向きである。 Activated carbon fiber has a large specific surface area and has many micropores, so it is very effective for removing the smell of powder. On the other hand, in removing the moldy odor, since the substance causing the moldy odor is a macromolecule, it is difficult to be trapped in the micropores of the activated carbon fiber and is not suitable for the activated carbon fiber.
活性炭素繊維のトリハロメタン類の除去能力改善については、 これまでに例え ぱ特開平 6— 9 9 0 6 4号、 特開平 7— 1 4 5 5 1 6号、 特開平 1 0— 2 4 4 2 5 3号、 特開平 1 1— 2 4 0 7 0 8号、 特開平 1 2 - 2 5 6 9 9 9号公報等が提 案されている。 これらはいずれも活性炭素繊維に吸着したトリハロメタン類を脱 着再生して活性炭素繊維の寿命の延命を図ろうとするものである。 さらに、 トリ ハロメタン類と黴臭原因物質を同時に除去する技術として、 本出願人はさきに特 開平 1 1一 2 4 0 7 0 7号公報において、 ミクロ細孔のみならずメソ細孔をも有 する活性炭素繊維を提案している。 しかしながら、 これらの従来技術は、 トリハロメタン類と黴臭原因物質とをと もに除去するための材料としては必ずしも十分なものとは言えない。 特に、 処理 水の流通しない状態 (すなわち、 静的条件) における吸着能力 (いわゆる平衡吸 着能力) のみならず、 水浄化等での実際上の使用条件である通水状態における除 去能力について改善すべき余地が大きい。 Improvements in the ability of activated carbon fibers to remove trihalomethanes have been described, for example, in JP-A-6-99064, JP-A-7-1455506, and JP-A-10-24442. No. 53, Japanese Unexamined Patent Application Publication No. 11-240708, Japanese Unexamined Patent Application Publication No. 1-256969, etc. have been proposed. These are all intended to extend the life of the activated carbon fiber by desorbing and regenerating the trihalomethanes adsorbed on the activated carbon fiber. Furthermore, as a technique for simultaneously removing trihalomethanes and fungal odor-causing substances, the present applicant has disclosed in Japanese Patent Application Laid-open No. Hei 11-244707 that not only micropores but also mesopores. Activated carbon fiber is proposed. However, these conventional techniques are not necessarily sufficient as materials for removing both trihalomethanes and fungi-causing substances. In particular, it has improved not only the adsorption capacity (ie, the so-called equilibrium adsorption capacity) when the treated water does not flow (that is, under static conditions), but also the removal capacity when the treated water is used, which is the actual use condition for water purification. There is a lot of room to do.
発 明 の 開 示 Disclosure of the invention
本発明の主な目的は、 トリハロメタン類の除去吸着性能及び黴臭原因物質の除 去吸着性能がともに優れた活性炭素繊維を提供することにある。 A main object of the present invention is to provide an activated carbon fiber which is excellent in both the performance of removing and adsorbing trihalomethanes and the performance of removing and adsorbing substances causing moldy odor.
本発明者は、 従来技術の問題に鑑みて研究を重ねた結果、 特定の微細構造を有 する活性炭素繊維が上記目的を達成できることを見出し、 本発明を完成するに至 つた。 As a result of repeated studies in view of the problems of the prior art, the present inventors have found that an activated carbon fiber having a specific microstructure can achieve the above object, and have completed the present invention.
すなわち、 本発明は、 下記に示す活性炭素繊維及びその製造方法に係るもので ある。 That is, the present invention relates to the following activated carbon fiber and a method for producing the same.
1. 77. 4 Kにおける窒素吸着等温線において、 相対圧力 P/P。での窒素ガ ス吸着量を V (P/Po) として、 1. Relative pressure P / P on nitrogen adsorption isotherm at 77.4 K. V (P / Po)
(a) V (0.1) の値が 200 c c/g以上、 (a) V (0.1) is greater than 200 c c / g,
(b) V (0.1) /V (0.2) の値が 0. 92〜0. 99、 (b) The value of V (0.1) / V (0.2) is 0.92 to 0.99,
(c) V (0.2) /V (0.8) の値が 0. 80〜0. 95及び (c) V (0.2) / V (0.8) is 0.80 to 0.95 and
(d) V (0.8) ZV (1.0) の値が 0. 80〜0. 90 (d) V (0.8) ZV (1.0) is 0.80 to 0.90
をすベて満たすことを特徴とする活性炭素繊維。 Activated carbon fiber characterized by satisfying all requirements.
2. 前記項 1記載の活性炭素繊維を含む浄水精製用材料。 2. A water purification material containing the activated carbon fiber according to the above item 1.
3. トリハロメタン類及び黴臭原因物質の吸着用活性炭素繊維の製造方法であ つて、 (1) 活性炭前駆体としてバナジウム、 白金及び鉄の少なくとも 1種の金 属成分を 0. 01〜5重量%含有するピッチを用い、 この前駆体を溶融紡糸し、 不 化処理し、 賦活処理することにより活性炭素繊維を得る工程、 及び 3. A method for producing activated carbon fibers for adsorption of trihalomethanes and moldy odor-causing substances, comprising: (1) 0.01 to 5% by weight of at least one metal component of vanadium, platinum and iron as an activated carbon precursor. A step of melt-spinning the precursor, passivating and activating the precursor using the contained pitch to obtain an activated carbon fiber, and
(2) 得られた活性炭素繊維の窒素ガス吸着量を測定することにより、 77. 4 Kにおける窒素吸着等温線において、 相対圧力 PZP。での窒素ガス吸着量を V (P/Po) として、 (2) By measuring the nitrogen gas adsorption amount of the obtained activated carbon fiber, the relative pressure PZP in the nitrogen adsorption isotherm at 77.4 K was obtained. V (P / Po)
(a) V (0.1) の値が 200 c c/g以上、 (b) V (0.1) /Ϋ (0.2) の値が 0. 92〜0. 99、 (a) V (0.1) is 200 cc / g or more, (b) The value of V (0.1) / Ϋ (0.2) is 0.92 to 0.99,
(c) V (0.2) ZV (0.8) の値が 0. 80〜0. 95及び (c) V (0.2) ZV (0.8) is 0.80 to 0.95 and
(d) V (0.8) /Y (1.0) の値が 0. 80〜0. 90 (d) The value of V (0.8) / Y (1.0) is 0.80 to 0.90
をすベて満たす活性炭素繊維を選出する工程を有することを特徴とする製造方法。 A process for selecting activated carbon fibers that satisfy all of the requirements.
4. 活性炭素繊維を用いてトリ八ロメタン類及び黴臭原因物質を吸着除去する 方法であって、 4. A method for adsorbing and removing trioctanemethane and fungi-causing substances using activated carbon fiber,
当該活性炭素繊維が、 77. 4 Kにおける窒素吸着等温線において、 相対圧力 PZP。での窒素ガス吸着量を V (P/Po) として、 The activated carbon fiber has a relative pressure PZP in the nitrogen adsorption isotherm at 77.4 K. V (P / Po)
(a) V (0.1) の値が 200 c cZg以上、 , (a) The value of V (0.1) is 200 c cZg or more,,
(b) V (0.1) /V (0.2) の値が 0. 92〜0. 99、 (b) The value of V (0.1) / V (0.2) is 0.92 to 0.99,
(c) V (0.2) ZV (0.8) の値が 0. 80〜0. 95及び (c) V (0.2) ZV (0.8) is 0.80 to 0.95 and
(d) V (0.8) /V (1.0) の値が 0. 80〜0. 90 (d) The value of V (0.8) / V (1.0) is 0.80 to 0.90
をすベて満たすことを特徴とする方法。 A method characterized by satisfying all of
5. 前記項 1記載の活性炭素繊維が充填された管状体に被処理水を通水するこ とにより、 トリ八ロメタン類及び黴臭原因物質を除去する方法。 5. A method for removing trioctanemethane and fungi-causing substances by passing water to be treated through a tubular body filled with activated carbon fibers according to the above item 1.
以下、 本発明について詳細に説明する。 なお、 本発明において 「ミクロ細孔」 とは細孔直径が 20 A未満の細孔、 「メソ細孔」 とは細孔直径が 20〜 500 A の細孔、 「マクロ細孔」 とは細孔直径が 50 OAを超える細孔をいう。 Hereinafter, the present invention will be described in detail. In the present invention, “micropore” refers to a pore having a pore diameter of less than 20 A, “mesopore” refers to a pore having a pore diameter of 20 to 500 A, and “macropore” refers to a fine pore. A pore having a pore diameter of more than 50 OA.
1. 活性炭素繊維 1. Activated carbon fiber
本発明の活性炭素繊維は、 77. 4 Kにおける窒素吸着等温線において、 相対 圧力 PZP。での窒素ガス吸着量を V (P/Po) として、 The activated carbon fiber of the present invention has a nitrogen adsorption isotherm at 77.4 K at a relative pressure PZP. V (P / Po)
(1) V (0.1) の値 (以下 「a値」 という。 ) が 200 c cZg以上、 (1) When the value of V (0.1) (hereinafter referred to as “a value”) is 200 c cZg or more,
(2) V (0.1) ZV (0.2) の値 (以下 「b値」 という。 ) が 0. 92〜0. 9 9、 (2) The value of V (0.1) ZV (0.2) (hereinafter referred to as “b value”) is 0.92 to 0.99,
(3) V (0.2) ZV (0.8) の値 (以下 「c値」 という。 ) が 0. 80〜0. 9 5及び (3) The value of V (0.2) ZV (0.8) (hereinafter referred to as “c value”) is 0.80 to 0.95 and
(4) V (0.8) ZV (1.0) の値 (以下 「d値」 という。 ) が 0. 80〜0. 9 0 (4) The value of V (0.8) ZV (1.0) (hereinafter referred to as “d value”) is 0.80 to 0.90
をすベて満たすことを特徴とする。 本発明において、 上記窒素吸着等温線は次のようにして作成する。 活性炭素繊 維を 77. 4K (窒素の沸点) に冷却し、 窒素ガスを導入して容量法により窒素 ガスの吸着量 V [c c/g] を測定する。 このとき、 導入する窒素ガスの圧力 P [mmHg] を徐々に上げ、 窒素ガスの飽和蒸気圧 P。 [mmHg] で除した値を 相対圧力 PZP。として、 各相対圧力に対する吸着量をプロットすることにより窒 素吸着等温線を作成する。 この窒素吸着等温線において、 各相対圧力 (PZPo) における窒素ガス吸着量を V (P/Po) とする。 例えば、 相対圧力が 0. 1で ある場合の窒素ガス吸着量は V (0.1) と表記される。 窒素吸着等温線は、 図 1に 示すように、 横軸に相対圧力 (P/P。) をとり、 縦軸に窒素ガス吸着量を V (P /Po) をとれば良い。 窒素ガスの吸着量の測定に際しては、 市販の自動ガス吸着 量測定装置を用いることができる。 例えば、 商品名 「AUTOSORB— 6」 (QUANT CHROME製) 等を好適に用いることができる。 Is satisfied. In the present invention, the nitrogen adsorption isotherm is created as follows. Cool the activated carbon fiber to 77.4 K (boiling point of nitrogen), introduce nitrogen gas, and measure the adsorption amount of nitrogen gas V [cc / g] by the volumetric method. At this time, the pressure P [mmHg] of the nitrogen gas to be introduced is gradually increased to the saturated vapor pressure P of the nitrogen gas. The value divided by [mmHg] is the relative pressure PZP. The nitrogen adsorption isotherm is created by plotting the amount of adsorption with respect to each relative pressure. In this nitrogen adsorption isotherm, let the amount of nitrogen gas adsorbed at each relative pressure (PZPo) be V (P / Po). For example, the nitrogen gas adsorption amount when the relative pressure is 0.1 is expressed as V (0.1). As shown in Fig. 1, the nitrogen adsorption isotherm can be obtained by taking the relative pressure (P / P.) On the horizontal axis and the nitrogen gas adsorption amount V (P / Po) on the vertical axis. In measuring the nitrogen gas adsorption amount, a commercially available automatic gas adsorption amount measuring device can be used. For example, trade name “AUTOSORB-6” (manufactured by QUANT CHROME) or the like can be preferably used.
上記 a値は 200 c c/g以上とし、 好ましくは 220 c c/g以上とする。 a値が 200 c cZg未満の場合は、 一般に、 被吸着物質を効果的に吸着除去す ることが困難になるおそれがある。 The value a is set to 200 cc / g or more, preferably 220 cc / g or more. If the a value is less than 200 ccZg, it may generally be difficult to effectively adsorb and remove the substance to be adsorbed.
上記 b値は 0. 92〜0. 99とし、 好ましくは 0. 95〜0. 99とする。 b値が 0. 92未満の場合は、 ミクロ細孔とミクロ細孔の細孔直径に近い細孔直 径をもつメソ細孔とが過多となるため、 所望の吸着性能が得られなくなるおそれ がある。 他方、 b値が 0. 99を超えると、 ミクロ細孔とミクロ細孔の細孔直径 に近い細孔直径をもつメソ細孔とが過少となるため、 吸着性能が低下することが ある。 The b value is 0.92 to 0.99, preferably 0.95 to 0.99. If the b value is less than 0.92, the number of micropores and mesopores having a pore diameter close to the pore diameter of the micropores becomes excessive, so that the desired adsorption performance may not be obtained. is there. On the other hand, if the b value exceeds 0.99, the number of micropores and mesopores having a pore diameter close to that of the micropores becomes too small, so that the adsorption performance may be reduced.
上記 c値は 0. 80〜 95、 好ましくは 0. 85〜0. 95とする。 c値 が 0. 80未満の場合は、 細孔直径 20〜100A付近のメソ細孔が過多となる ため、 本発明の効果が得られなくなることがある。 c値が 0. 95を超えると、 細孔直径 20〜100A付近のメソ細孔が過少となるため、 本発明の浄水精製用 材料等としての効果が得られなくなる場合がある。 The c value is set to 0.80 to 95, preferably 0.85 to 0.95. If the c value is less than 0.80, the mesopores having a pore diameter of about 20 to 100 A are excessive, and the effect of the present invention may not be obtained. If the c value exceeds 0.95, the number of mesopores in the vicinity of the pore diameter of 20 to 100 A becomes too small, so that the effect as the water purification material of the present invention may not be obtained.
上記 d値は 0. 80〜0. 90、 好ましくは 0. 82〜0. 90とする。 d値 が 0. 80未満の場合は、 マクロ細孔とマクロ細孔の細孔直径に近い細孔直径を もつメソ細孔とが過多となるため、 所望の吸着性能が得られなくなるおそれがあ る。 d値が 0 , 9 0を超えると、 マクロ細孔とマクロ細孔の細孔直径に近い細孔 直径をもつメソ細孔とが過少となるため、 本発明の浄水精製用材料等としての能 力が発揮されない場合がある。 The d value is 0.80 to 0.90, preferably 0.82 to 0.90. If the d value is less than 0.80, the macropores and the mesopores having a pore diameter close to the macropore diameter become excessive, so that the desired adsorption performance may not be obtained. You. If the d-value exceeds 0, 90, the macropores and the mesopores having a pore diameter close to the macropore diameter become too small, so that the performance as the material for water purification and purification etc. of the present invention is reduced. The power may not be exerted.
本発明の活性炭素繊維は、 従来の活性炭素繊維の用途にも好適に用いることが できる。 特に、 トリハロメタン類及び黴臭原因物質の吸着除去用材料に好適に用 いることができる。 従って、 浄水精製用材料、 ガス精製用材料等として使用する ことができる。 例えば、 浄水精製用材料として用いる場合は、 公知の浄水器等に おける吸着材に代えて本発明材料をそのまま使用すれば良い。 本発明は、 上記活 性炭素繊維を用いるトリハロメタン類及び黴臭原因物質の除去方法も包含する。 具体的には、 本発明の活性炭素繊維が充填された管状体に被処理水を通水するこ とにより、 被処理水中のトリハロメ夕ン類及び黴臭原因物質を吸着除去すること ができる。 このときの通水量、 本発明材料の使用量等も公知の方法 ·条件に従え ば良い。 The activated carbon fiber of the present invention can be suitably used for conventional activated carbon fiber applications. In particular, it can be suitably used as a material for adsorbing and removing trihalomethanes and fungi-causing substances. Therefore, it can be used as a material for water purification and gas purification. For example, when used as a water purification material, the material of the present invention may be used as it is instead of a known adsorbent in a water purifier or the like. The present invention also includes a method for removing trihalomethanes and moldy odor-causing substances using the activated carbon fibers. Specifically, by passing water to be treated through the tubular body filled with the activated carbon fiber of the present invention, trihalomethines and fungal odor-causing substances in the water to be treated can be adsorbed and removed. At this time, the amount of water passed, the amount of the material of the present invention, and the like may be in accordance with known methods and conditions.
2 . 活性炭素繊維の製造方法 2. Manufacturing method of activated carbon fiber
本発明の活性炭素繊維は、 上記 a〜d値を具備するものが得られる限り、 どの ような方法で製造しても良いが、 例えば次のような製造方法によることが望まし い。 The activated carbon fiber of the present invention may be produced by any method as long as it has the above-mentioned a to d values. For example, the following production method is preferable.
すなわち、 活性炭前駆体を溶融紡糸し、 不融化処理し、 賦活処理することによ り活性炭繊維を製造する方法において、 当該活性炭前駆体としてバナジウム、 白 金及び鉄の少なくとも 1種の金属成分を 0 . 0 1〜5重量%含有するピッチを用 いることを特徴とする方法によつて、 本発明の活性炭素繊維をより確実に得るこ とができる。 That is, in a method for producing an activated carbon fiber by melt-spinning, infusibilizing, and activating the activated carbon precursor, at least one metal component of vanadium, platinum, and iron is used as the activated carbon precursor. According to the method characterized by using a pitch containing 1 to 5% by weight, the activated carbon fiber of the present invention can be obtained more reliably.
金属成分は、 バナジウム、 白金及び鉄の少なくとも 1種である。 2種以上の金 属成分を併用する場合、 組み合わせる金属の種類、 その割合等は活性炭素繊維の 用途、 使用目的等に応じて適宜設定すれば良い。 The metal component is at least one of vanadium, platinum and iron. When two or more metal components are used in combination, the type of metal to be combined, the ratio thereof, and the like may be appropriately set according to the use of the activated carbon fiber, the purpose of use, and the like.
金属成分の含有量は活性炭前駆体中 0 . 0 1〜 5重量%、 好ましくは 0 . 1〜 2重量%になるように調整する。 金属成分の含有量が 0 . 0 1重量%未満の場合 は、 賦活反応時の金属の作用が弱くなる等の理由により、 上記 a値〜 d値を有す る活性炭素繊維が得られなくなることがある。 逆に 5重量%を超える場合は、 活 性炭中で金属成分が凝縮しゃすくなり、 活性炭素繊維の物理的強度が著しく低下 するため、 浄水用素材等としての実用性を欠くことがある。 なお、 金属成分の含 有量は、 金属化合物としての含有量ではなく金属元素換算の含有量を示し、 I C P発光分析法により測定した値を示す。 The content of the metal component is adjusted so as to be 0.01 to 5% by weight, preferably 0.1 to 2% by weight in the activated carbon precursor. If the content of the metal component is less than 0.01% by weight, activated carbon fibers having the above a-values-d cannot be obtained due to weakening of the action of the metal during the activation reaction. There is. Conversely, if it exceeds 5% by weight, Since the metal component condenses and forms in the charcoal, the physical strength of the activated carbon fiber is remarkably reduced, which may make it impractical as a water purification material. The content of the metal component is not a content as a metal compound but a content in terms of a metal element, and is a value measured by an ICP emission spectrometry.
活性炭前駆体は、 例えば上記金属成分を含む化合物 (金属化合物) とピッチと を混合することによつて調製することができる。 The activated carbon precursor can be prepared, for example, by mixing a compound containing the metal component (metal compound) and pitch.
上記ピッチとしては、 不融化、 炭素化等により活性炭になり得、 しかも金属化 合物と混合可能なものであれば特に限定されない。 例えば、 石油系ピッチ、 石炭 系ピッチ、 合成ピッチ等のいずれも使用できる。 また、 光学的性質としても、 等 方性又は異方性のいずれであっても良い。 The pitch is not particularly limited as long as it can be activated carbon by infusibilization, carbonization, and the like, and can be mixed with a metal compound. For example, any of petroleum pitch, coal pitch, synthetic pitch and the like can be used. The optical properties may be either isotropic or anisotropic.
なお、 活性炭前駆体を調製する場合、 例えばピッチの原料であるコールタール と金属化合物とを溶媒中で混合 ·攪拌した後、 減圧蒸留することによりピッチと 金属成分を含む活性炭前駆体を得ることもできる。 In the case of preparing an activated carbon precursor, for example, an activated carbon precursor containing pitch and a metal component may be obtained by mixing and stirring a coal tar, which is a raw material for pitch, and a metal compound in a solvent, and then performing distillation under reduced pressure. it can.
金属化合物としては、 これらの金属成分が含まれていれば特に限定されず、 無 機化合物及び有機化合物のいずれも使用することができる。 無機化合物としては、 例えば塩化物、 硝酸塩、 及び酢酸塩等の無機塩類が用いられる。 具体的には、 塩 化鉄、 硝酸鉄、 酢酸鉄等を例示することができる。 また、 有機化合物としては、 上記金属成分とァセチルアセトンゃシクロペン夕ジェン等との有機金属錯体が用 いられる。 具体的には、 トリスァセチルァセトナト鉄、 ァセチルァセトナト鉄、 トリスシク口ペン夕ジェニル鉄等を例示することができる。 The metal compound is not particularly limited as long as these metal components are contained, and any of an inorganic compound and an organic compound can be used. As the inorganic compound, for example, inorganic salts such as chloride, nitrate, and acetate are used. Specifically, iron chloride, iron nitrate, iron acetate and the like can be exemplified. As the organic compound, an organic metal complex of the above metal component and acetylacetone / cyclopentene is used. Specifically, iron trisacetyl acetatonate, iron acetyl acetatonate, trissix pen penis genil iron and the like can be exemplified.
金属化合物とピッチとの混合方法は、 均一に混合できれば限定されず、 例えば 金属化合物とピッチとをそのまま混合したり、 あるいは適当な溶媒中で両者を混 合しても良い。 特に、 金属化合物とピッチとを溶媒中で混合することが好ましい。 溶媒としては、 金属化合物及びピッチの双方を溶解できるものであれば特に限 定されず、 キノリン、 ベンゼン、 ジクロロメタン、 トルエン、 キシレン、 テトラ ヒドロフラン、 メタノール、 エタノール等の公知の溶媒の中から、 用いるピッチ の種類、 金属化合物の種類に応じて適宜選択すれば良い。 例えば、 鉄化合物とし てァセチルアセトン錯体を用い、 ピッチとして石炭系等方性ピッチを用いる場合 には、 キノリン等を用いることができる。 溶媒の使用量は、 均一な活性炭前駆体が得られる限り特に限定されず、 使用す る溶媒、 金属化合物等の種類に応じて適宜設定すれば良い。 The method of mixing the metal compound and the pitch is not limited as long as they can be uniformly mixed. For example, the metal compound and the pitch may be mixed as they are, or both may be mixed in an appropriate solvent. In particular, it is preferable to mix the metal compound and the pitch in a solvent. The solvent is not particularly limited as long as it can dissolve both the metal compound and the pitch.Pitch to be used is selected from known solvents such as quinoline, benzene, dichloromethane, toluene, xylene, tetrahydrofuran, methanol, and ethanol. And the type of the metal compound may be appropriately selected. For example, when an acetylacetone complex is used as the iron compound and a coal-based isotropic pitch is used as the pitch, quinoline or the like can be used. The amount of the solvent used is not particularly limited as long as a uniform activated carbon precursor can be obtained, and may be appropriately set according to the type of the solvent, the metal compound, and the like to be used.
次いで、 得られた活性炭前駆体を紡糸した後、 不融化処理及び/又は炭素化処 理し、 次いで賦活処理を施すことによって本発明活性炭素繊維を得ることができ る。 上記紡糸方法、 不融化処理、 炭素化処理及び賦活処理は、 以下に示す方法で 実施することが好ましい。 Next, after spinning the obtained activated carbon precursor, it is subjected to infusibilization treatment and / or carbonization treatment and then to activation treatment, whereby the activated carbon fiber of the present invention can be obtained. The spinning method, the infusibilization treatment, the carbonization treatment and the activation treatment are preferably carried out by the following methods.
紡糸方法は、 公知の溶融紡糸方法に従って行うことができる。 溶融温度及び紡 糸温度は、 一般に活性炭前駆体の軟化点温度以上の温度とし、 好ましくは軟化点 よりも 3 0〜1 0 0 °C高い温度に設定する。 溶融した活性炭前駆体は、 紡糸機の ノズル部へ送液され、 多数の細孔を穿ったノズル面より、 紡糸温度以下に制御さ れた雰囲気中に繊維を形成しつつ吐出される。 The spinning method can be performed according to a known melt spinning method. The melting temperature and the spinning temperature are generally set to a temperature equal to or higher than the softening point of the activated carbon precursor, and preferably set to a temperature higher by 30 to 100 ° C. than the softening point. The molten activated carbon precursor is sent to the nozzle of a spinning machine, and is discharged from a nozzle surface having many pores while forming fibers in an atmosphere controlled at a spinning temperature or lower.
不融化処理は、 不活性ガス雰囲気又は酸素含有ガス雰囲気下において活性炭前 駆体をその融点以下の温度から昇温速度 0 . 1〜 1 0 °CZ分で 4 0 0 °C程度まで 加熱することによつて実施することができる。 In the infusibilization treatment, the activated carbon precursor is heated from a temperature below its melting point to about 400 ° C at a rate of 0.1 to 10 ° CZ in an inert gas atmosphere or an oxygen-containing gas atmosphere. Can be implemented.
炭素化処理は、 窒素ガス、アルゴンガス等の不活性ガス雰囲気下において、 活性 炭前駆体を昇温速度 5〜1 0 °CZ分で 8 0 0〜1 2 0 0 °C程度まで加熱し、 その ときの最大温度を最大限 1 0分程度維持することにより実施することができる。 賦活処理は、 水蒸気、 二酸化炭素、 酸素及びこれらの混合ガス並びにこれらの ガスを窒素等の不活性ガスで希釈したガス雰囲気中において、 不融化処理及び Z 又は炭素化処理が施された活性炭前駆体を 8 0 0〜 1 2 0 0 °C程度の温度で 5〜 1 2 0分程度保持することにより実施することができる。 In the carbonization treatment, the activated carbon precursor is heated to about 800 to 1200 ° C. at a temperature increasing rate of 5 to 10 ° C.Z under an inert gas atmosphere such as nitrogen gas and argon gas. It can be implemented by maintaining the maximum temperature at that time for a maximum of about 10 minutes. The activation treatment is an activated carbon precursor that has been subjected to infusibilizing treatment and Z or carbonization treatment in a gas atmosphere in which water vapor, carbon dioxide, oxygen, a mixed gas thereof, and these gases are diluted with an inert gas such as nitrogen. Is held at a temperature of about 800 to 1200 ° C. for about 5 to 120 minutes.
この場合、 炭素化処理又は賦活処理に供する活性炭前駆体は、 酸素原子を 5重 量%以上含むことが好ましい。 酸素原子が 5重量%以上含まれることにより、 炭 素化又は賦活反応において酸素原子が脱離する際に金属成分と相互作用が働き、 本発明の活性炭素繊維の最大の特徴であるマク口細孔の細孔直径に近い細孔直径 をもつメソ細孔を適度に穿孔させる効果が得られる。 酸素原子の含有量は、 不融 化温度、 不融化時間等の不融化条件で適宜調節することができる。 In this case, the activated carbon precursor to be subjected to the carbonization treatment or the activation treatment preferably contains 5% by weight or more of oxygen atoms. When the oxygen atoms are contained in an amount of 5% by weight or more, when the oxygen atoms are desorbed in the carbonization or activation reaction, the metal components interact with each other. The effect of appropriately perforating mesopores having a pore diameter close to the pore diameter of the pores is obtained. The content of oxygen atoms can be appropriately adjusted under infusibilizing conditions such as infusibilizing temperature and infusibilizing time.
本発明では、 特にトリハロメ夕ン類及び黴臭原因物質の吸着用に適した活性炭 素繊維をより確実に得るために、 このようにして得られた活性炭素繊維の窒素ガ ス吸着性能を測定することにより、 77. 4 Kにおける窒素吸着等温線において、 相対圧力 P/PQでの窒素ガス吸着量を V (P/Po) として、 In the present invention, in order to more reliably obtain an activated carbon fiber particularly suitable for adsorbing trihalomenes and a substance causing a moldy odor, the nitrogen gas of the activated carbon fiber thus obtained is used. In the nitrogen adsorption isotherm at 77.4 K, the nitrogen gas adsorption amount at relative pressure P / P Q is defined as V (P / Po)
(a) V (0.1) の値が 200 c c/g以上、 (a) V (0.1) is greater than 200 c c / g,
(b) V (0.1) /V (0.2) の値が 0. 92〜0. 99、 (b) The value of V (0.1) / V (0.2) is 0.92 to 0.99,
(c) V (0.2) /V (0.8) の値が 0. 80〜0. 95及び (c) V (0.2) / V (0.8) is 0.80 to 0.95 and
(d) V (0.8) /V (1.0) の値が 0. 80〜0. 90 (d) The value of V (0.8) / V (1.0) is 0.80 to 0.90
をすベて満たす活性炭素繊維を選出する工程を有することが望ましい。 窒素ガス 吸着量の測定方法は前記と同様にすれば良い。 It is desirable to have a step of selecting an activated carbon fiber that satisfies all conditions. The method for measuring the nitrogen gas adsorption amount may be the same as described above.
また、 本発明は、 トリハロメタン類及び黴臭原因物質の吸着用活性炭素繊維を 選出する方法も包含する。 すなわち、 トリ八ロメタン類及び黴臭原因物質の吸着 用活性炭素繊維を選出する方法であって、 The present invention also includes a method for selecting activated carbon fibers for adsorbing trihalomethanes and fungi-causing substances. That is, a method for selecting activated carbon fibers for adsorbing trioctanes and moldy odor causing substances,
活性炭素繊維の窒素ガス吸着量を測定することにより、 77. 4Kにおける窒 素吸着等温線において、 相対圧力 PZP。での窒素ガス吸着量を V (P/Po) と して、 By measuring the amount of nitrogen gas adsorbed on the activated carbon fiber, the relative pressure PZP was obtained in the nitrogen adsorption isotherm at 77.4K. Let the amount of nitrogen gas adsorbed at V be P (P / Po)
(a) V (0.1) の値が 200 c c/g以上、 (a) V (0.1) is greater than 200 c c / g,
(b) V (0.1) /V (0.2) の値が 0. 92〜0. 99、 (b) The value of V (0.1) / V (0.2) is 0.92 to 0.99,
(c) V (0.2) /V (0.8) の値が 0. 80〜0. 95及び (c) V (0.2) / V (0.8) is 0.80 to 0.95 and
(d) V (0.8) /V (1.0) の値が 0. 80〜0. 90 (d) The value of V (0.8) / V (1.0) is 0.80 to 0.90
をすベて満たす活性炭素繊維を選出することを特徴とする方法が本発明に包含さ れる。 この選出方法は、 上記のような製法以外の方法で製造された活性炭素繊維 を含め、 あらゆる活性炭素繊維に適用できる。 窒素ガス吸着量の測定方法は前記 と同様にすれば良い。 上記 (a) 〜 (b) の条件をすベて満たす活性炭素繊維は、 トリハロメ夕ン類及び黴臭原因物質の吸着用材料として優れた効果を発揮する。 トリハロメタン類の分子の大きさは、 黴臭原因物質のようにミク口細孔内に侵 入できない大きさではない。 そこで、 ミクロ細孔とメソ細孔とを兼ね備えた活性 炭素繊維に着目し、 詳細に検討した結果、 メソ細孔がミクロ細孔に近い小さい細 孔部分及びマク口細孔に近い大きい細孔部分が特定の範囲で占められるように、 その微細構造を窒素吸着等温泉 (窒素ガス吸着量) によりコントロールすること によって、 高いトリ八ロメタン類吸着性能を維持しつつ黴臭原因物質の吸着性能 をも改善することが可能となる。 The present invention encompasses a method characterized by selecting an activated carbon fiber that satisfies all conditions. This selection method can be applied to all activated carbon fibers, including activated carbon fibers produced by a method other than the above-mentioned production method. The method for measuring the nitrogen gas adsorption amount may be the same as described above. Activated carbon fibers satisfying all of the above conditions (a) and (b) exhibit an excellent effect as a material for adsorbing trihalomenes and fungal odor-causing substances. The size of the molecules of trihalomethanes is not so large that they cannot penetrate into the pores of Miku like the substances that cause moldy odor. Therefore, we focused on activated carbon fibers that have both micropores and mesopores, and as a result of a detailed study, found that the small pores where the mesopores were close to the micropores and the large pores where the mesopores were close to the Mactopores. By controlling the fine structure with a hot spring such as nitrogen adsorption (nitrogen gas adsorption amount) so that it is occupied in a specific range, the adsorption performance of mold odor-causing substances can be maintained while maintaining high trioctane methane adsorption performance. Can also be improved.
従って、 本発明活性炭素繊維は、 カルキ臭に代表される低分子物質からトリ八 ロメタン類、 さらに黴臭原因物質等の巨大分子までを実質的にすべて除去できる 吸着材として優れた効果を発揮することができる。 すなわち、 かかる特徴を有す る本発明活性炭素繊維は、 トリ八ロメ夕ン類及び黴臭原因物質の吸着用活性炭素 繊維として有用であり、 具体的には浄水精製用材料、 ガス精製用材料等として好 適に用いることができる。 Therefore, the activated carbon fiber of the present invention exerts an excellent effect as an adsorbent capable of removing virtually all of low molecular substances represented by a odor of lime, macromolecules such as trichloromethanes, and substances causing a moldy odor. be able to. That is, the activated carbon fiber of the present invention having such characteristics is useful as an activated carbon fiber for adsorbing trioctane compounds and fungi-causing substances, and specifically, a water purification material and a gas purification material. Etc. can be suitably used.
図面の簡単な説明 BRIEF DESCRIPTION OF THE FIGURES
図 1は、 実施例 1の鉄含有活性炭素繊維、 実施例 2の白金含有活性炭素繊維、 比較例 1の金属を含まない活性炭素繊維及び比較例 3の鉄含有活性炭素繊維の窒 素吸着等温線を示す図である。 Figure 1 shows the nitrogen adsorption isotherms of the iron-containing activated carbon fiber of Example 1, the platinum-containing activated carbon fiber of Example 2, the metal-free activated carbon fiber of Comparative Example 1, and the iron-containing activated carbon fiber of Comparative Example 3. It is a figure showing a line.
発明を実施するための最良の形態 BEST MODE FOR CARRYING OUT THE INVENTION
以下、 実施例及び比較例を示し、 本発明の特徴とするところをよりいっそう明 確に示す。 ただし、 本発明は、 これら実施例に限定されるものではない。 Hereinafter, Examples and Comparative Examples will be shown, and the features of the present invention will be shown more clearly. However, the present invention is not limited to these examples.
なお、 本実施例では、 活性炭素繊維の窒素ガス吸着量は、 商品名 「AUT O S O R B— 6」 (QUAN T C H R OME製) を用いて測定した。 In this example, the amount of nitrogen gas adsorbed on the activated carbon fiber was measured using "AUTOSORB-6" (trade name, manufactured by QUANTCHROME).
実施例 1 Example 1
'水分及びキノリン不溶分を除去したコールタール 1 0 0 0 gを窒素雰囲気下 9 0 °Cに加温し、 そこにァセチルァセトナト鉄 6 gを溶解したキノリン混合液 2 0 O m lを徐々に滴下し、 9 0分間攪拌した。 次に、 これを減圧蒸留し、 さらに 3 LZ分の割合で空気を吹き込みながら 3 3 0 °Cで 3時間反応することにより、 鉄 含有コ一ルタ一ルビッチを得た。 このピッチの鉄含有量は 0 . 2 3重量%であつ た。 得られた鉄含有コールタールピッチを溶融温度 3 2 0 °Cで溶融押出紡糸して ピッチ繊維を得た。 紡糸されたピッチ繊維を空気中で常温から昇温速度 1〜1 0 でで加熱し、 最高温度 3 6 4°Cで 4分保持し、 全不融化時間 6 5分をかけて不融 化処理を行った。 次いで、 不融化したピッチ繊維を窒素雰囲気下 8 5 0 °Cで 6 0 分間飽和水蒸気に暴露し、 賦活処理を行い、 鉄含有活性炭素繊維を得た。 得られ た活性炭素繊維の a〜d値を表 1に示す。 また、 その窒素吸着等温線を図 1に示 す。 実施例 2 '100 g of coal tar from which water and quinoline-insoluble matter were removed was heated to 90 ° C under a nitrogen atmosphere, and 20 O ml of a quinoline mixed solution in which 6 g of acetylacetonatoiron was dissolved was added thereto. The mixture was gradually added dropwise and stirred for 90 minutes. Next, this was distilled under reduced pressure, and further reacted at 330 ° C. for 3 hours while blowing air at a rate of 3 LZ to obtain an iron-containing copper rubicite. The iron content of this pitch was 0.23% by weight. The obtained iron-containing coal tar pitch was melt-extruded and spun at a melting temperature of 320 ° C to obtain pitch fibers. The spun pitch fibers are heated in the air from room temperature at a heating rate of 1 to 10 and held at the maximum temperature of 364 ° C for 4 minutes, and the infusibilizing treatment is performed over a total infusibilizing time of 65 minutes. Was done. Next, the infusibilized pitch fiber was exposed to saturated steam at 850 ° C. for 60 minutes in a nitrogen atmosphere to perform an activation treatment to obtain an iron-containing activated carbon fiber. Table 1 shows a to d values of the obtained activated carbon fibers. Figure 1 shows the nitrogen adsorption isotherm. Example 2
ァセチルァセトナト鉄 6 gの代わりにァセチルァセトナト白金 5 . 7 gを使用 した以外は実施例 1と同様の方法でコールタールピッチを得た。 このピッチの白 金含有量は 2 . 6 0重量%であった。 紡糸されたピッチ繊維を空気中で常温から 昇温速度 2 °C/分で加熱し、 3 7 5 で 1 5分間保持し、 不融化処理を行った。 次いで、 不融化したピッチ繊維を窒素雰囲気下 8 5 0 で 3 5分間飽和水蒸気に 暴露し、 賦活処理を行い、 白金含有活性炭素繊維を作製した。 得られた活性炭素 繊維の a〜d値を表 1に示す。 また、 その窒素吸着等温線を図 1に示す。 A coal tar pitch was obtained in the same manner as in Example 1, except that 5.7 g of acetyl acetonato platinum was used instead of 6 g of acetyl acetonato iron. The platinum content of this pitch was 2.60% by weight. The spun pitch fibers were heated from room temperature in the air at a rate of temperature increase of 2 ° C / min, and kept at 375 for 15 minutes for infusibility treatment. Next, the infusibilized pitch fiber was exposed to saturated steam at 850 for 35 minutes in a nitrogen atmosphere to perform an activation treatment to produce a platinum-containing activated carbon fiber. Table 1 shows a to d values of the obtained activated carbon fibers. Figure 1 shows the nitrogen adsorption isotherm.
比較例 1 Comparative Example 1
金属化合物を混合しないこと及び賦活処理時間を 3 0分にした以外は実施例 1 と同様の方法で活性炭素繊維を製造した。 得られた活性炭素繊維の a〜d値を表 1に示す。 また、 その窒素吸着等温線を図 1に示す。 Activated carbon fibers were produced in the same manner as in Example 1, except that no metal compound was mixed and the activation treatment time was 30 minutes. Table 1 shows a to d values of the obtained activated carbon fibers. Figure 1 shows the nitrogen adsorption isotherm.
比較例 2 Comparative Example 2
ァセチルァセトナト鉄の量を 1 8 0 gに変更した以外は実施例 1と同様の方法 で鉄含有活性炭素繊維の作製を試みた。 この時のピッチの鉄含有量は 7重量%で あった。 しかし、 紡糸の際に糸切れが多発し、 操業上問題があり、 作製した鉄含 有活性炭素繊維は繊維形状が容易に崩壊し粉化した。 また、 鉄化合物の凝集物と 認められるものが多数存在した。 活性炭素繊維の粉化が著しく、 a〜d値の測定 は困難であった。 Production of iron-containing activated carbon fiber was attempted in the same manner as in Example 1, except that the amount of acetyl acetonato iron was changed to 180 g. At this time, the iron content of the pitch was 7% by weight. However, yarn breakage occurred frequently during spinning, and there was a problem in operation. The produced iron-containing activated carbon fiber easily collapsed into a powder form and powdered. In addition, there were many that were recognized as aggregates of iron compounds. Activated carbon fibers were remarkably powdered, and it was difficult to measure ad values.
比較例 3 Comparative Example 3
不融化処理における最高温度を 2 6 4 t:にした以外は実施例 1と同様の方法で 鉄含有活性炭素繊維を作製した。 なお、 この時の活性炭前駆体中の酸素原子含有 量は 2 . 5 5 %であった。 得られた活性炭素繊維の a〜d値を表 1に示す。 また、 その窒素吸着等温線を図 1に示す。 吸镥畳 吸蓊Activated iron-containing carbon fibers were produced in the same manner as in Example 1 except that the maximum temperature in the infusibilization treatment was changed to 26.4 t :. At this time, the oxygen atom content in the activated carbon precursor was 2.55%. Table 1 shows a to d values of the obtained activated carbon fibers. Figure 1 shows the nitrogen adsorption isotherm. Tatami mat
V(0.1) V(0.1)/V(0.2) V(0.2)/V(0.8) V(0.8)/V(1.0) 実施例 1 342 0.95 0.92 0.85 V (0.1) V (0.1) / V (0.2) V (0.2) / V (0.8) V (0.8) / V (1.0) Example 1 342 0.95 0.92 0.85
実施例 2 246 0.96 0.82 0.88 Example 2 246 0.96 0.82 0.88
比較例 1 328 0.97 0.97 0.99 Comparative Example 1 328 0.97 0.97 0.99
比較例 2 実施不可 実施不可 実施不可 実施不可 Comparative Example 2 Impossible Impossible Impossible Impossible Impossible
比較例 3 156 0.94 0.89 0.98 試験例 1 Comparative Example 3 156 0.94 0.89 0.98 Test Example 1
各実施例及び比較例で得られた活性炭素繊維について、 総トリハロメタンろ過 能力試験及びカビ臭ろ過能力試験を行った。 その結果を表 2に示す。 なお、 各試 験方法は以下の方法により実施した。 For the activated carbon fibers obtained in each of the examples and comparative examples, a total trihalomethane filtration ability test and a mold odor filtration ability test were performed. The results are shown in Table 2. Each test method was performed by the following method.
(1) 総トリハロメタンろ過能力試験 (1) Total trihalomethane filtration capacity test
J I S-S- 3201 『家庭用浄水器試験方法 (連続法) 』 に基づいてミルド 化した試料 8. 4 gをアクリル容器に 48mm (直径) · 30mm (高さ) とな るように充填して、 総トリハロメタン TTHM (CHC 13 : CHC 12B r : C HC 1 B r 2 : CHB r 3=45 : 30 : 20 : 5) の濃度が 102. 4 p p tの原 水を流量 3 LZ分で通水した。 このときの出口濃度 Cと初期濃度 C。の比 C/C 。が 0. 2となる通水量をろ過能力とした。 なお、 上記分析装置は、 商品名 『GC 一 14B』 (島津製作所製) を使用し、 ヘッドスペース法で実施した。 8.4 g of a milled sample based on JI SS-3201 “Test method for household water purifiers (continuous method)” was filled into an acrylic container so as to be 48 mm (diameter) · 30 mm (height). trihalomethane TTHM (CHC 13: CHC 1 2 B r: C HC 1 B r 2: CHB r 3 = 45: 30: 20: 5) passing water concentration raw water 102. 4 ppt at a flow rate 3 LZ worth of did. Outlet concentration C and initial concentration C at this time. The ratio of C / C. Is 0.2, which is defined as the filtration capacity. The above analyzer was run under the headspace method using the trade name “GC-I 14B” (manufactured by Shimadzu Corporation).
(2) カビ臭ろ過能力試験 (2) Mold smell filtration capacity test
J I S-S- 3 20 1 『家庭用浄水器試験方法 (連続法) 』 に基づいてミルド 化した試料 8. 4 gをアクリル容器に 48mm (直径) · 30mm (高さ) とな るように充填して、 2—メチルイソボルネオール濃度が 5.5 pp tの原水を流量 3 L/分で通水した。 このときの出口濃度 Cと初期濃度 C。の比 CZCQが 0. 2 となる通水量をろ過能力とした。 なお、 上記分析装置は、 商品名 『GCMS— Q P 5050』 (島津製作所製) を使用し、 パージトラップ法で実施した。 表 2 JI SS-320 1 Acrylic container was filled with 8.4 g of a milled sample based on the “Test method for household water purifiers (continuous method)” so as to be 48 mm (diameter) · 30 mm (height). Then, raw water having a 2-methylisoborneol concentration of 5.5 ppt was passed at a flow rate of 3 L / min. Outlet concentration C and initial concentration C at this time. The flow rate at which the ratio CZCQ became 0.2 was defined as the filtration capacity. The above analyzer was performed by the purge trap method using the trade name “GCMS-QP 5050” (manufactured by Shimadzu Corporation). Table 2
これらの結果からも明らかなように、 本発明の活性炭素繊維は、 トリ八口メタ ン類の吸着除去性能はもとより、 黴臭原因物質の吸着除去性能においても優れた 効果を発揮できることがわかる。 なお、 比較例 2は、 粉ィ匕が著しいため、 ろ過能 力試験の実施は困難であった。 As is clear from these results, the activated carbon fiber of the present invention can exert excellent effects not only on the adsorption and removal performance of trioctane methanes but also on the adsorption and removal performance of the fungi-causing substance. In Comparative Example 2, it was difficult to carry out a filtration ability test due to the remarkable powdering.
Claims
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| WO2020218370A1 (en) * | 2019-04-26 | 2020-10-29 | 株式会社クラレ | Carbonaceous material, method for producing same, filter for water purification and water purifier |
| US20210261441A1 (en) * | 2018-06-19 | 2021-08-26 | Ad'all Co., Ltd. | Activated carbon |
| EP3812349A4 (en) * | 2018-06-19 | 2022-02-09 | Ad'All Co., Ltd. | Activated carbon |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH03265510A (en) * | 1990-03-13 | 1991-11-26 | Osaka Gas Co Ltd | Production of metal-contg. activated carbon |
| JPH10328563A (en) * | 1997-05-30 | 1998-12-15 | Adall:Kk | Base material for removing noxious gas and its production |
| JPH11240707A (en) * | 1998-02-27 | 1999-09-07 | Adooru:Kk | Activated carbon |
| JPH11240708A (en) * | 1998-02-27 | 1999-09-07 | Adooru:Kk | Fibrous activated carbon |
-
2002
- 2002-09-26 WO PCT/JP2002/009919 patent/WO2003026792A1/en not_active Ceased
- 2002-09-26 JP JP2003530419A patent/JPWO2003026792A1/en active Pending
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH03265510A (en) * | 1990-03-13 | 1991-11-26 | Osaka Gas Co Ltd | Production of metal-contg. activated carbon |
| JPH10328563A (en) * | 1997-05-30 | 1998-12-15 | Adall:Kk | Base material for removing noxious gas and its production |
| JPH11240707A (en) * | 1998-02-27 | 1999-09-07 | Adooru:Kk | Activated carbon |
| JPH11240708A (en) * | 1998-02-27 | 1999-09-07 | Adooru:Kk | Fibrous activated carbon |
Cited By (8)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US20210261441A1 (en) * | 2018-06-19 | 2021-08-26 | Ad'all Co., Ltd. | Activated carbon |
| EP3812349A4 (en) * | 2018-06-19 | 2022-02-09 | Ad'All Co., Ltd. | Activated carbon |
| EP3812348A4 (en) * | 2018-06-19 | 2022-02-09 | Ad'All Co., Ltd. | ACTIVATED CHARCOAL |
| US11873235B2 (en) | 2018-06-19 | 2024-01-16 | Ad'all Co., Ltd. | Activated carbon |
| US12258284B2 (en) | 2018-06-19 | 2025-03-25 | Ad'all Co., Ltd. | Activated carbon |
| WO2020218370A1 (en) * | 2019-04-26 | 2020-10-29 | 株式会社クラレ | Carbonaceous material, method for producing same, filter for water purification and water purifier |
| JP6829796B1 (en) * | 2019-04-26 | 2021-02-10 | 株式会社クラレ | Carbonaceous materials and their manufacturing methods, as well as water purification filters and water purifiers |
| US12258276B2 (en) | 2019-04-26 | 2025-03-25 | Kuraray Co., Ltd. | Carbonaceous material, method for producing same, filter for water purification and water purifier |
Also Published As
| Publication number | Publication date |
|---|---|
| JPWO2003026792A1 (en) | 2005-01-06 |
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