TW419390B - Cleaning apparatus, filter and method of manufacturing the same - Google Patents
Cleaning apparatus, filter and method of manufacturing the same Download PDFInfo
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經濟部中央標準局員工消f合作社印製 · 41939Q_^ _ 五、發明説明() 【發明所屬技術領域】 本發明係關於適合用於製造例如半導體元件(LSI ) 或液晶顯示器(LCD )之無塵室或無麈操作台等之具有空 氣環境之調濕功能和空氣環境中之氣體有機雜質、粒狀雜 質之除去功能之潔淨裝置,還有關於在那樣的潔淨裝置使 .用之用以除去環境中之氣體有機雜質之過濾器及其製造方 法。 [習知技術] 今日在LSI或LCD之製造廣用無麈室等潔淨裝置。例 如由空白晶片(矽晶片)到製造1MDRAM晶元爲止之半 導體生產線包含約200個製程,又由玻璃原材料(LCD基 板)到製造9.4吋TFT爲止之LCD面板生產線包含約80 個製程。在這些生產線,使晶片或LCD基板在各製程一直 連續地流動是困難的。例如在TFT-LCD之生產線,在前段 製程已形成了全部的電路的半成品基板,到移到後段製程 爲止之數小時〜數十小時之期間,被迫在晶舟(Carrier ) 或保管庫(Stocker )之中在曝露在潔淨環境下等待。 像這樣將晶片或LCD基板長時間放置在一般之潔淨 裝置環境中時,在那些基板之表面就附著來自潔淨環境之 有機物。而且,例如在晶片附著了有機物之情況,發生如 下之不良。即,在附著了有機物之狀態,在晶片表面形成 絕緣氧化膜(Si02 )時,由於在絕緣氧化膜中取入有機物 中之炭元素成分,發生了絕緣氧化膜之絕緣耐壓大幅度降 低、漏電流也大幅度增大之問題。又,由於晶片表面吸附 2 本紙張八度適用中1¾¾家炸準()八4叱格(21〇/297公楚) <請先閱讀背面之注意事項再填寫本頁)Printed by the staff of the Central Bureau of Standards of the Ministry of Economic Affairs and Cooperatives · 41939Q_ ^ _ V. Description of the Invention (Technical Field of the Invention) The present invention relates to a dust-free environment suitable for manufacturing, for example, a semiconductor element (LSI) or a liquid crystal display (LCD). A clean device with an air environment humidity control function and a gas organic impurity and granular impurity removal function in a room or an airless operation table, etc., and a clean device for use in such a clean device Filter for gaseous organic impurities and its manufacturing method. [Knowledge technology] Today, LSI or LCD are widely used in clean rooms, such as clean rooms. For example, a semiconductor production line from blank wafers (silicon wafers) to manufacturing 1MDRAM wafers contains about 200 processes, and LCD panel production lines from glass raw materials (LCD substrates) to manufacturing 9.4-inch TFTs contain about 80 processes. In these production lines, it is difficult to continuously flow a wafer or an LCD substrate in each process. For example, in the TFT-LCD production line, the semi-finished substrate that has formed all the circuits in the previous stage is forced to be in the Carrier or Stocker during the hours to tens of hours before moving to the later stage. ) Waiting for exposure in a clean environment. When a wafer or an LCD substrate is left in a general clean device environment for a long time like this, organic substances from the clean environment adhere to the surfaces of those substrates. In addition, for example, when an organic substance is adhered to the wafer, the following problems occur. That is, when an insulating oxide film (Si02) is formed on the surface of the wafer in the state where organic substances are adhered, the carbon element component of the organic substance is taken into the insulating oxide film, and the insulation withstand voltage of the insulating oxide film is greatly reduced and leakage occurs. There is also a problem that the current is greatly increased. In addition, because the surface of the wafer is adsorbed, 2 paper octaves are suitable for use. 1¾¾Family (8) 4 叱 (21〇 / 297 cm) < Please read the precautions on the back before filling this page)
4 )9390 A7 B? 五、發明説明( 經濟部中央標準局晨工消费合作社印列4 有機物,光阻膜之密接性惡化,發生曝光、蝕刻不良,可 能無法形成正確的電路圖形。此外,在表面形成了絕緣膜 之晶片之表面電阻係數上升,晶片變成易帶靜電,在空氣 中浮遊之微粒子更易被晶片表面靜電吸附,更易發生絕緣 破壞。又,對潔淨裝置環境中所含的有機雜質照射光學機 器之紫外線時,在其潔淨裝置中發生光CVD反應,其產生 物附著在曝光裝置等之光學系統之透鏡或反射鏡等之表面 而發生朦朧》光學效率降低° 又,在來自環境之有機物附著在係LCD基板之玻璃基 板之狀態,在其表面上將薄膜電晶體(TFT )用之非晶型 矽(a-Si )成膜時,發生LCD基板和a-Si膜密接不良。像 這樣,來自潔淨環境之有機物對LSI或LCD之製造有不良 的影響。 而,利用例如紫外線/臭氧洗淨等洗淨技術也可除去附 著在基板表面之有機物。可是,平均一片基板之洗淨時間 需要數分鐘,常洗淨導致生產力降低。於是,尤其最近, 不僅金屬雜質或微粒子引起之基板污染,連存在於潔淨® 境中之有機雜質對半導體製造之影響都受到重視。例如’ 在美國之SEMATECH於1995年5月31日發表之 Technology Transfer #95052812 A-TR「Forecast of Airborne Molecular Contamination Limits for the 0.25 Micron High Performance Logic Process」,刊載如表1所不之晶片表面 之有機物污染控制位準(表面污染之容許値)°依據該記 載,到1998年在前段製程需要控制5xl013炭元素原子個數 (請先閱讀背面之注意事項再填寫本頁)4) 9390 A7 B? 5. Description of the invention (printed by Chengong Consumer Cooperative, Central Standards Bureau, Ministry of Economic Affairs, 4 Organic matter, the adhesion of the photoresist film is deteriorated, and exposure and etching failures may occur. In addition, correct circuit patterns may not be formed. The surface resistivity of the wafer on which an insulating film is formed increases, and the wafer becomes susceptible to static electricity. Particles floating in the air are more likely to be electrostatically adsorbed on the surface of the wafer and more likely to cause insulation damage. In addition, it is exposed to organic impurities contained in the clean device environment In the case of ultraviolet rays of optical equipment, a photo CVD reaction occurs in its clean device, and its products adhere to the surface of the lens or reflector of an optical system such as an exposure device, resulting in haziness. The optical efficiency is reduced. In the state of being attached to the glass substrate of the LCD substrate, when the amorphous silicon (a-Si) for a thin film transistor (TFT) is formed on the surface, a poor adhesion between the LCD substrate and the a-Si film occurs. Organic substances from a clean environment have an adverse effect on the manufacture of LSI or LCD. However, using cleaning techniques such as UV / ozone cleaning It can also remove organic matter attached to the surface of the substrate. However, the average cleaning time of a substrate takes several minutes, and frequent cleaning leads to reduced productivity. Therefore, especially recently, not only substrate contamination caused by metal impurities or particles, but also cleanliness® The impact of organic impurities in the environment on semiconductor manufacturing is valued. For example, 'Technology Transfer # 95052812 A-TR', "Forecast of Airborne Molecular Contamination Limits for the 0.25 Micron High Performance Logic" published by SEMATECH in the United States on May 31, 1995 Process ”, published in Table 1 on the wafer surface organic matter pollution control level (permissible surface pollution) ° According to this record, in the previous stage of the process in 1998 need to control the number of 5xl013 carbon element atoms (please read the back (Please fill in this page again)
本紙張尺度適珂中阂1¾家谍準(C._NS ) Λ4現格(2W公犛) 經濟部中央標隼局貝工消費合作社印裝 V 419390 二7 ___;_ _ D / 五、發明説明() /cm2,在後段製程需要控制lxl0i5炭元素原子個數/cm2。 表1 要求水準(年) 1995 1998 2001 2004 2007 2010 設計尺寸μηι 0.35 0.25 0.18 0.13 0.1 0.07 前段製程有機物 1E14 5E13 3E13 1E13 5E12 3E12 (atoms of C/cm2 ) 後段製程有機物 1E15 1E15 1E15 <1E15 <1E15 <1E15 (atoms of C/cm2) 因此,從以前在用以除去潔淨環境中所含氣體有機雜 質之裝置上就使用利用活性炭吸附並除去氣體有機雜質之 化學式過濾器。而,在使用活性炭之化學式過濾器之最簡 單的型式上,將粒狀活性炭塞入指定盒子等而成之充塡塔 廣爲人知。又,在其他型式上,將纖維狀活性炭和低融點 聚酯或聚酯不織布之黏接劑複合後製成毛氈狀之化學式過 濾器或者用黏接劑將粒狀活性炭牢固地黏在氨基甲酸酯泡 沫塑料或不織布製成塊狀及薄片形之化學式過濾器也廣爲 人知。 例如,對天花板面成爲潔淨空氣之吹出面之無麈室之 情況而言,在裝在天花板之除去粒子之過濾器之上游側配 置化學式過濾器係用以除去無塵室之空氣環境中之氣體有 機雜質之極有效之裝置。可是,活性炭係日本之消防法上 指定的可燃物,需要嚴格地注意火。因而,由防災上之觀 點,在天花板難配置使用了活性炭之化學式過濾器。 又,用於LSI或LCD之製造之潔淨裝置,一般保持在 4 /L (請先間讀背面之注意事項再填寫本頁)The size of this paper is 阂 1¾ the home spy standard (C._NS) Λ4 is present (2W public). The Central Standards Bureau of the Ministry of Economic Affairs is printed by the Shellfish Consumer Cooperative. V 419390 2 7 ___; _ _ D / V. Description () / Cm2, the number of carbon element atoms / cm2 in lxl0i5 carbon element needs to be controlled in the later process. Table 1 Requirement Level (Year) 1995 1998 2001 2004 2007 2010 Design size μηι 0.35 0.25 0.18 0.13 0.1 0.07 Organics in the former process 1E14 5E13 3E13 1E13 5E12 3E12 (atoms of C / cm2) Organics in the later process 1E15 1E15 1E15 < 1E15 < 1E15 < 1E15 (atoms of C / cm2) Therefore, a chemical filter that adsorbs and removes gaseous organic impurities with activated carbon has been used in a device for removing gaseous organic impurities contained in a clean environment. In the simplest form of a chemical filter using activated carbon, a filling tower formed by plugging granular activated carbon into a designated box or the like is widely known. In other types, a fibrous activated carbon is compounded with a low-melting point polyester or polyester non-woven adhesive to form a felt-like chemical filter or the granular activated carbon is firmly adhered to the carbamate with an adhesive Ester foam or non-woven chemical filters in block and sheet form are also widely known. For example, in the case of a clean room where the ceiling surface becomes the blowing surface of clean air, a chemical filter is arranged on the upstream side of the particle removal filter installed on the ceiling to remove the gas in the air environment of the clean room An extremely effective device for organic impurities. However, activated carbon is a flammable material specified in the Japanese Fire Fighting Law and requires careful attention to fire. Therefore, from the viewpoint of disaster prevention, it is difficult to arrange a chemical filter using activated carbon on the ceiling. In addition, the cleaning equipment used in the manufacture of LSI or LCD is generally maintained at 4 / L (please read the precautions on the back before filling this page)
本纸疚尺度適用中闻囚家榡卒i CNS ) Λ4現格(2丨》/_297公趦) A7 B7 4193 9 0 五、發明説明() 溫度23〜25 °C、相對濕度(45±1〇 ) %之環境。可是,因 .活性炭係弱疏水性’不僅氣體有機雜質,連空氣中之水分 都吸附很多。而且,活性炭只要相對濕度稍微增加,空氣 中之水分吸附量也急速增加。例如,先將幾乎未吸附水分 之未使用之活性炭保管在內部係乾燥環境之容器,然後將 該活性炭馬上曝露在溫度23〜25 °C、相對濕度50%之無麈 室環境時’活性炭就大量地吸附空氣中之水分,直到吸附 飽和爲止。因而,在往潔淨裝置之供氣側安裝了添加活性 炭之化學式過濾器時’在化學式過濾器之上游側調節濕 度,也因化學式過濾器所使用之活性炭大量吸附空氣中之 水分,潔淨裝置內之相對濕度變成低於指定値。濕度降低 使得易發生靜電,在LSI或LCD之製造上引起問題。爲了 解決此問題,添加了活性炭之化學式過濾器之製造業者有 必要進行麻煩的作業,即在出貨前調查使用處之環境溫濕 度並特意使化學式過濾器之活性炭吸附和該溫濕度平衡之 水分後密封包裝才出貨。 而,充塡塔型式之習知之化學式過濾器,有機物之吸 附效率高,但是有壓力損失(通氣阻力)大之缺點。而’ 毛氈狀或薄片形化學式過濾器在通氣性上優異’吸附效率 高也和充塡塔差不多,但是因自過濾件(例如不織布)或 使活性炭附著在薄片之黏接劑(例如氯丁橡膠系樹脂、氨 基甲_乙脂系樹脂、環氧系樹脂、较系樹脂等)或用以將 過濾件固接在周圍之框之密封劑(例如氯丁橡膠、砂橡膠 等)等發生之氣體有機雜質會被含在通過化學式過濾器後 5 本紙法尺度適)丨家標卒(C.NS ) Λ4^格(2i0.< 公犮) (錆先閱讀背面之注意事項再填寫本頁) 丁 -3 經濟部中央標隼局工消费合作杜印製 經濟部中央標準局貝τ;消费合作社印製 419390 五、發明説明() 之空氣中,可能對半導體製造有不良的影響。此外,這® 毛氈狀或薄片形化學式過濾器,邊一度除去無麈室瓌境中 所含ppb等級之極微量有機雜質,邊再使化學式過濾器# 身所發生之氣體有機雜質混入通過之空氣中。 又,在設於吸附層之下游側之除去粒狀雜質之過濾 器,因以前在構成元件上就含有發生氣體有機雜質之材 料,也有除去粒狀雜質之過濾器本身會發生之氣體有機β 質之不良。 在可轉用爲用以防止這種基板表面污染之化學式過濾 器之過濾器上,在特開昭61-103518號公報或特開平3-98611號公報上有公開。前著係爲了除去惡臭而開發,係 使由氨基甲酸酯泡沬塑料構成之基板浸入包含粉末活和乳 濁液型黏接劑及固態酸之水溶液後乾燥而成之過濾器,但 是乳濁液型黏接劑之合成橡膠乳液或其他的水分散系有機 黏接劑及係基材之氨基甲酸酯泡沬塑料本身也發生氣體有 機物之脫離。而,後者係爲了除去對健康有害之有害氣體 或惡臭而開發,其必要條件是在吸附劑倂用有機黏結劑, 但是該有機黏結劑含有聚乙烯等有機物,無法避免來自過 濾器本身之氣體有機物之脫離。 在其他和這種過濾器相關之特開昭63-310636號(專 利第2579767號)及在國公開之W091/169W號(日本專 利第2579767號)公報上,公開了使用水玻璃或無機黏結 劑使沸石等吸附劑載持在具有小貫通孔之蜂巢構造物之表 面之過濾器。 6 (锖先閱讀背命之注意事項再填寫本頁)The scale of this paper is applicable to the prisoner's family members in CNW i CNS) Λ4 is present (2 丨 "/ _297 Gong) A7 B7 4193 9 0 V. Description of the invention () Temperature 23 ~ 25 ° C, relative humidity (45 ± 1 〇)% of the environment. However, because activated carbon is weakly hydrophobic ', not only gaseous organic impurities but also moisture in the air are adsorbed a lot. Moreover, as long as the relative humidity of activated carbon increases slightly, the amount of moisture adsorbed in the air also increases rapidly. For example, first store unused activated carbon that has almost no moisture absorption in a container in an internal dry environment, and then immediately expose the activated carbon to a chamberless environment at a temperature of 23 to 25 ° C and a relative humidity of 50%. Ground adsorbs moisture in the air until the adsorption is saturated. Therefore, when a chemical filter added with activated carbon is installed on the air supply side of the clean device, the humidity is adjusted on the upstream side of the chemical filter, and the active carbon used in the chemical filter absorbs a large amount of moisture in the air. The relative humidity becomes lower than the specified value. The reduced humidity makes static electricity more prone to cause problems in the manufacture of LSI or LCD. In order to solve this problem, manufacturers of chemical filters with activated carbon need to perform troublesome work, that is, investigate the temperature and humidity of the environment before use and deliberately adsorb the activated carbon of the chemical filter and the moisture of the temperature and humidity balance. Shipped in a sealed package. However, the conventional chemical filter with a filling tower type has a high adsorption efficiency of organic matter, but has the disadvantage of large pressure loss (ventilation resistance). The 'felt-shaped or sheet-shaped chemical filter is excellent in air permeability' and its high adsorption efficiency is similar to that of the filling tower, but it is due to self-filtering elements (such as non-woven fabrics) or adhesives that attach activated carbon to the sheets (such as neoprene). Gases such as resins, carbamate-ethyl resins, epoxy resins, resins, etc.) or sealants (such as neoprene, sand rubber, etc.) used to secure the filter to the surrounding frame Organic impurities will be contained in 5 paper sizes after passing through the chemical filter. 丨 Family standard (C.NS) Λ4 ^ grid (2i0. ≪ public note) (锖 Please read the precautions on the back before filling this page) Ding-3 Industrial-consumer cooperation of the Central Standards Bureau of the Ministry of Economic Affairs Du printed by the Central Standards Bureau of the Ministry of Economic Affairs; printed by the Consumer Cooperative 419390 5. In the air of the invention description (), it may have adverse effects on semiconductor manufacturing. In addition, this ® felt-shaped or sheet-shaped chemical filter removes the trace ppb organic impurities contained in the chamber-free environment at one time, and then mixes the organic impurities of gases generated in the chemical filter # body into the air passing through in. In addition, the filter for removing particulate impurities on the downstream side of the adsorption layer has previously contained materials that generate gaseous organic impurities on the constituent elements, and there are also gaseous organic β substances that can occur in the filter itself that removes particulate impurities. Bad. A filter that can be used as a chemical filter to prevent surface contamination of such a substrate is disclosed in Japanese Patent Application Laid-Open No. 61-103518 or Japanese Patent Application Laid-Open No. 3-98611. The former was developed to remove bad odors. It is a filter made by immersing a substrate made of urethane foam plastic in an aqueous solution containing powder and emulsion type adhesives and solid acid, but it is opaque. Liquid type adhesives such as synthetic rubber emulsions or other water-dispersed organic adhesives and urethane foams of the base material also have gas organic compounds detached. However, the latter was developed to remove harmful gases or malodors that are harmful to health. The necessary condition is that an organic binder is used in the adsorbent. However, the organic binder contains organic substances such as polyethylene, and it is impossible to avoid gaseous organic substances from the filter itself Of it. In other publications related to this filter, JP-A-63-310636 (Patent No. 2579767) and National Publication No. W091 / 169W (Japanese Patent No. 2579767) disclose the use of water glass or inorganic binders. A filter in which an adsorbent such as zeolite is supported on the surface of a honeycomb structure having small through holes. 6 (Please read the precautionary note before filling out this page)
度適m中闽阄$:標卑;(τμΓ) μ规格厂1^297公^ - 經濟部中夾標準局員工消費合作社印製 419390 五、發明説明() 本發明之目的在於提供一種過濾器,在防災上優異且 濕度不會降低,還有無來自過濾器本身之氣體有機雜質之 脫離,而且除去所處理對象空氣中所含微量的氣體有機雜 質,可防止該有機物引起基板等之表面污染。本發明還提 供這種過濾器之製造方法和潔淨裝置。 【發明之綜合說明】 首先,本發明係關於具有使已調節濕度之空氣循環之 機構之潔淨裝置,其特徵在於在該空氣之循環路徑設置具 有疏水性沸石之通氣性過濾器和配置在該過濾器之下游側 之除去粒子狀雜質之除去粒子之過濾器。若利用該潔淨裝 置,可在不降低濕度下除去在潔淨裝置內循環之空氣中之 氣體有機雜質。該潔淨裝置,因未使用係可燃物之活性炭, 在防災上優異,該過濾器和除去粒子之過濾器可配置在潔 淨裝置之天花板部。此外,爲了更提高防災性,該過濾器 最好只用不含可燃物之材料構成。又,該過濾器最好只用 不產生氣體有機雜質之材料構成。 此外,在該過濾器之理想的構造上提供以使疏水性沸 石固接在蜂巢構造物之表面的。此時,該固接可利用使蜂 巢構造物浸入令疏水性沸石之粉末分散之懸濁液後將該蜂 I巢構造物乾燥之方法、利用黏接劑固接之方法等。又_,該 蜂巢構造物以無機纖維爲必要成分,在其他的成分上最好 爲含有黏土礦物或矽酸鈣之其中之一之不可燃構造物°此 外,該疏水性沸石之有效細孔徑最好係7埃以上。又,該 7 本紙張尺度適州中阀阀家彳ΐ•毕(A4At格门〗公趙) (請先閱讀背面之注意事項乔填寫本頁) •1^^·The degree is appropriate. Min: $; standard humble; (τμΓ) μ size factory 1 ^ 297g ^-Printed by the Consumer Cooperative of the Zhongjia Standard Bureau of the Ministry of Economic Affairs 419390 V. Description of the invention It is excellent in disaster prevention and the humidity will not decrease, and there is no detachment of gaseous organic impurities from the filter itself, and the removal of trace gaseous organic impurities in the air to be treated can prevent the organic substances from causing surface pollution of substrates and the like. The invention also provides a method for manufacturing such a filter and a cleaning device. [Comprehensive description of the invention] First, the present invention relates to a cleaning device having a mechanism that circulates air that has been adjusted for humidity, and is characterized in that an air-permeable filter having a hydrophobic zeolite is provided in the air circulation path and the filter is disposed Filter for removing particulate matter on the downstream side of the filter. If the cleaning device is used, gaseous organic impurities in the air circulating in the cleaning device can be removed without reducing the humidity. This cleaning device is excellent in disaster prevention because it does not use flammable activated carbon. The filter and the filter for removing particles can be placed on the ceiling of the cleaning device. In addition, in order to further improve the disaster prevention performance, it is preferable that the filter be made only of a material containing no combustible materials. In addition, it is preferable that the filter is made of only a material which does not generate gaseous organic impurities. In addition, the filter is desirably provided so that hydrophobic zeolite is fixed to the surface of the honeycomb structure. In this case, the method of fixing the honeycomb structure by immersing the honeycomb structure in a suspension in which the powder of the hydrophobic zeolite is dispersed and drying the honeycomb structure, and the method of fixing with an adhesive can be used. In addition, the honeycomb structure contains inorganic fiber as an essential component, and the other components are preferably incombustible structures containing one of clay mineral or calcium silicate. In addition, the effective pore diameter of the hydrophobic zeolite is the most Okay more than 7 Angstroms. In addition, the 7 paper sizes of Shizhou Middle Valve and Valve Jiajia • Bi (A4At Grid Men〗 赵) (Please read the notes on the back first and fill in this page) • 1 ^^ ·
,?T 經濟部中央標準局貝工消費合作社印製 Μ 419390__J;____ 五、發明説明() 除去粒子之過濾器也最好只用不產生氣體有機雜質之材料 構成。 其次,若利用本發明,提供一種過濾器,其特徵在於 將具有吸附氣體有機雜質之性質而且有效細孔徑大於該沸 石之有效細孔徑之無機物作爲黏接劑,使用以除去環境中 之氣體有機雜質之沸石固接在支撐物之表面。 又,提供一種過濾器,其特徵在於將無機物作爲黏接 劑,使用以除去環境中之氣體有機雜質之沸石固接在支撐 物之表面,形成第1吸附層;將具有吸附氣體有機雜質之 性質而且有效細孔徑大於該沸石之有效細孔徑之無機物固 接在該第1吸附層之表面,形成第2吸附層。在該過濾器, 在形成第1吸附層上用作黏接齊(I之無機物,也可具有比該 沸石之有效細孔徑大的有效細孔徑。 又,提供一種過濾器,其特徵在於將具有吸附氣體有 機雜質之性質而且有效細孔徑大於該沸石之有效細孔徑之 無機物作爲黏接劑,使將用以除去環境中之氣體有機雜質 之沸石造粒而成之小球固接在支撐物之表面。 又’提供一種過濾器,其特徵在於將無機物作爲黏接 劑,將用以除去環境中之氣體有機雜質之沸石造粒成小 球,使再在該小球之周圍塗了具有吸附氣體有機雜質之性 +質而且有效細孔徑大於該沸石之有效細孔徑之無機物而形 成之小球固接在支撐物之表面。 在這些過濾器,例如利用有效細孔徑8埃之沸石時, 利用有效細孔徑大於8埃之無機物除去環境中所含例如 8 ——--------— (,請先閲讀背面之注意事項再填寫本f) 訂 木紙張义戍適丨Π屮阎闽孓捣卑((’NS ) Λ4規洛(公兑) 經濟部中央標率局員工消費合作社印絮 ? ; 4193 90 a? > ___:__;___H7____ 五、發明説明() BHT或砂氧I元等用沸石無法吸附之分子徑大於8埃之氣體 有機雜質,而用沸石可除去例如DOP或DBP等分子徑小 於8埃之氣體有機雜質。此外,「黏結劑」除了固接沸石 和支撐物以外,還具有將沸石作爲一層結合之作用。 在這些過濾器,該支撐物例如可採用蜂巢構造物。那 時,該蜂巢構造物最好係以無機纖維爲必需成分之支撐 物。不僅該支撐物’而且藉著係吸附劑之沸石或用以使其 固接在支撐物表面之黏結劑也採用無機物,由構成本發明 之過濾器之材料不會發生氣體有機物之脫離。此外,在本 專利說明書中,蜂巢構造物未限定爲所謂的蜂巢構造,剖 面係格子形、波形等的也可。又,支撐物之構造未限定爲 蜂巢構造物,係空氣可通過構造物內部之其他各種構造也 可。例如石綿等三次元網目構造也適合用作支撐物。此時 如後述所示,不僅在網目構造之平面方向,而且在深度方 向也可令固接本發明之係吸附劑之沸石。在將吸附劑固接 在支撐物表面之方法上有,利用無機物之黏結劑固接之方 法,或者以無機物爲黏結劑將係吸附劑之沸石造粒成小球 後將該小球黏接在支撐物表面之方法。 又,若利用本發明,提供一種過濾器,其特徵在於將 具有吸附氣體有機雜質之性質而且有效細孔徑大於該沸石 +之有效細孔徑之無機物作爲黏接劑’將用以除去環境中之 氣體有機雜質之沸石造粒而成之小球充塡到外殼內而成。 又,提供一種過濾器,其特徵在於將無機物作爲黏接 劑,將用以除去環境中之氣體有機雜質之沸石造粒成小 9 本紙張尺度適/…1½¾家鸪# ( CNS ) Λ‘!規格(2丨f)〆297公綮) (請先閱讀背面之注意事項再填寫本頁)Printed by Shelley Consumer Cooperative, Central Standards Bureau of the Ministry of Economic Affairs M 419390__J; ____ 5. Description of the invention () The filter for removing particles should also be composed of materials that do not generate gaseous organic impurities. Secondly, if the present invention is used, a filter is provided, which is characterized in that an inorganic substance having the property of adsorbing gaseous organic impurities and having an effective pore diameter larger than the effective pore diameter of the zeolite is used as a binder to remove gaseous organic impurities in the environment. The zeolite is fixed on the surface of the support. In addition, a filter is provided, which is characterized in that an inorganic substance is used as an adhesive, and a zeolite used to remove gaseous organic impurities in the environment is fixed on the surface of the support to form a first adsorption layer; and it has the property of adsorbing gaseous organic impurities. In addition, an inorganic substance having an effective pore diameter larger than that of the zeolite is fixed on the surface of the first adsorption layer to form a second adsorption layer. In this filter, an inorganic substance used as a binder on the first adsorption layer (I) may have an effective pore diameter larger than the effective pore diameter of the zeolite. Further, a filter is provided, which is characterized by having An inorganic substance that adsorbs the properties of gaseous organic impurities and has an effective pore diameter larger than the effective pore diameter of the zeolite is used as a binder, so that the pellets formed by granulating zeolite used to remove gaseous organic impurities in the environment are fixed to the support. The surface also provides a filter, which is characterized in that inorganic substances are used as adhesives, and zeolites used to remove gaseous organic impurities in the environment are granulated into pellets, and the adsorbed gas is coated around the pellets. The nature of organic impurities + quality and inorganic pores with an effective pore size larger than the effective pore size of the zeolite are fixed to the surface of the support. In these filters, for example, when using a zeolite with an effective pore size of 8 angstroms, the effective Inorganic substances with a pore size greater than 8 angstroms are removed from the environment. For example, 8 ——--------— (Please read the precautions on the back before filling in this f) Π 屮 Yan Min 孓 Piaobei (('NS) Λ4 Regulations (confirmation) Printed by the Consumer Cooperatives of the Central Standards Bureau of the Ministry of Economic Affairs? 4193 90 a? ≫ ___: __; ___H7____ V. Description of the invention () BHT Gas or organic impurities with a molecular diameter of less than 8 angstroms, which cannot be adsorbed by zeolites, such as sand or oxygen, and gaseous organic impurities with a molecular diameter of less than 8 angstroms, such as DOP or DBP. In addition to zeolite and the support, it also has the function of combining zeolite as a layer. In these filters, for example, the support may be a honeycomb structure. At that time, the honeycomb structure is preferably a support using inorganic fibers as an essential component. Not only the support, but also an adsorbent-based zeolite or a binder used to fix the support to the surface of the support also uses an inorganic substance, and the gas constituting the filter of the present invention does not detach from the gas. In this patent specification, the honeycomb structure is not limited to a so-called honeycomb structure, and a cross-section lattice shape, a wave shape, etc. may be used. The structure of the support is not limited to a honeycomb structure. The air can pass through various other structures inside the structure. For example, a three-dimensional mesh structure such as asbestos is also suitable as a support. At this time, as shown below, the mesh structure can be used not only in the plane direction but also in the depth direction. The zeolite of the adsorbent system of the present invention is fixed. The method of fixing the adsorbent to the surface of the support includes the method of fixing the binder with an inorganic substance, or granulating the adsorbent zeolite with the inorganic substance as a binder. Method for bonding the small ball to the surface of the support after forming the small ball. In addition, if the present invention is used, a filter is provided, which is characterized in that it has the property of adsorbing gaseous organic impurities and has an effective pore diameter greater than that of the zeolite +. The inorganic material with a fine pore diameter is used as an adhesive agent. The pellets made of zeolite used to remove gaseous organic impurities in the environment are filled into the shell. In addition, a filter is provided, which is characterized in that inorganic matter is used as a binder, and zeolite used to remove gaseous organic impurities in the environment is granulated into 9 small papers of a suitable size / ... 1½¾ 家 鸪 # (CNS) Λ '! Specification (2 丨 f) 〆297mm 綮 (Please read the notes on the back before filling this page)
P -Γ Γ·' i 4^9390 i 4^9390 經濟部中央標準局員工消費合作社印製 五、發明説明() 球,使再在該小球之周圍塗了具有吸附氣體有機雜質之性 質而且有效細孔徑大於該沸石之有效細孔徑之無機物而形 成之小球充塡到外殼內而成。 在這些過濾器也一樣,例如利用有效細孔徑8埃之沸 石時,利用有效細孔徑大於8埃之無機物除去環境中所含 例如BHT或矽氧烷等用沸石無法吸附之分子徑大於8埃之 氣體有機雜質,而用沸石可除去例如DOP或DBP等分子 徑小於8埃之氣體有機雜質。還可得到設計上之融通性, 即按照空氣流路之形狀和面積、過濾器之設置條件,可適 當地選擇外殻之形狀和大小、小球之充塡量。 在此,該沸石不管是疏水性或是親水性都可。使用疏 7]C性沸石時,因空氣中之水分吸附量比親水性沸石的少’ 沸石多孔質構造所具有原來之吸附容量不會因水分吸附而 減少。因此,有過爐器之壽命比親水性沸石長之優點。而, 親水性沸石具有價格比疏水性沸石便宜之優點。 又,最好該沸石之有效細孔徑係7埃以上而且具有吸 附該氣體有機雜質之性質、有效細孔徑大於該沸石之有效 細孔徑之該無機物,分布在15〜300埃之範圍之每該無機物 單位重量之細孔的總容積係〇.2cc/g以上,或者該無機物之 細孔之比表面積係以上。那種具有有效細孔徑大 於該沸石之有效細孔徑之該無機物之主成分’具體而言’ 係多孔性黏土礦物、矽藻土、二氧化矽、氧化鋁、二氧化 矽和氧化鋁之混合物'砂酸絕、活性氧化鋁、多孔質玻璃 之其中之一或其混合物。而該多孔性黏土礦物最好係緞帶 10 (锖先閱讀背而之注意事項再填莴本頁)P -Γ Γ · 'i 4 ^ 9390 i 4 ^ 9390 Printed by the Consumer Cooperative of the Central Bureau of Standards of the Ministry of Economic Affairs 5. Description of the invention () The ball is coated with the property of adsorbing gas and organic impurities around the ball and Small spheres formed by inorganic substances having an effective pore diameter larger than the effective pore diameter of the zeolite are filled into the shell. The same applies to these filters. For example, when using a zeolite with an effective pore size of 8 angstroms, an inorganic substance with an effective pore diameter of more than 8 angstroms is used to remove the molecules contained in the environment that cannot be adsorbed by zeolite, such as BHT or silica. Gaseous organic impurities, and zeolite can remove gaseous organic impurities such as DOP or DBP with a molecular diameter of less than 8 angstroms. You can also get the design flexibility, that is, according to the shape and area of the air flow path and the conditions of the filter, you can appropriately choose the shape and size of the shell, and the amount of small balls. Here, the zeolite may be either hydrophobic or hydrophilic. When sparse 7] C zeolite is used, the amount of moisture absorbed in the air is less than that of hydrophilic zeolite. The original adsorption capacity of the zeolite porous structure will not be reduced by moisture adsorption. Therefore, there is an advantage that the life of the furnace is longer than that of the hydrophilic zeolite. However, hydrophilic zeolites have the advantage of being cheaper than hydrophobic zeolites. In addition, it is preferable that the effective pore size of the zeolite is 7 angstroms or more and has the property of adsorbing the gaseous organic impurities, and the effective pore size is larger than the effective pore size of the zeolite. The total volume of the pores per unit weight is 0.2 cc / g or more, or the specific surface area of the pores of the inorganic substance is more than. The main component of the inorganic substance having an effective pore diameter greater than the effective pore diameter of the zeolite is, specifically, a porous clay mineral, diatomaceous earth, silica, alumina, a mixture of silica and alumina. One of oxalic acid, activated alumina, porous glass, or a mixture thereof. And this porous clay mineral is best to have a ribbon 10 (read the precautions before filling in this page)
本紙張尺度遴⑴中内阀窣抒净((:_NS ) Λ4規格(:!丨公萍) 經濟部中央標隼局員工消费合作社印裒 i 419390 B7 * 五、發明说明() 狀構造之含水矽酸鎂質黏土礦物、活性白黏土、酸性白黏 土、活性膨潤土、矽酸鋁金屬鹽之微結晶和二氧化矽微粒 子之複合物之其中之一或其混合物。不管如何,具有吸附 該氣體有機雜質之性質、有效細孔徑大於該沸石之有效細 孔徑之該無機物,同時具有將該沸石之粉末機械式地載持 在支撐物表面之性能或作爲將該沸石造粒成小球時之結合 劑之性能,和吸附用該沸石無法吸附之分子徑大於該沸石 之有效細孔徑之氣體有機雜質之性能。此外,該過濾器只 由不發生氣體有機雜質之材料構成,最好該過濾器只由不 含可燃物之材料構成。 又,該無機物包含無機系固接輔助齊彳也可。那時,最 好無機系固接輔助劑至少包含矽酸蘇打、二氧化矽或氧化 鋁之中至少一個。 又,若利用本發明,提供一種過濾器之製造方法’其 特徵在於藉著使支撐物浸入令用以除去環境中之氣體有機 雜質之沸石之粉末和具有吸附氣體有機雜質之性質而且有 效細孔徑大於該沸石之有效細孔徑之作爲黏接劑之無機物 之粉末分散之懸濁液後乾燥,在該支撐物之表面形成吸附 J^5r。 又,提供一種過濾器之製造方法,其特徵在於藉著使 支撐物浸入令用以除去環境中之氣體有機雜質之沸石之粉 末和作爲黏接劑之無機物之粉末分散之懸濁液後乾燥,在 該支撐物之表面形成第1吸附層,藉著再浸入令具有吸附 氣體有機雜質之性質而且有效細孔徑大於該沸石之有效細 11 (請先聞讀背V1SJ之注意事項再填寫本頁 一 m n - i .1^ 本紙银尺度適州中阀阀家標萃(CNS > Λ4現格(Ή0/297公筇) 經濟部中去標準局員工消費合作社印製 ^ 4/193 90 A7 ___ R7___ 1、發明説明() 孔徑之無機物之粉末分散之懸濁液後乾燥,在該第1吸附 層之表面形成第2吸附層。 若利用這些過濾器之製造方法,該過濾器可只由不發 生氣體有機雜質之材料構成。又實質上該過濾器就只用不 含可燃物之材料構成。此外,在這些製造方法,在該支撐 物之表面形成第1吸附層後再在第1吸附層之上面形成第2 吸附層時,在該無機物之懸濁液混入了溶膠狀態之無機系 固接輔助劑之情況,該無機物就包含無機系固接輔助劑。 又.,若利用本發明,提供一種潔淨裝置,在具有使已 調節濕度之空氣循環之機構之潔淨裝置,在空氣之循環路 徑設置上述本發明之其中一種過濾器和配置在該過濾器之 下游側之除去粒子狀雜質之除去粒子之過濾器。若利用該 潔淨裝置,就可在不使濕度降低下除去在潔淨裝置內循環 之空氣中之氣體有機雜質。該潔淨裝置,因未使用係可燃 物之活性炭,在防災上優異,因此,就可將該過據器和除 去粒子之過濾器配在潔淨裝置之天花板部。 其次,若利用本發明,提供一種過瀘器,其特徵在於 在令和具有合成沸石之通氣性第1過濾部之上游側或下游 側相鄰下配置具有吸附氣體有機雜質之性質而且具有有效 細孔徑大於該合成沸石之有效細孔徑之無機吸附劑之通氣 性第2過濾部。該過濾器,因未使用係可燃物之活性炭, 在防災上優異。若利用該過濾器’就可在不使濕度降低下 除去在潔淨裝置內循環之空氣中之氣體有機雜質。在該過 濾器,該第1過濾部之構造係使合成沸石固接在支撐物之 (請先閱讀背由之注意事項再填寫本頁)In this paper, we select the internal valve ((: _NS)) Λ4 specification (:! 丨 Gongping), the staff consumer cooperative of the Central Bureau of Standards of the Ministry of Economic Affairs, India 419390 B7 * 5. Description of the invention () Water in the structure One or a mixture of magnesium silicate clay minerals, activated white clay, acidic white clay, activated bentonite, microcrystals of aluminum silicate metal salts, and silicon dioxide microparticles. In any case, it has the ability to adsorb the gas organically The nature of the impurities, the inorganic substance having an effective pore diameter larger than the effective pore diameter of the zeolite, and at the same time the performance of mechanically supporting the powder of the zeolite on the surface of the support or as a binder when granulating the zeolite into pellets Performance and the performance of adsorbing gaseous organic impurities whose molecular diameter cannot be absorbed by the zeolite is larger than the effective pore size of the zeolite. In addition, the filter is only composed of materials that do not generate gaseous organic impurities. Combustible material-free material. The inorganic substance may include an inorganic fixing aid. In that case, it is preferable that the inorganic fixing aid contains at least At least one of acid soda, silicon dioxide, or alumina. In addition, if the present invention is used, a method for manufacturing a filter is provided, which is characterized in that a zeolite is used to remove gaseous organic impurities in the environment by immersing a support. The powder and the suspension of powder dispersed inorganic powder which has the property of adsorbing gaseous organic impurities and has an effective pore diameter larger than the effective pore diameter of the zeolite as an inorganic substance as a binder are dried to form an adsorption J ^ 5r on the surface of the support. In addition, a method for manufacturing a filter is provided, which is characterized by immersing a support in a suspension liquid in which a powder of zeolite used to remove gaseous organic impurities in the environment and a powder of inorganic material as a binder are dispersed, and then dried, A first adsorption layer is formed on the surface of the support. By re-immersion, it has the property of adsorbing gaseous organic impurities and the effective pore size is greater than the effective pore size of the zeolite. 11 (Please read the precautions of V1SJ before filling in this page. mn-i .1 ^ This paper is a silver standard of Shizhou Zhong valve and valve house standard (CNS > Λ4 is current (Ή0 / 297) 筇) Printed by the cooperative ^ 4/193 90 A7 ___ R7___ 1. Description of the invention () The suspension of the dispersed powder of inorganic material with pore size is dried and a second adsorption layer is formed on the surface of the first adsorption layer. If these filters are used In the manufacturing method, the filter can be composed only of materials that do not generate gaseous organic impurities. In fact, the filter is only composed of materials that do not contain combustible materials. In addition, in these manufacturing methods, the first surface of the support is formed. When the second adsorption layer is formed on the first adsorption layer after the first adsorption layer, when the suspension of the inorganic substance is mixed with the inorganic fixing aid in the sol state, the inorganic substance includes the inorganic fixing aid. In addition, if the present invention is used, a clean device is provided. In the clean device having a mechanism for circulating the humidity-adjusted air, one of the filters of the present invention described above and a filter disposed in the filter are provided in the air circulation path. Particle filter for removing particulate impurities on the downstream side. By using the cleaning device, the gaseous organic impurities in the air circulating in the cleaning device can be removed without reducing the humidity. The clean device is excellent in disaster prevention because it does not use flammable activated carbon. Therefore, it is possible to arrange the collector and the filter for removing particles on the ceiling of the clean device. Next, if the present invention is used, a purifier is provided, which is characterized in that it is arranged adjacent to the upstream side or the downstream side of the first permeable filter having a synthetic zeolite, and has the property of adsorbing organic impurities in the gas and has effective fineness. The air-permeable second filtering part of the inorganic adsorbent having a pore diameter larger than the effective pore diameter of the synthetic zeolite. This filter is excellent in disaster prevention because it does not use flammable activated carbon. By using this filter ', gaseous organic impurities in the air circulating in the clean device can be removed without reducing the humidity. In this filter, the structure of the first filter section is to fix the synthetic zeolite to the support (please read the precautions before filling in this page)
本紙張尺度速;!’|中阀阀家活莩(〔、>«)/\4現格(2!〇/2<^公冷) 經濟部中央標率局負工消费合作社印製 ν ί .我、θ39〇 β7 ______ ______—--— 7、發明说明() 表面,該第2過濾部之構造係使該無機吸附劑固接在支撐 物之表面也可。此時,例如該第1過濾部之構造係藉著使 支撐物浸入令該合成沸石分散之懸濁液後乾燥而使合成沸 石固接在支撑物之表面,該第2過濾部之構造係藉者使支 撐物浸入令該無機吸附劑分散之懸濁液後乾燥而使無機吸 附劑固接在支撐物之表面。 .又,該第1過濾部之構造係使用合成沸石之粉末形成 之小球固接在支擦物,該第2過爐部之構造係使用該無機 吸附齊!1之粉末形成之小球固接在支撐物也可。 此外,也可將具有透氣性之支撐物以和該支撐物之通 氣方向交叉之境界面爲境界分割成2個區域,在—個區 域,讓用合成沸石或合成沸石粉末形成之小球固接在支撐 物之表面,形成第1過濾部,在另一個區域,讓用無機吸 附劑或該無機吸附劑之粉末形成之小球固接在支擦物之表 面,形成第2過濾部。 又,讓用合成沸石或合成沸石粉末形成之小球固接在 支撐物之表面時,及/或讓用無機吸附劑或該無機吸附劑之 粉末形成之小球固接在支撐物之表面時最好使用由滑石、 高嶺礦物、膨潤土、矽酸蘇打、二氧化矽或氧化鋁之至少 一種構成之固接輔助劑。 ' 該第2過濾部之無機吸附劑由矽藻土、二氧化矽、氧 化鋁、二氧化矽和氧化鋁之混合物、矽酸鋁、活性氧化鋁、 多孔質玻璃、緞帶形構造之含水矽酸鎂質黏土礦物、活性 白黏土、酸性白黏土、活性膨潤土之至少一種構成也可。 13 (諸先閱讀背面之注意事項再填寫本頁) i. 丁 -m 本紙張尺度適坷中闲闽家榡缂(CMS > Λ4規格(21ϋ>·π7公埯) 經濟部中央標準局黃工消费合作社印掣 A7 ’,(A 193 9 0_^____ i、發明説明() 又,在該合成沸石之有效細孔徑係7埃以上,而且在 該第2過濾部之無機吸附劑,係分布在15〜300埃之範圍之 每單位重量之細孔的總容積係〇.2cc/g以上,或者該無機吸 附劑之細孔之比表面積係l〇〇m2/g以上也可。 該支撐物可採用蜂巢構造物。此時,該蜂巢構造物最 好係以無機纖維爲必需成分之支撐物。 又,將該合成沸石之小球充塡在外殼內,構成該第1 過濾部,將該無機吸附劑之小球充塡在另一外殼內,構成 該第2過濾部也可。此外,該合成沸石最好係疏水性。 【發明之最佳實施例】 以下,邊參照附加之圖面邊說明本發明之最佳實施 例。 圖1係槪略表示之本發明之實施例1之潔淨裝置1之 構造之說明圖。該潔淨裝置1 ,具體而言例如係無塵室或 無塵操作台等。洗淨裝置1由用以製造例如LSI或LCD等 之處理空間2、位於該處理空間2之上下之天花板部(送 氣增壓系統)3和地板下面部(回氣增壓系統)4、以及 位於處理空間2之側方之回氣通路5構成。 在天花板部3 gB置風扇單元10和具有透氣性之過濾器 11及具有除去粒子之過濾器12之潔淨風扇單元13 »在處 理空間2設置成爲熱產生源之例如半導體製造裝置14。地 板下面部4用鑽了多個孔之多孔板15隔開。又,在地板下 面部4設置用以處理半導體製造裝置14之顯熱負載之無結 14 本紙張尺度试川中阁囤孓棵準(C,NS》Λ4規格(UOX 2W公淡) (請先閲讀背面之注意事項再填寫本頁)Speed of this paper;! '| Zhong valve valve home activity ([, > «) / \ 4 present grid (2! 〇 / 2 & ^ public cold) Printed by the Central Standards Bureau of the Ministry of Economic Affairs, Consumer Cooperatives ν ί. I, θ39〇β7 ______ ______ --- 7. Description of the invention () On the surface, the structure of the second filter part may fix the inorganic adsorbent on the surface of the support. At this time, for example, the structure of the first filter unit is obtained by immersing a support in a suspension liquid in which the synthetic zeolite is dispersed and drying the structure to fix the synthetic zeolite on the surface of the support. One is to immerse the support in the suspension in which the inorganic adsorbent is dispersed, and then to dry the inorganic adsorbent to the surface of the support. In addition, the structure of the first filter section is fixed to the rubbing ball using a powder formed of a powder of synthetic zeolite, and the structure of the second furnace section uses a solid ball formed of the inorganic adsorption powder! It can be attached to the support. In addition, a breathable support can also be divided into two areas with the boundary interface that intersects the ventilation direction of the support as the realm. In one area, the beads formed by synthetic zeolite or synthetic zeolite powder are fixed. A first filter portion is formed on the surface of the support, and in another area, a ball formed of an inorganic adsorbent or a powder of the inorganic adsorbent is fixed to the surface of the support to form a second filter portion. In addition, when a small ball formed by synthetic zeolite or a synthetic zeolite powder is fixed to the surface of the support, and / or a small ball formed by an inorganic adsorbent or a powder of the inorganic adsorbent is fixed to the surface of the support. It is preferable to use a fixing adjuvant composed of at least one of talc, kaolin mineral, bentonite, silicate soda, silica, or alumina. '' The inorganic adsorbent of the second filter is composed of diatomaceous earth, silica, alumina, a mixture of silica and alumina, aluminum silicate, activated alumina, porous glass, and ribbon-shaped aqueous silicon. At least one kind of magnesium acid clay mineral, activated white clay, acidic white clay, and activated bentonite may be used. 13 (Please read the notes on the back before filling in this page) i. Ding-m This paper is suitable for medium and small households (CMS > Λ4 size (21ϋ > · π7 埯)) Central Standards Bureau of the Ministry of Economic Affairs Industrial and consumer cooperatives 'printing A7', (A 193 9 0 _ ^ ____ i. Description of the invention () In addition, the effective pore diameter of the synthetic zeolite is 7 angstroms or more, and the inorganic adsorbent in the second filtering section is distributed. The total volume of the pores per unit weight in the range of 15 to 300 Angstroms is 0.2 cc / g or more, or the specific surface area of the pores of the inorganic adsorbent is 100 m2 / g or more. A honeycomb structure can be used. In this case, the honeycomb structure is preferably a support using inorganic fibers as an essential component. In addition, the pellets of the synthetic zeolite are filled in a casing to constitute the first filtering part, and the The pellets of the inorganic adsorbent may be filled in another casing to form the second filtering portion. In addition, the synthetic zeolite is preferably hydrophobic. [Best Embodiment of the Invention] Hereinafter, referring to the attached drawings The preferred embodiment of the present invention will be described below. An explanatory diagram of the structure of the cleaning device 1 of the embodiment 1. The cleaning device 1 is, for example, a clean room or a clean operation table, etc. The cleaning device 1 is used for manufacturing a processing space such as an LSI or an LCD. 2. The ceiling portion (supply booster system) 3 located above and below the processing space 2 and the lower floor portion (return booster system) 4 and the return air passage 5 located on the side of the processing space 2 are formed. 3 gB fan unit 10, air-permeable filter 11 and particle-removing filter 12 clean fan unit 13 »For example, a semiconductor manufacturing device 14 is installed in the processing space 2 as a heat generation source. The bottom floor part 4 is drilled. Multi-well plates 15 with multiple holes are separated. Furthermore, a junction 14 for processing the sensible heat load of the semiconductor manufacturing device 14 is provided on the lower part 4 of the floor. Specifications (UOX 2W public light) (Please read the precautions on the back before filling this page)
經濟部中央標準局員工消費合作社印敢 ,丨 4193 90 "7 • Η / 五、發明説明() 露盤管16。無結露盤管16意指以在熱交換器表面不結露 之條件下冷卻空氣之空氣冷卻器。在回氣通路5設置溫度 感測器17,控制無結露盤管16之冷水流量調整閥18,使 得該溫度感測器17所偵測到之溫度變成指定之設定値,而 且在盤管不結露下保持固定之濕度° 而且,藉著潔淨風扇單元13之風扇單元10運轉,在 調整適當的氣流速度下,潔淨裝置1內部之空氣按照天花 板部3—處理空間2->地板下面部4一回氣通路5->天花板 部3之順序流動循環。又,在該循環中,被無結露盤管16 冷卻,利用潔淨風扇單元13內之過濾器11和除去粒子之 過濾器12除去空氣中之氣體有機雜質和粒子狀雜質,向處 理空間2內供給適溫且潔淨之空氣。 過濾器11具有用以自循環空氣除去氣體有機雜質之 疏水性沸石。又過濾器11只由不含可燃物而且不發生氣體 有機雜質之材料構成。 除去粒子之過濾器12配置在過濾器11之下游側,該 除去粒子之過濾器12具有可除去粒子狀雜質之功能。又, 用以除去灰塵等之除去粒子之過濾器12只由不發生氣體 有機雜質之材料構成。 又,所吸入外氣經由外氣路徑20適當地供給潔淨裝置 _ 1之地板下面部4內。在該外氣路徑20配置具有用以自所 吸入外氣除去氣體有機雜質之疏水性沸石之過濾器21,在 過濾器21之上游側設置進行所吸入外氣之除塵、調溫、調 濕之單元型空調機器22。又,在外氣路徑20 置濕度感 15 本紙張尺度珣州中阈同家標辛(C:NS ) Λ4規格(〕】()乂29:?公筇) (讀先閱讀背面之注意事項再填寫本f) 訂 經濟部中央標率局員工消費合作社印製 V 4193 90 B7___ 五、發明説明() 測器27,控制單元型空調機器22之調濕部之供水壓力調 整閥29,使得濕度感測器27所偵測到之濕度變成指定之 設定値。而,在處理空間2內設置濕度感測器28 ’用該濕 度感測器28偵測處理空間2內之環境之濕度。 由外氣路徑20供給潔淨裝置1之地板下面部4之所吸 入外氣,經由回氣通路5及天花板部3引入處理空間2。 此外,該所吸入外氣和主要由生產之排氣構成之排氣被控 制成保持供排氣量之平衡,使得室內壓力變成定値。排氣 由排氣口 25經由排氣孔26排到室外。 圖2係過濾器11之槪略的分解組立圖。在相鄰之波形 片30之間具有在構造上挾住無凹凸之薄板片31之蜂巢構 造物32,在該蜂巢構造物32之表面整體固接疏水性沸石。 如後述所示,疏水性沸石之有效細孔徑最好係7埃以上。 如圖所不,過灑器11在構造上’將錦製外框35a、35b、 35c、35d組立成筒形,使得朝向所處理空氣之流通方向 (圖中,空白箭頭33所示之方向),在其內部空間配置表 面固接了疏水性沸石之蜂巢構造物32。吸附層11之外形 及尺寸可配合設置空間任意地設計變更。 簡單地說明過濾器U之製造方法之一例。無機纖維 (陶磁纖維、玻璃纖維、二氧化矽纖維、氧化銘纖維)和 有機材料(紙漿、熔融維尼隆之混合物)及矽酸鈣3種材 料以1 : 1 : 1之等重量混合,利用濕式抄紙法抄製成厚 度約0.3mm。此外,也可使用以矽酸鎂爲主成分之海泡石 (sepiolite)、砍酸銘鐵載體(attapalgite)等之黏土礦物,替代 16 本紙張尺度適⑴中®闷家捽孪() ΛΑ規格(2!〇 / 公苋) ~ (請先間讀背面之注意事項再填窍本頁) 丁 ,言 經濟部中央標準局員工消费合作社印裝 Γ 415390 五、發明説明() 矽酸鈣。利用波形板軋機將該抄製片加工成波形,用^接 劑將所製成之波形片30黏在薄板片31,形成圖2所示之 蜂巢構造物32。將該蜂巢構造物32放入電氣爐’進行100 t:、1小時之熱處理後,完全除去有機成分’使蜂巢構造 物32變成多孔性。其次,將多孔性蜂巢構造物 水性沸石之粉末(數μπι )和無機系溶膠黏接劑(矽膠 '氧 化鋁溶膠等)分散之懸濁液中數分鐘後,以300 °C、1小 時之熱處理乾燥,就可得到過濾器11。這樣得到之過濾器 11,因在構成材料上不含可燃物,完全脫離並除去在將吸 附層熱處理時構成材料所含成爲表面污染之原因之氣體有 機雜質成分,過濾器本身也不會發生氣體有機雜質。 其次,說明過濾器11之其他製造方法之一例。到製造 蜂巢構造物32爲止和剛才說明之製造方法例一樣。在上述 例子,使多孔性蜂巢構造物32含浸疏水性沸石之粉末(數 μηι ),但是在本例,用黏接齊!!使粒狀疏水性沸石附著在蜂 巢構造物32。圖3係在本例之製造方法之過濾器11之模 式剖面部分放大圖。在波形片3〇和薄板片31之表面整體 用不易燃性黏接劑無間隙地固接粒狀疏水性沸石36。然 後,藉著將該蜂巢構造物32放入電氣爐,在黏接劑之耐熱 溫度以下之100 °C進行1小時之熱處理後,完全脫離並除 去黏接劑所含成爲表面污染之原因之氣體有機雜質成分, 製造過濾器11。所處理空氣通過圖3所示剖面形狀成虛擬 半月形之筒形空間37。此外’如圖4所示,也可藉著在由 山形片3 8和薄板片31組合而成之蜂巢構造物32之表面整 (請先閱請.背面之注意事項再填寫本頁)Yin Gan, Staff Consumer Cooperative of the Central Standards Bureau of the Ministry of Economic Affairs, 4193 90 " 7 • Η / V. Description of the invention () Exposed coil tube 16. The non-condensing coil 16 means an air cooler that cools the air without dew condensation on the surface of the heat exchanger. A temperature sensor 17 is provided in the return air passage 5 to control the cold water flow adjustment valve 18 of the non-condensing coil 16 so that the temperature detected by the temperature sensor 17 becomes a specified setting 値 and there is no condensation on the coil The fixed humidity is maintained below. Furthermore, by operating the fan unit 10 of the clean fan unit 13, the air inside the clean device 1 is adjusted in accordance with the ceiling section 3-processing space 2- > The return air passage 5- > the sequential flow cycle of the ceiling portion 3. In this cycle, it is cooled by the non-condensing coil 16, and the gaseous organic impurities and particulate impurities in the air are removed by the filter 11 and the particle removing filter 12 in the clean fan unit 13 and are supplied into the processing space 2. Suitable temperature and clean air. The filter 11 has a hydrophobic zeolite for removing gaseous organic impurities from the circulating air. The filter 11 is made of a material that does not contain combustible materials and does not generate gaseous organic impurities. The particle removing filter 12 is disposed downstream of the filter 11. The particle removing filter 12 has a function of removing particulate impurities. In addition, the particle-removing filter 12 for removing dust and the like is composed of a material that does not generate gaseous organic impurities. The inhaled outside air is appropriately supplied to the floor lower portion 4 of the cleaning device _ 1 via the outside air path 20. A filter 21 having a hydrophobic zeolite for removing gaseous organic impurities from the inhaled outside air is arranged in the outside air path 20, and an upstream side of the filter 21 is provided for dust removal, temperature adjustment and humidity adjustment of the inhaled outside air. Unit type air conditioner 22. Also, place humidity in the outside air path 20 and set the humidity 15 in the paper size. Quzhou middle threshold same standard Xin (C: NS) Λ4 specifications (]) () 乂 29:? Public 筇) (Read the precautions on the back before filling Book f) Order V 4193 90 B7___ printed by the Consumer Cooperatives of the Central Standards Bureau of the Ministry of Economic Affairs. 5. Description of the invention () Detector 27, water supply pressure adjustment valve 29 of the humidity control section of the control unit type air conditioner 22, to make humidity sensing The humidity detected by the device 27 becomes the specified setting. A humidity sensor 28 'is provided in the processing space 2', and the humidity of the environment in the processing space 2 is detected by the humidity sensor 28. The sucked-in outside air supplied to the lower floor portion 4 of the cleaning device 1 through the outside air path 20 is introduced into the processing space 2 through the return air passage 5 and the ceiling portion 3. In addition, the inhaled outside air and the exhaust gas mainly composed of the produced exhaust gas are controlled to maintain a balance between the supply and exhaust volume so that the indoor pressure becomes constant. Exhaust is discharged to the outside through the exhaust port 25 through the exhaust hole 26. FIG. 2 is a schematic exploded assembly view of the filter 11. A honeycomb structure 32 is provided between the adjacent corrugated sheets 30 to hold the non-concavo-convex sheet 31 in structure. A hydrophobic zeolite is fixed to the entire surface of the honeycomb structure 32. As will be described later, the effective pore diameter of the hydrophobic zeolite is preferably 7 angstroms or more. As shown in the figure, the sprinkler 11 is structurally 'assembled the brocade frames 35a, 35b, 35c, 35d into a cylindrical shape so as to face the flow direction of the processed air (the direction shown by the blank arrow 33 in the figure) A honeycomb structure 32 having a hydrophobic zeolite immobilized on the surface is arranged in its internal space. The shape and size of the adsorption layer 11 can be arbitrarily designed and changed according to the installation space. An example of a method of manufacturing the filter U will be briefly described. Inorganic fiber (ceramic fiber, glass fiber, silicon dioxide fiber, oxidized fiber), organic materials (mixture of pulp, fused vinylon), and calcium silicate are mixed in an equal weight of 1: 1, using wet type The papermaking method makes a thickness of about 0.3 mm. In addition, clay minerals such as sepiolite and attapalgite with magnesium silicate as the main component can also be used instead of 16 papers of moderate size ® 捽 家 捽 双 () ΛΑ specifications (2! 〇 / public money) ~ (Please read the precautions on the back before filling out this page) Ding Yanyan, printed by the Consumer Cooperatives of the Central Standards Bureau of the Ministry of Economic Affairs 415 390 5. Description of the invention () Calcium silicate. This copied sheet was processed into a corrugated sheet by a corrugated sheet rolling mill, and the corrugated sheet 30 produced was bonded to the thin sheet sheet 31 with a cement to form a honeycomb structure 32 as shown in FIG. 2. The honeycomb structure 32 was placed in an electric furnace 'and subjected to a 100 t: heat treatment for 1 hour, and then the organic components were completely removed' to make the honeycomb structure 32 porous. Secondly, disperse the porous honeycomb structure aqueous zeolite powder (several μm) and the inorganic sol adhesive (silicone, alumina sol, etc.) in the suspension for several minutes, and then heat-treat at 300 ° C for 1 hour. The filter 11 is obtained by drying. The filter 11 thus obtained does not contain flammable materials in the constituent material, and completely removes and removes gaseous organic impurities that cause surface contamination contained in the constituent material when the adsorption layer is heat-treated. The filter itself does not generate gas Organic impurities. Next, an example of another manufacturing method of the filter 11 will be described. Until the honeycomb structure 32 is manufactured, it is the same as the manufacturing method example just described. In the above example, the porous honeycomb structure 32 is impregnated with the powder (a few μm) of the hydrophobic zeolite. However, in this example, the granular hydrophobic zeolite is adhered to the honeycomb structure 32 by bonding together. Fig. 3 is an enlarged partial sectional view of the filter 11 in the manufacturing method of this example. The granular hydrophobic zeolite 36 is fixed to the entire surface of the corrugated sheet 30 and the thin plate sheet 31 with a non-flammable adhesive without gaps. Then, by putting the honeycomb structure 32 into an electric furnace, and performing a heat treatment at 100 ° C below the heat-resistant temperature of the adhesive for 1 hour, the gas contained in the adhesive that causes the surface contamination is completely removed and removed. Organic impurity component, and the filter 11 is manufactured. The processed air passes through a cylindrical space 37 having a virtual half-moon shape in cross section as shown in FIG. In addition, as shown in FIG. 4, the surface of the honeycomb structure 32 composed of a mountain-shaped sheet 38 and a thin sheet 31 can be adjusted (please read it first. Please note on the back before filling this page)
本紙ilui適用中函[.¾家枕疗( M ) Μ现格(2以)〆297公筇) 經濟部中央標準局真工消費合作社印製 ί 4 193 90 五、發明説明() 體用不易燃性黏接劑無間隙地固接粒狀疏水性沸石36,製 造過濾器11。該圖4之情況,所處理空氣通過剖面形狀成 三角形之筒形空間39。 照這樣製造之過濾器11,因構成材料不含可燃物,如 圖1所示將過濾器11裝在天花板部3之情況,和將以係可 燃物之活性炭爲基底之習知之化學式過濾器裝在天花板面 之情況相比,在防災上之安全性上顯著提高。此外,在圖1 所示之潔淨裝置1 ,若處理所吸入外氣之過濾器21和處理 循環空氣之過濾器11都採用相同的構造,和以係可燃物之 活性炭爲基底之習知之化學式過濾器裝在天花板面之情況 相比,在防災上之安全性上更高。 在係除去粒子之過濾器之一般的中性能過濾器或 HEPA過瀘器、ULPA過濾器,因在過濾件使用含有揮發 性有機物之黏接劑,有來自黏接劑之逸脫氣體。因此,除 去粒子之過濾器12使用未用黏接劑之過濾件,或者即使使 用黏接劑也使用藉由加熱移除等處理除去了揮發性有機物 之過濾件,此外最好在係將過濾件固定在框架之裝置之密 封件也選擇不會發生逸脫氣體之種類,或用無逸脫氣體之 材料在物理上壓住過濾件而固定在框架。 其次,本發明之實施例1之另一潔淨裝置1'如圖5所 示。圖5所示之潔淨裝置1'不是將使疏水性沸石固接之蜂 巢構造物之過濾器11裝在潔淨裝置1'之天花板部3全面, 在各處間隔設置。在本例,和圖1相比,過濾器11之設置 台數變成一半。其他方面和剛才在圖1所說明之潔淨裝置1 18 本紙張尺度適用中闽國京棉準(C/NS ) Λ4規格(公筇) (請先閱讀背面之注意事項再填寫本頁)This paper ilui is applicable to Chinese letter [. ¾ Home Pillow Therapy (M) M is current (2 to) 〆297 public 筇) Printed by the Real Consumer Cooperatives of the Central Standards Bureau of the Ministry of Economic Affairs ί 4 193 90 V. Description of the invention The flammable adhesive is fixed to the granular hydrophobic zeolite 36 without gaps to produce a filter 11. In the case of Fig. 4, the processed air passes through a cylindrical space 39 having a triangular cross-section. Since the filter 11 manufactured in this way does not contain combustible materials, as shown in FIG. 1, the filter 11 is mounted on the ceiling portion 3, and the conventional chemical filter based on activated carbon based on combustible materials is installed. Compared with the situation on the ceiling, the safety in disaster prevention is significantly improved. In addition, in the clean device 1 shown in FIG. 1, if the filter 21 for processing the inhaled outside air and the filter 11 for processing the circulating air both have the same structure, and the conventional chemical filtering based on activated carbon based on combustibles Compared with the case where the device is installed on the ceiling surface, the safety in disaster prevention is higher. In general, medium-performance filters, HEPA filters, and ULPA filters are filters that remove particles. Because the filter contains an adhesive containing volatile organic compounds, there is an escape gas from the adhesive. Therefore, the filter 12 for removing particles uses a filter without an adhesive, or even if an adhesive is used, a filter with volatile organic compounds removed by heat removal or the like is used. The seal of the device fixed to the frame is also selected to be a type that does not cause outgassing, or a filter element is used to physically press the filter to fix it to the frame. Next, another cleaning device 1 'according to Embodiment 1 of the present invention is shown in FIG. The cleaning device 1 ′ shown in FIG. 5 is not that the filter 11 of the honeycomb structure to which the hydrophobic zeolite is fixed is installed on the ceiling portion 3 of the cleaning device 1 ′ in its entirety and spaced apart from each other. In this example, as compared with FIG. 1, the number of filters 11 is set to half. In other respects, and the cleaning device 1 just described in Figure 1, this paper size is applicable to the China Minjing Beijing Cotton Standard (C / NS) Λ4 specifications (public money) (Please read the precautions on the back before filling this page)
h如——II ,-- i^n =_ ...... _ - 經濟部中央標準局員工消費合作社印製 、Γ 4193 90 B; 熹 - 1 1 - 1-- —— — _ _ 五、發明説明() 之構造一樣。因此,在圖5所示之潔淨裝置1',藉著對和 剛才在圖1所說明之潔淨裝置1 一樣之構成元件賦與相同 的符號,省略詳細說明。 在進行半導體之製造等之潔淨裝置發生之成爲基板表 面污染之原因之有機物只限於自密封劑發生之有機物矽氧 烷、自建材中之不易燃劑發生之磷酸酯、自建材中之可塑 劑產生之鄰苯二甲酸鹽、自光阻劑密接劑發生之HMDS、 自盒之防止氧化劑發生之BHT等高沸點•高分子有機化合 物。這些有機物之發生源係無塵室等潔淨裝置之構成材料 或位於潔淨裝置內部之用於製造之各種零件,由所吸入外 氣弓1起的很少。因此,過濾器Η之作用主要係自循環空氣 中除去在潔淨裝置內部發生之成爲表面污染之原因之高沸 點•高分子有機化合物,降低潔淨裝置內部之這些有機物濃 度。具有過濾器11之潔淨裝置運轉時,在運轉初期潔淨裝 置內部之有機物濃度最高,隨著運轉時間之經過,自循環 空氣中逐一除去這些有機物,濃度就降低下去,終於在和 潔淨裝置內部之發生量平衡之濃度穩定化。關於空氣循環1 次所除去有機物量,比較裝在天花板全面之圖1之潔淨裝 置1和間隔安裝之圖5之潔淨裝置1',有2 : 1之關係。 即,自運轉初期之最高濃度到到達和潔淨裝置內部之發生 量平衡爲止之時間,在間隔安裝之圖5之潔淨裝置1'之情 況比裝在天花板全面之圖1之潔淨裝置1之情況長很多。 又,最終到達之平衡濃度,在間隔安裝之情況也比裝在天 花板全面之情況稍高。即,有間隔安裝時濃度之降低費時、 19 — _^--------Q II (請先閱讀背面之注意事項存填寫本1) .1Τ 本紙張尺度過扪中阈囚家標嗥|.(-’:^)/\4圯格(21〇/247公漦) 經滴部中央橾準局員工消f合作社印聚 Ί 419390 g i — . 五、發明説明() 降低後之平衡濃度也比全面安裝之情況稍高之缺點,但是 由於想減少過濾器11之起始費用或定期更換所伴隨之運 轉費用之經濟上的要求,如圖5之實例所示,間隔設置過 濾器11之情況也不少。 其次,在圖6說明本發明之實施例2之過濾器100。 該過濾器100也具有和剛才在圖2所說明之過濾器11 大致相同之構造。但,在本實施例2之過濾器100,在構 造上的不同點係使用有效細孔徑比該沸石之有效細孔徑大 之有機物作爲黏接劑,使粉末狀之沸石固接在蜂巢構造物 112之表面整體。即,本實施例2之過濾器100,在構造 上在外框115a、115b、115c、115d之內部空間在和通 氣方向113近似平行地交互堆積使用該無機物作爲黏接劑 將粉末狀沸石固接在表面之波形片110和薄板片111。過 濾器100之外形或尺寸等可配合設置空間任意設計。 在此,說明過濾器100之製造方法之一例。到蜂巢構 造物成形爲止之製程和上述方法一樣。因在除去有機質成 分後之蜂巢構造物m之表面殘留無數微米大小之凹坑, 可製造以該凹坑爲孔之多孔性蜂巢構造物112。以後吸附 劑或黏接劑之微粒子就嵌入該凹坑。其次,將該蜂巢構造 物112浸泡在使沸石之粉末和具有吸附氣體有機雜質之性 質而且使用有效細孔徑比該沸石之有效細孔徑大之作爲黏 接劑之無機物,例如黏土礦物、矽藻土、二氧化政、氧化 鋁、二氧化矽和氧化鋁之混合物、矽酸鋁、活性氧化鋁、 多孔質玻璃等分散之懸濁液中數分鐘後拉起’以300 °c、1 一 20__ 本紙張尺度過用中阈固( (.NsTa4祕(2iOx 297公漦) (請先閱讀背面之注意事項再填寫本頁)h as ——II,-i ^ n = _ ...... _-printed by the Consumer Cooperatives of the Central Standards Bureau of the Ministry of Economic Affairs, Γ 4193 90 B; 熹-1 1-1-- —— — _ _ Fifth, the invention description () has the same structure. Therefore, in the cleaning device 1 'shown in Fig. 5, the same components as those of the cleaning device 1 described earlier in Fig. 1 are assigned the same reference numerals, and detailed descriptions are omitted. The organic substances that cause the surface contamination of substrates in clean equipment such as semiconductor manufacturing are limited to organic substances that occur from sealants, phosphates that originate from non-flammable agents in building materials, and plasticizers that originate from building materials. High boiling point and high molecular organic compounds such as phthalates, HMDS generated from photoresist adhesives, and BHT that prevents oxidants from occurring. The sources of these organic substances are the constituent materials of clean devices such as clean rooms or various parts used for manufacturing inside the clean devices. Therefore, the role of the filter Η is mainly to remove the high boiling point and high molecular organic compounds that cause surface contamination inside the clean device from the circulating air, and reduce the concentration of these organic substances in the clean device. When a clean device with a filter 11 is in operation, the organic matter concentration in the clean device is highest in the initial stage of the operation. As the operating time elapses, these organic materials are removed one by one from the circulating air, and the concentration decreases. The concentration of the quantity is stabilized. Regarding the amount of organic matter removed once by air circulation, the cleaning device 1 of FIG. 1 installed on the entire ceiling and the cleaning device 1 ′ of FIG. 5 installed at intervals are compared, and there is a 2: 1 relationship. That is, the time from the highest concentration at the beginning of the operation to the balance between the amount of occurrence inside the clean device and the clean device 1 'shown in Fig. 5 installed at intervals is longer than the clean device 1 shown in Fig. 1 installed on the ceiling. a lot of. In addition, the equilibrium concentration finally reached is slightly higher in the case of interval installation than in the case of full ceiling installation. That is, it takes time to reduce the concentration when the installation is spaced. 19 — _ ^ -------- Q II (Please read the precautions on the back and fill in this 1).嗥 |. (-': ^) / \ 4 圯 格 (21〇 / 247 公 漦) Employees of the Central Bureau of Standards of the Ministry of Economic Affairs and Consumers Cooperative Cooperative Association Printing 419390 gi —. V. Description of the invention () Balance after reduction The density is also slightly higher than the case of full installation. However, due to the economic requirements of reducing the initial cost of the filter 11 or the operating costs associated with periodic replacement, as shown in the example of FIG. 5, the filters 11 are arranged at intervals. There are many cases. Next, a filter 100 according to the second embodiment of the present invention will be described with reference to FIG. 6. This filter 100 also has a structure substantially the same as that of the filter 11 just described in FIG. 2. However, in the filter 100 of the second embodiment, an organic substance having an effective pore diameter larger than the effective pore diameter of the zeolite is used as an adhesive in different points of the structure, and the powdered zeolite is fixed to the honeycomb structure 112. The surface of the whole. That is, the filter 100 of the second embodiment is structurally stacked in the inner space of the outer frames 115a, 115b, 115c, and 115d approximately parallel to the aeration direction 113. The inorganic substance is used as an adhesive to fix the powdery zeolite to Corrugated sheet 110 and thin sheet 111 on the surface. The shape or size of the filter 100 can be arbitrarily designed according to the installation space. Here, an example of a method of manufacturing the filter 100 will be described. The process until the honeycomb structure is formed is the same as above. As the honeycomb structure m after the removal of the organic matter component has pits of countless microns in size, a porous honeycomb structure 112 having the pits as holes can be manufactured. Later, fine particles of the adsorbent or the adhesive are embedded in the pit. Secondly, the honeycomb structure 112 is immersed in an inorganic substance, such as clay mineral, diatomaceous earth, which makes the powder of zeolite and has the property of adsorbing gaseous organic impurities and has an effective pore diameter larger than the effective pore diameter of the zeolite. , Alumina, alumina, a mixture of silica and alumina, aluminum silicate, activated alumina, porous glass and other dispersed suspensions after several minutes, pull up at 300 ° c, 1-20__ this Paper scale over-threshold ((.NsTa4 secret (2iOx 297 cm)) (Please read the precautions on the back before filling this page)
經濟部中央標準局員工消費合作杜印製 Ί: 419390 : r— — ~' ---1-- * ^ 五、發明説明() 小時之熱處理乾燥後,如圖7所示,使用無機物作爲黏接 劑使沸石之粉末固接在構成蜂巢構造物U2之波形片110 和薄板片111之表面而形成吸附層120 ’就可得到過濾器 100。該懸濁液至少含有無機系固接輔助劑,例如矽酸蘇 打或矽膠或氧化鋁溶膠之一也可。這些在剛才之實施例作 爲無機系溶膠黏接劑作用,但是在本實施例作爲牢固地接 合沸石和該無機物(黏接劑)之固接輔助劑作用’或作爲 用以將沸石之粉末和用作黏接劑之無機物牢固地固接在蜂 巢構造物112之表面(包含成爲蜂巢構造物112之元件之 單元之內表面(以下相同))之輔助劑作用。這樣得到之 過濾器1〇〇,因在構成材料上不含可燃物、完全脫離並除 去在將吸附層熱處理時構成材料所含成爲表面污染之原因 之氣體有機雜質成分,過濾器本身也不會發生氣體有機雜 質。 其次,說明過濾器100之其他製造方法。因到製造蜂 巢構造物Π2爲止和上述之製造方法例一樣’省略其說 明。本製造方法之特徵在於用黏接劑使由沸石之粉末造粒 而成之小球附著在蜂巢構造物112之表面。在將沸石之粉 末造粒時,將具有吸附氣體有機雜質之性質而且使用有效 細孔徑比該沸石之有效細孔徑大之無機物作爲沸石間之黏 接劑,和沸石之粉末混合。將沸石之粉末和用作黏接劑之 無機物以包含了適量之水和無機系固接輔助劑之狀態混 合,變成顯示黏土狀之黏性和可塑性,可造粒。用作黏接 劑之無機物或無機系固接輔助劑之種類和剛才說明之製造 {請先閱讀背面之注意事項再填苑本頁)Printed by the Central Department of Standards, Ministry of Economic Affairs, for consumer cooperation Du 印: 419390: r— — ~ '--- 1-- * ^ V. Description of the invention () After the heat treatment and drying for hours, as shown in Figure 7, inorganic substances are used as adhesives. The filter 100 is obtained by fixing the zeolite powder to the surface of the corrugated sheet 110 and the thin plate sheet 111 constituting the honeycomb structure U2 to form an adsorption layer 120 ′. This suspension may contain at least an inorganic fixing aid, such as one of silicate soda or silica gel or alumina sol. These are used as the inorganic sol adhesive in the previous example, but in this example, they are used as a fixing aid to firmly join the zeolite and the inorganic substance (adhesive) or as a powder and a zeolite. An inorganic substance used as an adhesive is an auxiliary agent that is firmly fixed to the surface of the honeycomb structure 112 (including the inner surface of the unit that becomes a component of the honeycomb structure 112 (the same applies hereinafter)). The filter 100 obtained in this way does not contain any combustible materials in the constituent materials, completely detaches them, and removes gaseous organic impurities that cause surface contamination contained in the constituent materials during the heat treatment of the adsorption layer. Gas organic impurities have occurred. Next, another manufacturing method of the filter 100 will be described. Since the honeycomb structure Π2 is manufactured, it is the same as the above-mentioned manufacturing method example 'and its explanation is omitted. This manufacturing method is characterized in that pellets made of zeolite powder are adhered to the surface of the honeycomb structure 112 with an adhesive. When granulating the powder of zeolite, an inorganic substance having the property of adsorbing gaseous organic impurities and having an effective pore diameter larger than the effective pore diameter of the zeolite is used as a binder between the zeolites and mixed with the zeolite powder. The powder of zeolite and the inorganic substance used as a binding agent are mixed in a state containing an appropriate amount of water and an inorganic-type fixing auxiliary agent, so as to show clay-like viscosity and plasticity, and can be granulated. Types of inorganic substances or inorganic fixing aids used as adhesives and the manufacturing just described {Please read the precautions on the back before filling in this page)
本紙張尺度適用中^1.¾家捸莩(('NS ) Λ4規格(210〆297公發) 經濟部中央標率局員工消资合作社印製 ^4193 90 ;;____ 五、發明説明(.) 方法一樣。 進一步說明過滬器100之另一製造方法。因到製造蜂 巢構造物112爲止和上述之製造方法例一樣,省略其說 明。本製造方法之特徵也在於用黏接劑使由沸石之粉末和 無機物之黏接劑混合後造粒而成之小球附著在蜂巢構造物 112之表面。但,無機物之黏接劑未必一定要如上述之製 造方法般「具有吸附氣體有機雜質之性質而且具有比該沸 石之有效細孔徑大之有效細孔徑」。和上述製造方法完全 不同之點係小球之表面構這。在小球之表面塗了具有吸附 -氣體有機雜質之性質而且具有有效細孔徑比該沸石之有效 細孔徑大之無機物。 , 圖δ係使用無機物作爲黏接劑使由沸石造粒而成之小 球121固接在構成蜂巢構造物112之波形片110及薄板片 111之表面而成之過濾器之模式剖面部分放大圖。使 用無機物作爲黏接劑,用不易燃性黏接劑將由沸石造粒而 成之小球121固接在波形片110和薄板片111之所有的表 面整體。此外’在不易燃性黏接劑上,可使用例如聚醯亞 胺系、聚醯胺亞胺系等耐熱性黏接劑等。所處理空氣在本 實施例通過剖面形狀成虛擬半月形之細筒部117。然後, 藉著像這樣固接了小球121之蜂巢構造物112放入電氣 :爐,在黏接劑之耐熱溫度以下之1〇〇 °c進行約2小時之熱 處理後,完全脫離並除去黏接劑所含成爲表面污染之原因 之氣體有機雜質成分,可製造過濾器100。 照這樣製造之過濾器1㈨,因構成材料不含可燃物, 22 {請先間讀背面之注$項再填tr本頁) fftn tit· ------訂 _---- \fy n^i In If —^ϋ* 本紙張尺度適川中®1¾家標卑(CNS ) Λ4坭格(2IOX 297公势) 經濟部中央標率局眞_t消費合作社印製 ii: 4193 90 a7 ' B7 五、發明説明() 將過濾器100裝在天花板面之情況,和將以係可燃物之活 性炭爲基底之習知之化學式過濾器裝在天花板面之情況相 比’在防災上之安全性上顯著提高。此外,使所處理空氣 通過之空間之剖面形狀未限定爲上述之半月形,可設爲任 何形狀。 在進行半導體基板或玻璃基板之製造之各種潔淨裝 置,例如無麈室、無塵操作台、無麈房間、用以保管潔淨 產品之各種Stocker等各種規模之潔淨裝置或稱爲迷你環 境之局部的潔淨裝置發生各種氣體有機雜質。可是,成爲 基板表面污染之原因的係高沸點•高分子有機化合物。例 如,自無塵室之密封劑發生之有機物矽氧烷、自建材中之 不易燃劑發生之磷酸酯、自建材中之可塑劑產生之鄰苯二 甲酸鹽、自光阻劑密接劑發生之HMDS、自盒之防止氧化 劑發生之BHT等。沸石,尤其稱爲分子篩之合成沸石具有 均勻的有效細孔徑,不能吸附比其有效細孔徑更大之氣體 分子。例如,用有效細孔徑爲δ埃之沸石可吸附成爲基板 表面污染之原因之D0P或DBP (因爲DOP或DBP之大 小小於8埃)。可是,用有效細孔徑爲8埃之沸石不能吸 附成爲基板表面污染之原因之ΒΗΤ或矽氧烷(因爲ΒΗΤ 或矽氧烷之大小大於8埃)。在本實施例2之過濾器1〇〇, 利用用作沸石之黏接劑之無機物之吸附作用可吸附並除去 上述用沸石不能吸附之ΒΗΤ或矽氧烷。 又,因在沸石結晶無自結合性,爲了使沸石之粉末成 形成小球或成層狀地固接在蜂巢構造物112之表面,必須 23 本紙張尺度適丨丨]中闹珣家標卒(C_NS ) Λ4規格(2I()〆 ) (請先閱讀背面之注意事項再填寫本頁)This paper is applicable to the standard of ^ 1. ¾ furniture (('NS) Λ4 specifications (210〆297)) Printed by the Consumers' Cooperative of the Central Standards Bureau of the Ministry of Economic Affairs ^ 4193 90; ) The method is the same. Another manufacturing method of the Shanghai device 100 is further explained. Since the honeycomb structure 112 is the same as the above manufacturing method example, the description is omitted. The manufacturing method is also characterized by the use of an adhesive to make zeolite. The pellets formed by mixing the powder and the inorganic adhesive are adhered to the surface of the honeycomb structure 112. However, the inorganic adhesive may not necessarily have the property of adsorbing gas and organic impurities as in the manufacturing method described above. And it has a larger effective pore diameter than the effective pore diameter of the zeolite. "The point that is completely different from the above-mentioned manufacturing method is the surface structure of the spheres. An inorganic substance having a larger pore diameter than the effective pore diameter of the zeolite. Fig. Δ shows the use of an inorganic substance as an adhesive to fix the pellet 121 made of zeolite to the honeycomb structure 112. An enlarged view of a pattern cross section of a filter formed on the surface of the corrugated sheet 110 and the thin plate sheet 111. An inorganic substance is used as an adhesive, and a non-flammable adhesive is used to fix the small balls 121 made of zeolite to the waveform. All the surfaces of the sheet 110 and the sheet 111 are integral. In addition, for non-flammable adhesives, heat-resistant adhesives such as polyimide-based and polyimide-based adhesives can be used. In this embodiment, the thin cylindrical portion 117 having a virtual half-moon cross-section is formed. Then, the honeycomb structure 112 to which the small balls 121 are fixed like this is put into an electric furnace, and the temperature is 1 ° below the heat-resistant temperature of the adhesive. 〇 ° C After about 2 hours of heat treatment, the gas organic impurities contained in the adhesive that cause surface contamination can be completely removed and removed, and the filter 100 can be manufactured. The filter manufactured in this way is 1㈨, because the constituent materials do not contain Combustible materials, 22 (please read the note on the back and fill in the tr page) fftn tit · ------ order _---- \ fy n ^ i In If — ^ ϋ Chuanzhong® 1¾ Family Standard (CNS) Λ4 坭 Grid (2IOX 297 public power) Central Ministry of Economic Affairs Printed by the Bureau_t Consumer Cooperative ii: 4193 90 a7 'B7 V. Description of the invention () When the filter 100 is installed on the ceiling, and the conventional chemical filter based on combustible activated carbon is installed on the The condition of the ceiling surface is significantly improved in terms of safety in disaster prevention. The cross-sectional shape of the space through which the treated air passes is not limited to the half-moon shape described above, and any shape may be used. Various cleaning devices for semiconductor substrate or glass substrate manufacturing, such as clean rooms, dust-free operating tables, clean rooms, various stockers used to store clean products, etc. Various organic impurities are generated in the cleaning device. However, high-boiling-point, high-molecular-weight organic compounds are the cause of substrate surface contamination. For example, organic siloxanes generated from sealants in clean rooms, phosphate esters generated from non-flammable agents in building materials, phthalates generated from plasticizers in building materials, and photoresist adhesives. HMDS, self-boxed BHT to prevent the occurrence of oxidants, etc. Zeolites, especially synthetic zeolites called molecular sieves, have a uniform effective pore size and cannot adsorb gas molecules larger than their effective pore size. For example, using a zeolite with an effective pore size of δ angstroms can adsorb DOP or DBP (because the size of DOP or DBP is less than 8 angstroms) that causes the surface contamination of the substrate. However, zeolite with an effective pore size of 8 angstroms cannot adsorb BHT or siloxane, which is the cause of contamination of the substrate surface (because the size of BHT or siloxane is greater than 8 angstroms). In the filter 100 of this Example 2, the above-mentioned BHT or siloxane which cannot be adsorbed by the zeolite can be adsorbed and removed by the adsorption of an inorganic substance used as a binder of the zeolite. In addition, since there is no self-binding property in zeolite crystals, in order to form the zeolite powder into small balls or to be fixed in layers on the surface of the honeycomb structure 112, it is necessary to set the standard of 23 papers. (C_NS) Λ4 specification (2I () 〆) (Please read the precautions on the back before filling this page)
Α7 Β7 t?; Α193 90 五、發明説明() 添加黏接劑。以前這種黏接劑一般利用如滑石、膨潤土般 之黏土礦物。這些以前之各種黏接劑之分布在15〜300埃之 範圍之細孔之總容積(各黏接劑之每單位重量)各自係 .0.07cc/g、0,06cc/g、0.03cc/g,反黏接劑之細孔之比表面 積各自不超過 28m2/g、21m2/g、23m2/g。 以前就一直在使用之這些黏接劑重視透氣性,在相鄰 之黏接劑微粒子間或相鄰之黏接劑微粒子和沸石微粒子之 間隙部分形成之透氣孔之主要大小係5〇〇埃以上。即,透 氣孔係透氣性極佳也不易發生物理吸附之大孔。又,在滑 石、高嶺土、膨潤土等黏接劑微粒子本身之表面也不太存 在易發生物理吸附之細孔。這是由於認爲黏接劑應只是用 以將沸石之粉末機械式地載持在支撐物表面’爲了提高吸 附性能,最好儘量增多沸石之載持量’相對於黏接劑之沸 石之含有比例要儘量少。即,對黏接劑要求沸石之粉末之 載持性能和處理對象氣體易到達所載持沸石之粉末之表面 之優異的透氣性能,而未要求吸附性能。 而,本實施例之過濾器100 ’在相鄰之黏接劑微粒子 間或相鄰之黏接劑微粒子和沸石微粒子之間隙部分形成之 透氣孔和以前之黏接劑一樣’但是因在黏接劑微粒子本身 之表面存在易發生物理吸附之細孔,即係孔徑大小20埃以 內之細孔之微小孔,或係孔徑大小20埃以上500埃以內之 細孔之中等孔’用黏接劑微粒子本身之表面吸附並除去用 沸石無法吸附之BHT或矽氧烷。而且因也具有處理對象氣 體易到達沸石之粉末表面之優異的透氣性能’和以前一樣 24 本紙張尺度通川中阀囤家棉肀(CNS ) 格(2〖(ΐχ2Μ公冰) -------f (請先閱讀背面之注意事項再填寫本頁) ,-° 經濟部中央標率局員工消費合作社印裝 經濟部中央襟嗥局員工消费合作社印製 4193 90 五、發明説明() 地發揮沸石之選擇性吸附特性,即不吸附比沸石之細孔徑 大之分子而吸附比沸石之細孔徑小之分子且其吸附性能也 極優異之特性。此外,氣體狀分子之物理吸附之容易性之 順序係微小孔、中等孔、大孔,而大孔和物理吸附幾乎無 關。圖9係對於在本發明之用無機物之黏接劑微粒子將沸 石之粉末載持在支撐物之表面之吸附層所示吸附層剖面之 模式部分放大圖。所處理對象氣體如自吸附層之表面(和 所處理對象氣體之接觸面)鑽進在沸石微粒子和黏接劑微 粒子之間形成之透氣孔般進入吸附層內部或相反地自吸附 層內部出去外部。那時,氣體有機雜質之分子進入位於沸 石微粒子和黏接劑微粒子之各自之表面之細孔而被吸附並 除去。 爲了達成本發明之目的,使用具有比沸石之有效細孔 徑大之主要爲中等孔區域或微小孔區域之細孔之無機物作 爲黏接劑,使沸石之粉末固接在蜂巢構造物112,作爲吸 附層120,構成過濾器100,或者利用一樣之該無機物之 黏接劑將沸石之粉末成形成小球121後,使該小球121固 接在蜂巢構造物112之表面,構成過濾器100。又,在圖 10如A-A剖面、B-B剖面所示,藉著具有比沸石之有效 細孔徑大之主要爲中等孔區域或微小孔區域之細孔之無機 物之黏接劑,將沸石之粉末成形成小球121後,將該小球 121充塡到在側面具有多個透氣口 123之雙重圓筒形之外 殼122內,構成過濾器100',也可達成本發明之目的。所 處理空氣自外殼122之內側圓筒流入,穿過外殼122內之 25 本纸浓尺度適叫中闽1¾家標準(('NS ) Λ4覘格(2丨0,,297公始) (請先聞讀背面之注意事項再填寫本頁)Α7 Β7 t ?; Α193 90 V. Description of the invention () Add adhesive. In the past, such adhesives generally used clay minerals such as talc and bentonite. The total volume of pores (per unit weight of each adhesive) of these previous various adhesives distributed in the range of 15 to 300 Angstroms are each 0.07cc / g, 0,06cc / g, 0.03cc / g. The specific surface area of the pores of the anti-adhesive agent should not exceed 28m2 / g, 21m2 / g, 23m2 / g, respectively. These adhesives that have been used before attach importance to air permeability. The main size of the air pores formed between adjacent adhesive particles or the gap between adjacent adhesive particles and zeolite particles is more than 500 angstroms. . That is, the air pores are large pores which are excellent in air permeability and are not prone to physical adsorption. In addition, pores that are prone to physical adsorption do not exist on the surface of adhesive particles such as talc, kaolin and bentonite. This is because it is believed that the adhesive should only be used to mechanically support the zeolite powder on the surface of the support. 'In order to improve the adsorption performance, it is best to increase the amount of zeolite supported' relative to the zeolite content of the adhesive. Keep the proportion as small as possible. That is, the adhesive requires the support performance of the zeolite powder and the excellent gas permeability of the processing target gas to easily reach the surface of the supported zeolite powder, but no adsorption performance is required. However, the filter 100 of this embodiment has the same ventilation holes formed between the adjacent adhesive particles or the gap between the adjacent adhesive particles and the zeolite particles as the previous adhesives, but because of the adhesion There are pores that are prone to physical adsorption on the surface of the particle of the agent itself, that is, small pores with a pore size of less than 20 angstroms, or isopores among pores with a pore size of 20 angstroms and 500 angstroms. The surface itself adsorbs and removes BHT or siloxane that cannot be adsorbed with zeolite. And because it also has the excellent breathability of the target gas easily reach the surface of the zeolite powder, it is the same as before. The paper size of the paper is 24. (CNS). (2 〖(ΐχ2Μ 公 冰) ----- --f (Please read the notes on the back before filling out this page),-° Printed by the Consumer Standards Cooperative of the Central Standards Bureau of the Ministry of Economic Affairs 4193 90 Utilizing the selective adsorption characteristics of zeolite, that is, it does not adsorb molecules larger than the pore size of zeolite, and adsorbs molecules smaller than the pore size of zeolite, and has excellent adsorption performance. In addition, the ease of physical adsorption of gaseous molecules The order is micropores, medium pores, and macropores, and the macropores are almost independent of physical adsorption. Figure 9 shows an adsorption layer for supporting zeolite powder on the surface of a support by using inorganic binder particles in the present invention. An enlarged view of the pattern of the section of the adsorption layer shown. The gas to be treated, such as the surface of the adsorption layer (and the contact surface of the gas to be treated), is drilled into the zeolite particles and the adhesive The air pores formed between the particles enter the inside of the adsorption layer or go out of the inside of the adsorption layer on the contrary. At that time, molecules of gaseous organic impurities enter the pores on the respective surfaces of the zeolite particles and the adhesive particles to be adsorbed and In order to achieve the purpose of the present invention, an inorganic substance having pores which are larger than the effective pore diameter of zeolite, mainly medium pore area or micro pore area, is used as an adhesive, so that the zeolite powder is fixed to the honeycomb structure 112, As the adsorption layer 120, the filter 100 is formed, or the same zeolite powder is used to form a small ball 121 by using the same inorganic adhesive, and the small ball 121 is fixed on the surface of the honeycomb structure 112 to constitute the filter 100. In addition, as shown in the AA section and the BB section in FIG. 10, the powder of zeolite is made of an adhesive having inorganic pores which are larger than the effective pore diameter of the zeolite, mainly medium pore regions or micro pore regions. After the small ball 121 is formed, the small ball 121 is filled into a double-cylindrical housing 122 having a plurality of air vents 123 on the side to form a filter 100 '. Purpose of the invention. The processed air flows in from the inner cylinder of the shell 122 and passes through the 25 paper thick scales in the shell 122. The standard is called Zhongmin 1¾ standard (('NS) Λ4 觇 Grid (2 丨 0,, 297) Start) (Please read the notes on the back before filling in this page)
ί 4 193 90 五、發明説明() 小球121之充塡層後,通過外殼122之外側圓筒和外筒124 所夾住之空間出去。所處理空氣之流通方向用箭頭113表 示。 例如,將大小爲數μιη之粉末狀之細孔徑8埃之合成沸 石和數μπι之粉末狀之酸處理蒙脫石之黏接劑混合後固接 在蜂巢構造物112之表面,或將該混合物成形成小球121 後,固接在蜂巢構造物112之表面,或充塡到外殻內,就 可製造本發明之過濾器100或1〇〇〜此外,蒙脫石 (montmorillonite)係出產於法國之Montmorillon之化學成分 爲Al4Si8 ( OH ) 4·ηΗ20之黏土礦物之命名,將蒙脫石酸 處理後,變成細孔徑爲15〜300埃之細孔容積約0.37cc/g、 比表面積約300m2/g。細孔徑爲40~600埃之範圍之細孔容 積佔細孔容積整體之約22%,藉著將酸處理蒙脫石用作細 孔徑爲8埃之合成沸石之黏接劑,可將用沸石無法吸附之 分子大小大於8埃BHT或矽氧烷物理吸附在該黏接劑之細 孔內。 經濟部中央標率局負工消费合作社印製 (請先閲讀背面之注意事項再填寫本頁) 以前就一直用作粉末狀沸石之黏接劑的滑石(talc)、高 嶙石(kaolinite)、膨潤土(bentonite),大孔區域之容積大,但 .是微小孔區域或中等孔區域之內部表面積或容積小,物理 吸附性能也小。而,纖維狀之係多孔性黏土礦物之海泡石 之細孔由10埃之微小孔和200埃之中等孔構成,微小孔區 域或中等孔區域之內部表面積或容積大,物理吸附性能也 .大。酸處理蒙脫石(活性黏土)、合成富鎂蒙脫石 (stevensite)、合成鎂綠泥石、合成絲鋅鋁石(fraipontite)、或 26 本紙诙尺度適用中因闽家抒卒(rNS ) A4規格(2Κ)Χ29Τ公釐,) 經濟部中央標準局員工消費合作杜印製 Λ7 B7 五、發明説明() 諸如合成絲鋅鋁石般之矽酸鋁鹽金屬鹽之微結晶及氧化矽 微粒子的複合物等多孔性黏土礦物也和海泡石一樣,物理 吸附性能大。這些多孔性黏土礦物都是分布在15埃〜300 +埃之範圍之每單位重量之細孔容積係〇.2cc/g以上,而且比 表面積係l〇〇m2/g以上。係纖維狀多孔性黏土礦物之海泡 石或坡縷石、酸處理蒙脫石(活性黏土)、多孔性之各種合成 黏土等如後述所示,也可適合用作本發明之第2吸附層。 在此,在潔淨裝置內由基板表面所偵測之有機污染物 之中量最多的種類係DOP和DBP。這些在氯化乙烯材料 中含有大量,其分子徑位於6埃〜8埃之範圍。因,此若將 沸石之細孔徑設爲7埃以上,用沸石可除去成爲基板表面 污染之原因之氣體有機物之中量最多的種類DOP和 DBP。而,藉著在該沸石之黏接劑使用有效細孔徑比該分 子徑比沸石之有效細孔徑大之無機物,除去有效細孔徑比 該分子徑比該沸石之有效細孔徑大之氣體有機雜質。 又,對於沸石結晶之水或極性物質之吸附力強度和與 骨格中之鋁原子數對應之陽離子之靜電力相依。隨著結晶 中之二氧化矽(Si02)和氧化鋁(A1203 )之含有重量比 .Si02/Al203變大,結晶中之陽離子數減少,疏水性增大。在 Si02/Ai203約2〜5表示親水性,而在Si02/Al203 20以上到 無限大爲止之沸石親水性減少,疏水性就超過。 圖11係表示含有重量比Si02/Al203和每100g沸石之 水分吸附量(cc/100g )之關係圖。在SiCVAl2〇32〇以上’ 水分吸附量降低,在80以上幾乎不吸附。此外,對於 27 i 4193 90 —I--------d衣— (請先閱讀背面之注意事項再填寫本頁) 訂1ί 4 193 90 V. Description of the invention () After the filling layer of the small ball 121, go out through the space sandwiched by the outer cylinder 124 and the outer cylinder 124. The flow direction of the treated air is indicated by arrow 113. For example, a powdery synthetic zeolite having a pore size of 8 angstroms and a powdery acid-treated montmorillonite adhesive having a size of several μm are mixed and fixed on the surface of the honeycomb structure 112, or the mixture is mixed. After forming the small ball 121, it can be fixed on the surface of the honeycomb structure 112 or filled into the shell, and the filter 100 or 100 of the present invention can be manufactured. In addition, montmorillonite is produced in The chemical composition of Montmorillon in France is named as the clay mineral of Al4Si8 (OH) 4 · ηΗ20. After montmorillonite acid treatment, the pore volume is about 0.37cc / g, and the specific surface area is about 300m2. / g. The pore volume in the range of 40 to 600 angstroms accounts for about 22% of the total pore volume. By using acid-treated montmorillonite as an adhesive for synthetic zeolite with a pore diameter of 8 angstroms, zeolite can be used. The size of the molecules that cannot be adsorbed is greater than 8 angstroms. BHT or siloxane is physically adsorbed in the pores of the adhesive. Printed by the Central Standards Bureau of the Ministry of Economic Affairs, Consumer Cooperatives (please read the precautions on the back, and then fill out this page). Talc, kaolinite, kaolinite, Bentonite has a large pore area but a small or medium pore area with a small internal surface area or volume and a small physical adsorption performance. In addition, the fibrous porous clay mineral sepiolite pores are composed of 10 angstrom pores and 200 angstrom middle pores. The internal surface area or volume of the small pore area or medium pore area is large, and the physical adsorption performance is also good. Big. Acid-treated montmorillonite (active clay), synthetic magnesium-rich montmorillonite (stevensite), synthetic magnesite, synthetic fraipontite (fraipontite), or 26 paper scales suitable for use by the Fujian family (rNS) A4 size (2K) × 29T mm,) Consumption cooperation by employees of the Central Standards Bureau of the Ministry of Economic Affairs, Du printed Λ7 B7 V. Description of the invention () Microcrystalline crystals such as synthetic aluminosilicate metal salts and fine silica particles Porous clay minerals, such as composites, have the same physical adsorption properties as sepiolite. These porous clay minerals have a pore volume per unit weight of 0.2 cc / g or more, and a specific surface area of 100 m2 / g or more, distributed in a range of 15 angstroms to 300 angstroms. The sepiolite or palygorskite, which is a fibrous porous clay mineral, acid-treated montmorillonite (active clay), and various synthetic clays are also suitable for use as the second adsorption layer of the present invention as described below. . Here, DOP and DBP are the most abundant types of organic contaminants detected from the surface of the substrate in the clean device. These are contained in a large amount in the vinyl chloride material, and their molecular diameters range from 6 to 8 angstroms. Therefore, if the pore size of the zeolite is set to 7 angstroms or more, DOP and DBP, which are the most abundant types of gaseous organic substances that cause the surface contamination of the substrate, can be removed with zeolite. In addition, by using an inorganic substance having an effective pore diameter larger than the effective pore diameter of the zeolite in the adhesive of the zeolite, gaseous organic impurities having an effective pore diameter larger than the molecular diameter of the zeolite are removed. In addition, the strength of the adsorption force to the water or polar material of the zeolite crystal depends on the electrostatic force of the cations corresponding to the number of aluminum atoms in the bone. As the content ratio of silicon dioxide (Si02) and aluminum oxide (A1203) in the crystal becomes larger, the number of cations in the crystal decreases and the hydrophobicity increases. In Si02 / Ai203, about 2 to 5 indicate hydrophilicity, while in Si02 / Al203 above 20 to infinity, the zeolite's hydrophilicity decreases and the hydrophobicity exceeds. Fig. 11 is a graph showing the relationship between the content of Si02 / Al203 and the amount of water adsorbed (cc / 100g) per 100 g of zeolite. The amount of water absorption decreases when SiVCAl2300 + is exceeded, and it is hardly adsorbed above 80V. In addition, for 27 i 4193 90 —I -------- d clothing — (Please read the precautions on the back before filling this page) Order 1
D 本紙張尺度適.丨ίΗ7闽阄家標卑(C'NS ) Λ4規格(21〇_χ·:^7公婼) 經濟部中央標準局貝工消費合作社印製 A7 A 19-0__ίίΖ__—__ 五、發明説明()D This paper is of appropriate size. 丨 Η7 Min's Family Standards (C'NS) Λ4 specification (21〇_χ ·: ^ 7 婼) Printed by the Shell Worker Consumer Cooperative of the Central Standards Bureau of the Ministry of Economic Affairs A7 A 19-0__ίίZZ ______ V. Description of the invention ()
SiO2/Al2O340之疏水性沸石,水之吸附等溫線圖如圖12所 示。在相對濕度50% ’活性炭之水分吸附量(cc ).爲0.11 (cc/g ),疏水性沸石(g )之水分吸附量(cc )爲0.03 (cc/g )。沸石吸附水後,沸石之對於氣體有機物之吸附 容量,和無吸附水之情況相比,因減少了吸附水之容積, 吸附性能之持續時間,即作爲吸附劑之壽命也隨之減少。 即,在一般相對濕度30〜60%之潔淨裝置內,用以吸附並除 去氣體有機物之沸石最好係疏水性。 而,在本發明也可使用親水性沸石。在無麈室或無麈 操作台之空氣環境中搬運之矽晶片雖有一些差異,都在表 面形成自然氧化膜,因此其晶片表面係親水性。又,在該 空氣環境中搬運之玻璃基板也由於玻璃本身之物性而係親 水性,這是周知的。這種來自污染形成了自然氧化膜之矽 晶片或玻璃基板之親水性表面之空氣環境之有機物具有和 親水性表面充分溶合之親水基。即,剛才說明之成爲表面 污染之原因之有機物係具有炭元素之雙重結合或笨環之化 學構造之高沸點•高分子之疏水性有機物,當然具有疏水 基。可是,這些有機物也同時具有成爲表面污染之原因之 .親水基。於是,因矽晶片等電子材料係親水性,又應吸附 之有機物具有親水基,變成也可利用親水性沸石。 在親水性沸石,Si02/Al203比係約2〜5,而在疏水性 沸石,_ Si02/Al203比係由20到無限大。疏水性沸石作爲吸 附材料之壽命比親水性沸石的長,但是因疏水性沸石係以 親水性沸石爲原料,經利用酸處理之脫鋁處理和後面之加 28 .............. I - .- I- -I I -— 1^1 ^^^1 ^1 (請先閱讀背面之注意事項再填寫本頁) 訂 ο 本紙張尺度適Θ屮囚丨^家揉半(),\4規格(2!0>297公总) 經湳部中夾標準局負工消资合作社印裝 、A193 90 at ...________ B7 五、發明説明() 熱乾燥之製程而製成,價格比親水性沸石貴。親水性沸石 利用量產易降低價格,而疏水性沸石不易降低價格。 又,將沸石和具有吸附氣體有機雜質之性質而且具有 比該沸石之有效細孔徑大之中等孔區域或微小孔區域之有 效細孔徑之無機物作爲黏接劑,在預備用以將由該沸石之 粉末造粒而成之小球固接在支撐物之狀態下,例如將水與 該沸石和該無機物兩者之粉末混合,變成黏土狀,用造粒 機造粒成約0.3〜0.8mm之小球。藉著利用高速空氣將其吹 到預先附著了無機系或不燃性黏接劑之支撐物,可製造如 圖δ所示之本發明之過濾器。支撐物未必限定爲蜂巢構造 物,可列舉石綿等三次元網目構造。在後者,因所處理空 氣橫穿網目構造物,空氣阻力大,但是和吸附劑之接觸機 會反而比蜂巢構造物多。 其次,圖13係本發明之實施例2之其他過濾器131之 槪略的分解組立圖。此外,在該過濾器131,因小球121 本身之構造和剛才在圖6所說明之過濾器100之構造相 同,藉著對於相同之構成元件在圖13賦與和圖6相同之符 號,省略其說明。 該過濾器131在構造上,如圖14所示,堆積了波形片 110和薄板片1Π之蜂巢構造物1Π之表面,使用具有吸 氣體有機雜質之性質而且具有比該沸石之有效細孔徑大 之有效細孔徑之無機物作爲黏接劑,使沸石固接,形成第1 吸附層125,再在其表面使同樣的無機物固接後形成了第2 吸附層Π6。此外,過濾器131之外形或尺寸等可配合設 29 (請先閱讀背面之注意事項再填寫本頁} 訂* 本紙張尺度適州中1¾¾家樣卑() Λ4规格(2丨().<297公超) / ^ 1 - I ........... .. . 經濟部中央標率局員工消費合作办印製 ί 4193 90___βτ_________ 五、發明説明() 置空間任意地設計。但,在形成第1吸附層125時用作黏 接劑之無機物和在形成第2吸附層126時使用之無機物不 同,未必需要吸附氣體有機雜質之性能。又’具有比沸石 之有效細孔徑小之有效細孔徑的也可。例如係以前一直在 用之幾乎沒有參與物理吸附之細孔之如滑石、高嶺土'膨 潤土般之黏土礦物也可。又’係如砂酸蘇打、砂膠、氧化 鋁溶膠般之無機系固接輔助劑的也可。圖15係在本發明之 由第1吸附層和第2吸附層構成之複合吸附層剖面之模式 部分放大圖。 在此,說明過濾器131之製造方法之一例。首先,製 造多孔性蜂巢構造物112。到形成吸附層爲止和剛才說明 ’ 之方法一樣,省略其說明。其次,將蜂巢構造物Η 2浸在 使沸石之粉末和以前一直用作黏接劑之如滑石、高嶺土、 膨潤土般之黏土礦物之粉末微粒子分散之懸濁液中數分鐘 後,以約300 °C、1小時之熱處理乾燥後’形成第1吸附 層125。接著,將形成了第1吸附層後之蜂巢構造物112 浸在具有比沸石之有效細孔徑大之有效細孔徑而且具有吸 附氣體有機雜質之性質之無機物,例如多孔性黏土礦物、 矽藻土、二氧化矽、氧化鋁、二氧化矽和氧化鋁之混合物、 矽酸鋁、活性氧化鋁、多孔質玻璃等之微粒子作爲黏接劑 -並令分散之懸濁液中數分鐘後,以300 °C、1小時之熱處 理乾燥,形成第2吸附層120 〇在該多孔性黏土礦物上, 有海泡石或坡縷石等緞帶狀構造之含水矽酸鎂質黏土礦 物、活性黏土、酸性黏土、活性膨潤土、矽酸銘金屬鹽之 30 (請先聞讀背面之注意事項再填寫本頁〕 hx 丁 - ,-° 本紙張尺度適州中國1¾家栉準(CNS ) Λ4規格(2丨0 XM7公犮〉 經濟部中央標準局員工消費合作社印製 Γ 419390 五、發明説明() 微結晶和二氧化砍微粒子之複合物等。照這樣可得到在第1 吸附層125上塗了第2吸附層126之蜂巢構造物112。在 形成第1吸附層125和第2吸附層126時使用之無機物至 少含有無機系固接輔助劑,例如矽酸蘇打或矽膠或氧化鋁 溶膠之一也可。無機系固接輔助劑之功用係作爲使形成第1 吸附層125之沸石之粉末或無機物之黏接劑牢固地固接在 蜂巢構造物112之孔等之輔助劑,還作爲使形成第2吸附 層126之無機物牢固地固接在第1吸附層125之輔助劑。 照這樣得到之蜂巢構造物,因在構成材料上不含可燃 物、完全脫離並除去在將吸附層熱處理時構成材料所含成 爲表面污染之原因之氣體有機雜質成分,蜂巢構造物112 本身也不會發生氣體有機雜質。此外’在圖13所示外框 115之材料最好使用不會產生如鋁般之氣體有機物且不含 可燃物之材料。又,爲了將蜂巢構造物112固定在外框115 或塞住蜂巢構造物112和外框115之間隙部分之黏接劑或 密封劑最好也是不會產生氣體有機物且不含可燃物之特性 的。此時,也可例如對在蜂巢構造物112安裝外框115而 完成組立之過濾器131整體進行熱處理,完全脫離並除去 來自過濾器131之構成材料之不易燃性黏接劑或密封劑之 成爲表面污染之原因之氣體有機雜質成分。於是,可只用 不含可燃物之材料或不會產生氣體有機物之材料構成過濾 器131整體。 此外,在本發明令沸石等之吸附劑固接之支擦物之構 造當然不限剛才在圖6或圖13等所說明之蜂巢構造物 31 本紙張尺度適用中国囚家標莩((.'NS ) Λ4.«1格(川ΓχπΊίί:) 1!-----—f {請先閱讀背面之注^一^項再填寫本頁) 訂·· 經濟部中央標準局負工消費合作枉印製 W 4Ϊ9390 ___ :; 五、發明説明() 112。例如,在圖6、圖13,將以夾住薄板片ill配置之 波形片110之稜線之方向配置成和所處理空氣之流通方向 _ (箭頭Π3之方向)平行,但是也可將波形片110之稜線 之方向配置成和所處理空氣之流通方向(箭頭113之方向) 具有適當的夾角。又,在圖6、圖13,將相鄰波形片110 之稜線之方向配置成彼此平行,但是將相鄰波形片11〇之 稜線之方向配置成彼此交叉也可。那時,因相鄰波形片110 間之稜線相碰,就不會擔心相鄰波形片110間密接’也可 省略薄板片ill。此外,·像這樣在構成和在圖6、圖13所 說明之蜂巢構造物112不同之支撐物之情況,利用和剛才 相同的方法也可在其表面固接沸石。 又,說明按照本發明之另一過濾器之製造方法。利用 用上述之製造方法所製造之石綿或陶磁之成形品之三次元 網目構造物作爲支撐物。而且在此製造方法例’用黏接齊® 使粒狀沸石附著在支撐物之表面。關於粒狀沸石,將無機 物作爲黏接劑和沸石之粉末混合後成形成球形。在該小球 之周圍,預備塗了具有比該沸石之有效細孔徑大之有效細 孔徑而且具有吸附氣體有機雜質之性質之無機物而形成了 被覆層之附被覆層之沸石小球。該小球之製造方法也可’ 爲了形成無機物之被覆層,將成形成球形之沸石浸在分散 了塗膜用之無機物之懸濁液後’拉起、乾燥。爲了增加被 覆層之強度,在該懸濁液使溶膠狀之無機系固接輔助劑和 塗膜用之無機物一起分散,使得在小球所塗之無機物含有 無機系固接輔助劑。塗膜用之無機物或無機系固接輔助劑 32 (請先閲讀背面之注意事項再填寫本頁) — —訂·——,----0---- 本紙張尺度遇用t闽因家揉隼(C'NS ) /\4说格(2i«〆 Μ7'公疫) i 、. 經濟部中央標準局員工消f合作社印聚 t 419390 at __B7___ 五、發明説明() 之種類如上述所示。 藉著利用高壓氣流將照這樣所造粒之小球吹在令預先 含浸無機系黏接劑之三次元網目構造上,可製造按照本發 明之過濾器。 圖16係槪略表示之本發明之實施例2之潔淨裝置201 之構造之說明圖。該潔淨裝置201基本上具有和剛才在圖1 所說明之潔淨裝置1相同之構造。即,由用以製造例如LSI 或LCD等之處理空間202、位於該處理空間202之上下之 天花板部203和地板下面部204、以及位於處理空間202 .之側方之回氣通路205構成。在天花板部203配置風扇單 元210及具有剛才說明之過濾器100或過濾器131之其中 之一和除去粒狀雜質之過濾器212之潔淨風扇單元2Π 〇 在處理空間202設置成爲熱產生源之例如半導體製造裝置 214。在用多孔板215隔開之地板下面部204設置處理半 導體製造裝置214之熱負載之無結露盤管210。控制無結 露盤管16之冷水流量調整閥18,使得設於回氣通路205 之溫度感測器217所偵測到之溫度變成指定之設定値,而 且在盤管不結露下保持固定之濕度。而且,藉著風扇單元 210運轉,在調整適當的氣流速度下,潔淨裝置201內部 之空氣按照天花板部203—處理空間202〇地板下面部 汾4->回氣通路205->天花板部203之順序流動循環。又, 在該循環中,被無結露盤管216冷卻’利用潔淨風扇單元 213內之過濾器1〇〇或過濾器Π1之其中之一和除去粒子 之過濾器212除去空氣中之氣體有機雜質和粒子狀雜質。 (請先閱讀背面之注意事項再填寫本頁) ------------訂·--*---The adsorption isotherm diagram of SiO2 / Al2O340 hydrophobic zeolite and water is shown in Figure 12. At a relative humidity of 50%, activated carbon has a water adsorption amount (cc) of 0.11 (cc / g), and a hydrophobic zeolite (g) has a water adsorption amount (cc) of 0.03 (cc / g). After zeolite adsorbs water, the adsorption capacity of zeolite for gaseous organics is reduced compared with the case without adsorbed water, because the volume of adsorbed water is reduced, and the duration of the adsorption performance, that is, the life of the adsorbent is also reduced. That is, in a clean device with a general relative humidity of 30 to 60%, the zeolite used to adsorb and remove gaseous organic matter is preferably hydrophobic. However, a hydrophilic zeolite can also be used in the present invention. Although there are some differences in the silicon wafers that are transported in the air environment of a clean room or a clean operation table, the natural oxide film is formed on the surface, so the surface of the wafer is hydrophilic. It is also known that glass substrates transported in this air environment are hydrophilic due to the physical properties of the glass itself. This organic substance from the air environment that contaminates the hydrophilic surface of a silicon wafer or glass substrate on which a natural oxide film is formed has a hydrophilic group that is sufficiently fused to the hydrophilic surface. That is, the organic substance that has just been explained as the cause of surface contamination is a high boiling point and high molecular weight hydrophobic organic substance with a chemical structure of a double combination of carbon elements or a clumsy ring, of course, having a hydrophobic group. However, these organic substances also have a hydrophilic group that causes surface contamination. Therefore, since electronic materials such as silicon wafers are hydrophilic, the organic substances to be adsorbed have hydrophilic groups, and hydrophilic zeolites can be used. In hydrophilic zeolite, the ratio of Si02 / Al203 is about 2 ~ 5, while in hydrophobic zeolite, the ratio of SiO2 / Al203 is from 20 to infinity. The lifetime of hydrophobic zeolite as an adsorbent is longer than that of hydrophilic zeolite, but because hydrophobic zeolite uses hydrophilic zeolite as the raw material, it is treated by acid treatment with dealumination and plus 28 ... ..... I-.- I- -II -— 1 ^ 1 ^^^ 1 ^ 1 (Please read the precautions on the back before filling in this page) Order ο The paper size is suitable Half (), \ 4 specifications (2! 0 > 297 total) Printed by the Ministry of Standards and Technology Bureau of the Ministry of Work and Consumer Cooperatives, A193 90 at ...________ B7 V. Description of the invention () Thermal drying process and Made, the price is more expensive than hydrophilic zeolite. The production of hydrophilic zeolite is easy to reduce the price, but the price of hydrophobic zeolite is not easy to reduce. In addition, a zeolite and an inorganic substance having the property of adsorbing gaseous organic impurities and having an effective pore diameter larger than the effective pore diameter of the zeolite, or an effective pore diameter of a small pore region, are used as a binder to prepare a powder of the zeolite The granulated pellets are fixed on a support, for example, water is mixed with the powder of the zeolite and the inorganic substance to become clay, and granulated by a granulator into pellets of about 0.3 to 0.8 mm. The filter of the present invention as shown in Fig. Δ can be manufactured by blowing it to a support to which an inorganic or non-combustible adhesive is attached in advance by using high-speed air. The support is not necessarily limited to a honeycomb structure, and may include a three-dimensional mesh structure such as asbestos. In the latter case, because the treated air traverses the mesh structure, the air resistance is large, but the contact with the adsorbent is more than that of the honeycomb structure. Next, Fig. 13 is a schematic exploded assembly diagram of another filter 131 according to the second embodiment of the present invention. In addition, in this filter 131, since the structure of the small ball 121 itself is the same as that of the filter 100 just described in FIG. 6, the same constituent elements as in FIG. 13 are given the same symbols as in FIG. 6, and are omitted. Its description. The filter 131 is structurally, as shown in FIG. 14, the surface of the honeycomb structure 1Π on which the corrugated sheet 110 and the thin sheet sheet 1Π are stacked. An inorganic substance having an effective pore diameter is used as an adhesive to fix the zeolite to form a first adsorption layer 125, and then a second adsorption layer Π6 is formed by fixing the same inorganic substance on the surface. In addition, the shape or size of the filter 131 can be matched with the setting 29 (Please read the precautions on the back before filling out this page} Order * This paper size is suitable for 1¾¾ in the state () Λ4 specifications (2 丨 (). ≪ 297 Public Super League) / ^ 1-I ........... .... Printed by the Employees' Co-operation Office of the Central Bureau of Standards of the Ministry of Economic Affairs 4193 90 ___ βτ _________ 5. Description of the invention () Arbitrary design of the space However, the inorganic substance used as an adhesive when the first adsorption layer 125 is formed is different from the inorganic substance used when the second adsorption layer 126 is formed, and the performance of adsorbing gaseous organic impurities is not necessarily required. Small effective pores are also possible. For example, clay minerals such as talc, kaolin and bentonite, which have been used in the past and have little pores that participate in physical adsorption, can also be used. It is also possible to use an inorganic sol-like inorganic fixing adjuvant. Fig. 15 is an enlarged view of a schematic partial pattern of a composite adsorption layer composed of a first adsorption layer and a second adsorption layer according to the present invention. Here, the filter 131 will be described. An example of a manufacturing method. First, The porous honeycomb structure 112 is manufactured. The method of the description above is omitted until the adsorption layer is formed, and the description is omitted. Next, the honeycomb structure Η 2 is immersed in a powder of zeolite and a talc that has been used as an adhesive. , Kaolin, bentonite-like clay mineral powder dispersed in the suspension for several minutes, and then dried at a heat treatment of about 300 ° C for 1 hour to form a first adsorption layer 125. Next, a first adsorption layer will be formed The subsequent honeycomb structure 112 is immersed in an inorganic substance having a larger effective pore diameter than that of zeolite and the property of adsorbing gaseous organic impurities, such as porous clay minerals, diatomite, silica, alumina, dioxide A mixture of silicon and alumina, fine particles of aluminum silicate, activated alumina, porous glass, etc. are used as adhesives-and the dispersed suspension is dried for several minutes at 300 ° C for 1 hour to form The second adsorption layer 120. On the porous clay mineral, there are hydrated magnesium silicate clay minerals such as sepiolite and palygorskite, activated clay, and acid clay. 30, activated bentonite, silicic acid metal salt (please read the precautions on the back before filling in this page) hx Ding-,-° This paper size is suitable for China 1¾ China Standard (CNS) Λ4 specification (2 丨 0 XM7 Public Card> Printed by the Consumer Cooperative of the Central Bureau of Standards of the Ministry of Economic Affairs Γ 419390 V. Description of the invention () A composite of microcrystals and micron particles, etc. In this way, a second adsorption layer can be coated on the first adsorption layer 125 The honeycomb structure 112 of 126. The inorganic substance used in forming the first adsorption layer 125 and the second adsorption layer 126 contains at least an inorganic fixing auxiliary agent, for example, one of silicate soda, silica gel, or alumina sol. The function of the inorganic fixing aid is to help fix the powder of zeolite or inorganic binder forming the first adsorption layer 125 to the pores of the honeycomb structure 112, etc., and also to form the second adsorption. The inorganic substance of the layer 126 is firmly fixed to the auxiliary agent of the first adsorption layer 125. The honeycomb structure 112 obtained in this way does not contain combustible materials in the constituent materials, completely desorbs and removes gaseous organic impurities that cause surface contamination contained in the constituent materials during the heat treatment of the adsorption layer, and the honeycomb structure 112 itself does not. Gas organic impurities can occur. In addition, the material of the outer frame 115 shown in Fig. 13 is preferably a material that does not generate gaseous organic matter such as aluminum and does not contain combustible materials. In addition, in order to fix the honeycomb structure 112 to the outer frame 115 or to seal the gap between the honeycomb structure 112 and the outer frame 115, an adhesive or a sealant is preferred that it does not generate gaseous organic matter and does not contain combustible materials. At this time, for example, the entire filter 131 that has been assembled by installing the outer frame 115 on the honeycomb structure 112 may be heat-treated to completely remove and remove the non-flammable adhesive or sealant from the constituent material of the filter 131. Causes of surface contamination due to gaseous organic impurities. Therefore, the filter 131 as a whole can be composed of a material that does not contain combustible materials or a material that does not generate gaseous organic materials. In addition, of course, in the present invention, the structure of the support to which the zeolite and the adsorbent are fixed is not limited to the honeycomb structure described in FIG. 6 or FIG. 13 and the like. NS) Λ4. «1 Grid (Chuan ΓχπΊίί :) 1! -----— f {Please read the note on the back ^ a ^ item before filling out this page) Order ·· Central Laboratories of the Ministry of Economic Affairs, Consumer Co-operation for Offensive Work 枉Printed W 4Ϊ9390 ___ :; 5. Description of the invention () 112. For example, in FIG. 6 and FIG. 13, the direction of the ridge line of the corrugated sheet 110 arranged by sandwiching the thin sheet ill is arranged parallel to the flow direction of the processed air (direction of arrow Π3), but the corrugated sheet 110 may be arranged. The direction of the ridge line is arranged to have an appropriate angle with the flow direction of the processed air (direction of arrow 113). In FIGS. 6 and 13, the directions of the ridge lines of the adjacent wave pieces 110 are arranged parallel to each other, but the directions of the ridge lines of the adjacent wave pieces 110 may be arranged to cross each other. At that time, because the ridges between the adjacent wave pieces 110 collide, there is no fear that the adjacent wave pieces 110 are tightly connected, and the thin plate piece ill may be omitted. In addition, when the support structure is different from that of the honeycomb structure 112 described in Figs. 6 and 13, the zeolite can be fixed to the surface by the same method as before. A method for manufacturing another filter according to the present invention will be described. The three-dimensional mesh structure of the asbestos or ceramic magnet molded product manufactured by the above-mentioned manufacturing method is used as a support. In addition, in this example of the manufacturing method ', the granular zeolite is adhered to the surface of the support by Adhesive®. Regarding granular zeolite, an inorganic substance is used as a binder and a powder of zeolite is mixed to form a spherical shape. Around the pellets, a zeolite pellet with a coating layer is formed by coating an inorganic substance having an effective pore diameter larger than the effective pore diameter of the zeolite and having the property of adsorbing gaseous organic impurities. The method for producing the pellets may be used to form a coating layer of an inorganic substance by immersing a spherical zeolite in a suspension in which an inorganic substance for a coating film is dispersed and pulling it up and drying. In order to increase the strength of the coating layer, the sol-like inorganic fixing aid and the inorganic substance for coating film are dispersed together in the suspension so that the inorganic substance coated on the pellets contains the inorganic fixing aid. Inorganic substances or inorganic fixing aids for coating film 32 (Please read the precautions on the reverse side before filling out this page) ——— Order · ——, ---- 0 ---- This paper is in use Family rubbing (C'NS) / \ 4 said grid (2i «〆Μ7 'public epidemic) i .. Staff of the Central Standards Bureau of the Ministry of Economic Affairs, Cooperative Cooperative, Printing and Printing, t 419390 at __B7___ V. The types of invention description () are as above As shown. A filter according to the present invention can be manufactured by blowing the pellets thus granulated on a three-dimensional mesh structure impregnated with an inorganic adhesive in advance using a high-pressure air flow. Fig. 16 is an explanatory diagram schematically showing the structure of a cleaning device 201 according to the second embodiment of the present invention. The cleaning device 201 basically has the same structure as the cleaning device 1 described just now in FIG. That is, a processing space 202 for manufacturing, for example, an LSI or an LCD, a ceiling portion 203 and an underfloor portion 204 located above and below the processing space 202, and a return air passage 205 located on the side of the processing space 202. The ceiling unit 203 is provided with a fan unit 210 and a clean fan unit 2Π having one of the filter 100 or the filter 131 described above and a filter 212 for removing granular impurities. The processing space 202 is provided as an example of a heat generation source. Semiconductor manufacturing device 214. A non-condensing coil 210 for processing the thermal load of the semiconductor manufacturing apparatus 214 is provided below the floor portion 204 separated by the perforated plate 215. The cold water flow adjustment valve 18 of the non-condensing coil 16 is controlled so that the temperature detected by the temperature sensor 217 provided in the return air path 205 becomes the specified setting 値, and a fixed humidity is maintained without the coil being dew condensation. In addition, by operating the fan unit 210 and adjusting the appropriate airflow speed, the air inside the cleaning device 201 follows the ceiling portion 203-the processing space 202 and the bottom portion of the floor fen 4- > return air passage 205- > the ceiling portion 203 The sequential flow cycle. In this cycle, it is cooled by the non-condensing coil 216. One of the filter 100 or the filter Π1 in the clean fan unit 213 and the particle-removing filter 212 are used to remove gaseous organic impurities and Particulate impurities. (Please read the notes on the back before filling in this page) ------------ Order ·-* ---
-i HHM 本紙乐尺度適.丨丨H,闽挥家標準(CNS ) Λ4规格(2丨(>/297公您) 經濟部中央標隼局員工消費合作社印製 419390 at ___ B7 _ -*— _____ —— — . _ ......... 一.._._ 五、發明説明() 除去粒子之過濾器12配置在過濾器11之下游側,該 除去粒子之過濾器12具有可除去粒子狀雜質之功能。又, 用以除去灰塵等之除去粒子之過濾器12只由不發生氣體 有機雜質之材料構成。又,所吸入外氣經由外氣路徑220 適當地供給潔淨裝置201之地板下面部204內。在該外氣 路徑220配置具有用以自所吸入外氣除去氣體有機物之親 水性沸石之過濾器221、進行所吸入外氣之除麈、調溫、 調濕之單元型空調機器222以及濕度感測器227,控制單 元型空調機器222之調濕部之供水壓力調整閥229,使得 濕度感測器227所偵測到之濕度變成指定之設定値。而, 在處理空間202內設置濕度感測器228,用該濕度感測器 28偵測處理空間202內之環境之濕度。由外氣路徑220供 給潔淨裝置201之地板下面部204之所吸入外氣,經由回 氣通路205及天花板部203引入處理空間202。而且,由 排氣口 225經由排氣孔226向室外排出和所吸入外氣平衡 之空氣量。此外,圖上雖未示,在該潔淨裝置201也和剛 才在圖5所說明之情況一樣,不是將過濾器100或過濾器 131裝在潔淨裝置2〇1之天花板部203之全面,而是間隔 設置也可。 其次,詳細說明本發明之實施例之過濾器311。 圖17係本發明之實施例3之過濾器311之立體圖, U )、( b )分別表示分解圖、組立圖。該過濾器311 如圖Π ( a)所示,包括含有用以除去通過空氣中之氣體 有機雜質之合成沸石之第1過濾部31 la和具有用以除去用 34 本紙張尺度適用中阐1¾ Ϊ:標準((:NS ) Λ‘1况格(210 X 37公释) (#先閱讀背面之注意事項再填寫本頁)-i HHM The size of this paper music is suitable. 丨 丨 H, Fujian Standards (CNS) Λ4 Specification (2 丨 (> / 297) You printed by the Consumer Standards Cooperative of the Central Standardization Bureau of the Ministry of Economic Affairs 419390 at ___ B7 _-* — _____ —— —. _ ......... V. Description of the invention () The filter 12 for removing particles is arranged on the downstream side of the filter 11, and the filter 12 for removing particles It has the function of removing particulate impurities. In addition, the particle removing filter 12 for removing dust and the like is composed only of materials that do not generate gaseous organic impurities. In addition, the inhaled outside air is appropriately supplied to the cleaning device through the outside air path 220. In the floor portion 204 of 201. A filter 221 having a hydrophilic zeolite for removing gaseous organic substances from the inhaled outside air is arranged in the outside air path 220, and the deaeration, temperature and humidity of the inhaled outside air are performed. The unit type air conditioner 222 and the humidity sensor 227 control the water supply pressure adjustment valve 229 of the humidity control section of the unit type air conditioner 222, so that the humidity detected by the humidity sensor 227 becomes a specified setting. A humidity sensor 228 is disposed in the processing space 202, The humidity sensor 28 detects the humidity of the environment in the processing space 202. The inhaled outside air supplied to the underfloor portion 204 of the cleaning device 201 from the outside air path 220 is introduced into the processing space 202 via the return air passage 205 and the ceiling portion 203 In addition, the amount of air balanced and the amount of outside air taken in is exhausted from the exhaust port 225 to the outside through the exhaust hole 226. In addition, although not shown in the figure, the cleaning device 201 is also the same as the case just described in FIG. 5 It is not necessary to install the filter 100 or the filter 131 on the entire surface of the ceiling portion 203 of the cleaning device 200, but it may be arranged at intervals. Next, the filter 311 of the embodiment of the present invention will be described in detail. FIG. 17 shows the present invention. In the perspective view of the filter 311 of Embodiment 3, U) and (b) respectively show an exploded view and an assembly view. The filter 311 includes a first filter section 31a containing a synthetic zeolite for removing organic impurities passing through the air as shown in FIG. Π (a), and has a filter for removing 34 papers. : Standard ((: NS) Λ'1 condition (210 X 37)) (#Read the precautions on the back before filling this page)
經濟部中央標準局員工消费合作社印製 f: 4193 90 . 13 i 五、發明説明() 該第1過濾部31 la之合成沸石無法除去之氣體有機雜質之 具有比該合成沸石之有效細孔徑大之有效細孔徑之無機吸 附劑之透氣性第2過濾部311b。如圖17 C b )所示’藉 著將這些第1過濾部311a和第2過濾部311b重疊成彼此 相鄰,並將氣體有機雜質發生量少之氟樹脂系墊片339夾 在中間後,用螺絲固定凸緣’連結兩者。在照這樣連 結之過濾器311之上游側和下游側形成往圖上未示之管子 等之連接凸緣320。此外,這些第1、第2過濾部311a、 31 lb都除了氟樹脂系墊片339以外,只用不含可燃物之材 料構成,而且只用不產生氣體有機物之材料構成。 圖18係這些第1、2過濾器部311a、311b之槪略的 分解組立圖。第1、2過濾器部311a、311b都具有和剛 才在圖2所說明之過濾器11大致相同之構造。即,如圖1S 戶斤示,利用蜂巢構造物332構成,而蜂巢構造物332在構 造上,在相鄰波形片330之間夾住無凹凸之薄板片311後, 將銘製外框 335a、335b、335c、335d 及凸緣 320、334 組立成向[所處理空氣之流通方向333開口。但,在本發明 之實施例3之過濾器311,在第1過濾部311a、第2過濾 部31 lb分別用合成沸石、具有比該合成沸石之有效細孔徑 大之有效細孔徑之無機吸附劑分別固接在蜂巢構造物332 之表面整體。如後述所示,合成沸石之有效細孔徑最好係7 埃以上。又,如後述所示,無機吸附劑最好由矽藻土、二 氧化矽、氧化鋁、二氧化矽和氧化鋁之混合物、矽酸鋁、 活性氧化鋁、多孔質玻璃、緞帶形構造之含水矽酸鎂質黏 35 (請先閱讀背面之注意事項再填寫本頁) 灯· 0. 本纸張尺度適丨丨1屮阈阀家#準ί ) Λ4规格(2]〇 /297公弟) 419390 ... 經濟部中央標準局員工消费合作社印掣 A7 B7 五、發明説明() 土礦物、活性白黏土、酸性白黏土、活性膨潤土之至少〜 種構成。將這些無機吸附劑之3細孔特性如表2所示’作 爲參考。 在此,簡單說明第1、2過濾器部311a、311b之製 造方法之一例。到形成蜂巢構造物爲止之製程和上述一 樣。在第1過濾部311a、第2過濾部311b分別將蜂巢構 造物332在各自之側浸在使合成沸石之粉末(數μπι )和無 機系溶膠黏接劑(矽膠、氧化鋁溶膠、矽酸蘇打等)分散 之懸濁液中、使具有比該合成沸石之有效細孔徑大之有效 細孔徑之無機吸附劑之(由矽藻土、二氧化矽、氧化銘、 _ 36 __ 本纸張尺度中®丨^1家樣準(CNS「八4说格(:ΜΟχ297公楚) (請先閲請背面之注意事項再填寫本頁)Printed by the Consumer Cooperative of the Central Bureau of Standards of the Ministry of Economic Affairs f: 4193 90. 13 i V. Description of the invention () The gas organic impurities that cannot be removed by the synthetic zeolite in the first filtering section 31 la have a larger effective pore size than the synthetic zeolite The air-permeable second filter portion 311b of the inorganic adsorbent having an effective pore diameter. As shown in FIG. 17C b) 'After the first filter portion 311a and the second filter portion 311b are overlapped to be adjacent to each other, and a fluororesin gasket 339 having a small amount of gaseous organic impurities is sandwiched therebetween, Screw the flange 'to the two. On the upstream side and the downstream side of the filter 311 connected in this way, connection flanges 320 are formed toward pipes or the like not shown in the figure. In addition, these first and second filter sections 311a and 31 lb are made of a material containing no combustible materials except a fluororesin gasket 339, and are made of a material that does not generate gaseous organic matter. Fig. 18 is a schematic exploded assembly view of the first and second filter portions 311a and 311b. Both the first and second filter sections 311a and 311b have substantially the same structure as the filter 11 just described in FIG. That is, as shown in FIG. 1S, the honeycomb structure 332 is used, and the honeycomb structure 332 is structurally sandwiched between the adjacent corrugated sheet 330 without the uneven plate sheet 311, and then the outer frame 335a, 335b, 335c, 335d and flanges 320, 334 are assembled so as to open in [the flow direction of treated air 333]. However, in the filter 311 of Example 3 of the present invention, synthetic zeolite is used in the first filtering portion 311a and 31 lb in the second filtering portion, and an inorganic adsorbent having an effective pore size larger than that of the synthetic zeolite is used. They are respectively fixed to the entire surface of the honeycomb structure 332. As will be described later, the effective pore diameter of the synthetic zeolite is preferably 7 angstroms or more. As will be described later, the inorganic adsorbent is preferably made of diatomaceous earth, silica, alumina, a mixture of silica and alumina, aluminum silicate, activated alumina, porous glass, and a ribbon structure. Water-containing Magnesium Silicate 35 (Please read the precautions on the back before filling in this page) Lamp · 0. The paper size is appropriate 丨 丨 1 屮 Valve Home # 准 ί) 4 specifications (2) 〇 / 297 ) 419390 ... A7 B7, a consumer cooperative of employees of the Central Standards Bureau of the Ministry of Economic Affairs 5. Description of the invention () At least ~ species of soil mineral, activated white clay, acidic white clay, activated bentonite. The 3 pore characteristics of these inorganic adsorbents are shown in Table 2 'as a reference. Here, an example of a method of manufacturing the first and second filter sections 311a and 311b will be briefly described. The process until the honeycomb structure is formed is the same as above. The honeycomb structure 332 was immersed on each side of the first filtering part 311a and the second filtering part 311b with a synthetic zeolite powder (several μm) and an inorganic sol adhesive (silica gel, alumina sol, and silicic acid soda). Etc.) of an inorganic adsorbent (made of diatomaceous earth, silica, oxide, etc.) in a dispersed suspension that has an effective pore diameter larger than the effective pore diameter of the synthetic zeolite. ® 丨 ^ 1 sample standard (CNS "eight-four said grid (: ΜΟχ297 公 楚) (Please read the notes on the back before filling in this page)
表2 腿樣品 用BET法量沏ί之 比表面積(m2/g ) 用N2吸附法量測之細孔 容積(cc/g) 15〜300埃 砍藻土 200 0.25 矽膠 400 0.61 氧化鋁溶膠 250 0.60 矽酸鋁 225 0.60 活性氧化鋁 300 0.30 多孔質玻璃 400 0.15 海泡石 295 0.33 活性白黏土 300 0.37 活性膨潤土 87 0.23 經濟部中央標率局員工消費合作祍印製 ‘419390 a 7 —~—------------------ B7 五、發明説明( ) r 二氧化矽和氧化鋁之混合物、砍酸鋁、活性氧化鋁、多孔 質玻璃 '緞帶形構造之含水矽酸鎂質黏土礦物、活性白黏 土、酸性白黏土、活性膨潤土之至少一種構成)粉末(數 μιη )和無機系溶膠黏接劑(矽膠、氧化鋁溶膠、矽酸蘇打 等)分散之懸濁液中數分鐘後,以3〇〇 °C ' 1小時之熱處 理乾燥,就可各自得到第1、2過濾器部311a、311b。 但,矽膠或氧化鋁溶膠係包含由單分散之豪微米到數十豪 微米之一次粒子之懸濁液,可是在固接在支撐物之表面之 乾燥狀態,變成係由一次粒子集合而成之三次元凝聚物之 矽膠或氧化鋁溶膠。因此,將多孔性蜂巢構造物332浸在 只有矽膠或氧化鋁溶膠之無機系溶膠黏接劑之懸濁液後乾 燥,也可得到無機系溶膠黏接劑固接在蜂巢構造物332之 表面之第2過濾部311b。 利用這些第1、2過濾器部311a、311b構成之過濾 器311,因在構成材料上不含可燃物’完全脫離並除去在 將過濾器熱處理時構成材料所含成爲表面污染之原因之氣 體有機雜質成分,過濾器本身也不會發生氣體有機雜質。 圖19係用以表示這些第1、2過濾器部311a、311b 之另一連結狀態之過濾器311之槪略的分解組立圖。如圖 19所示之過濾器311在構造上’將比在圖18所說明的長 的鋁製外框335a、335b、335c、335d及凸緣320組立 成筒形,在其內部空間配置將合成沸石固接在表面之蜂巢 構造物332a和將具有比該合成沸石之有效細孔徑大之有 交女細孔徑之無機吸附劑固接在表面之蜂巢構造物兩 __________________________ 37_:__ 木氏張尺度埤出中國闽本樣卑(('NS ) Λ4現将(2丨公漦) (請先閲讀背面之注意事項再填寫本頁)Table 2 Specific surface area (m2 / g) of leg sample by BET method, pore volume (cc / g) measured by N2 adsorption method Aluminum Silicate 225 0.60 Activated Alumina 300 0.30 Porous Glass 400 0.15 Sepiolite 295 0.33 Activated White Clay 300 0.37 Activated Bentonite 87 0.23 Printed by the Ministry of Economic Affairs of the Central Standards Bureau, Consumer Consumption, printed '419390 a 7 — ~ ---- ---------------- B7 V. Description of the invention () r A mixture of silica and alumina, chopped aluminum, activated alumina, porous glass' ribbon structure At least one composition consisting of hydrous magnesium silicate clay mineral, activated white clay, acidic white clay, activated bentonite powder (several μm) and inorganic sol adhesive (silicone, alumina sol, silicic acid soda, etc.) After a few minutes in the turbid liquid, it was dried by heat treatment at 300 ° C 'for 1 hour, and the first and second filter portions 311a and 311b were obtained. However, the silica gel or alumina sol is a suspension containing primary particles ranging from monodisperse micrometers to tens of micrometers, but in a dry state fixed on the surface of the support, it becomes a collection of primary particles Three-dimensional condensate of silica gel or alumina sol. Therefore, the porous honeycomb structure 332 can be dipped in a suspension of an inorganic sol adhesive containing only silicon gel or alumina sol and dried to obtain an inorganic sol adhesive fixed on the surface of the honeycomb structure 332. The second filtering unit 311b. The filter 311 constituted by the first and second filter portions 311a and 311b is completely free of combustible materials and does not contain gas, which is a cause of surface contamination when the filter is heat-treated. Impurity components, and the filter itself does not generate gaseous organic impurities. FIG. 19 is a schematic exploded assembly view of the filter 311 showing another connection state of the first and second filter portions 311a and 311b. The filter 311 shown in FIG. 19 is structured to assemble a long aluminum frame 335a, 335b, 335c, 335d and a flange 320 longer than those described in FIG. 18 into a cylindrical shape. A honeycomb structure 332a with zeolite fixed on the surface and a honeycomb structure with an inorganic adsorbent having an intersect female pore size larger than the effective pore size of the synthetic zeolite fixed on the surface __________________________ 37_: __ Mu's Zhang scale Illustrated Chinese Minben (('NS) Λ4 will now be (2 丨 public)) (Please read the notes on the back before filling this page)
經濟部中央標準局貝工消費合作祍印製 * 4133 90 a? B7__ 五、發明説明() 者。此時,蜂巢構造物3:32a、332b配置成彼此密接也可; 蜂巢構造物332a、332b在共同之筒形鋁製外框335a、 335b、335c、335d之內部空間配置成彼此分離也可。在 圖19,用蜂巢構造物332a和外框335a〜d形成第1過濾部 31 la,用蜂巢構造物332b和外框335a〜d形成第2過濾部 311b。 圖20係表示其他實施例之過濾器311之構造之立體 圖。在本實施例,將係具有透氣性之支撐物之蜂巢構造物 380以和其通氣方向383交叉之境界面(在圖上係距離過 濾器兩端等距離之位置)爲境界分割成2個區域,在一個 區域,讓用合成沸石或合成沸石粉末形成之小球固接在蜂 巢構造物380之表面而形成第1過濾部,在另一個區域, 讓用有效細孔徑比合成沸石大之無機吸附劑或該無機吸附 劑之粉末形成之小球固接在蜂巢構造物380之表面而形成 第2過濾部。在本實施例係,使未分割之一體化之蜂巢構 造物380之相對於通氣方向383之上游側381之約一半浸 在令該合成沸石分散之懸濁液後乾燥而在蜂巢構造物380 之上游側381之表面形成合成沸石之無機材料層,再使蜂 巢構造物380之相對於通氣方向383之下游側382之約一 半浸在令具有比該合成沸石之有效細孔徑大之有效細孔徑 之無機吸附劑(由矽藻土、二氧化矽、氧化鋁、二氧化矽 .和氧化鋁之混合物、矽酸鋁、活性氧化鋁、多孔質玻璃、 緞帶形構造之含水矽酸鎂質黏土礦物、活性白黏土、酸性 白黏土、活性膨潤土之至少一種構成)分散之懸濁液後乾 38 (讀先閱讀背面之注意事項再填寫本頁) 訂 本紙張尺度適川中闽囚家#隼(CNS ) ,\4規格(210>._ 公f > ί 419390 經濟部中央標準局員工消費合作社印製 A 7 Β7 五、發明説明() 燥而在下游側382之表面形成該無機吸附劑之無機材料層 的。合成沸石之無機材料層和該無機吸附劑之無機材料層 在上游側381和下游側382之境界附近彼此重疊也可;又, 在上游側381和下游側382之境界附近,露出都未形成合 成沸石之無機材料層和該無機吸附劑之無機材料層之蜂巢 構造物380之原本之底子也可。將該蜂巢構造物380和圖 19 一樣用筒形之鋁製外框圍住,就形成本發明之過濾器 311 〇用外框所圍住之蜂巢構造物380之上游側381之部 分相當於第1過濾部311a,而用外框所圍住之蜂巢構造物 380之下游側382之部分相當於第2過濾部31 lb。在本例’ 將包含合成沸石之第1過濾部31 la和包含該無機吸附劑之 第2過濾部31 lb之任何一方相對於過濾器311之通氣方向 配置在上游側都可。 若依據本發明者之見識,如後述所示,將合成沸石之 無機材料層作爲第1吸附層設置在支撐物之表面後,再將 該無機吸附劑之無機材料層作爲第2吸附層設置成重疊在 其上之構造,和將各自之吸附層分成第1過濾部31 la和第 2過濾部31 lb之構造相比,能以更小型之構造得到相等之 .有機雜質除去性能。 過濾器部311a、311b之製造方法未限定爲上述方 法,使加工成小球之合成沸石或該無機吸附劑附著在薄片 (支撐物)也可,其方法如上述所示。 圖23 ( a )、( b )都表示使用外殼並充塡小球而成 之本發明之其他實施例之過濾器370 ’( a )係(b )之 39 (請先閱讀背面之注意事項再填寫本1)Printed by the Central Bureau of Standards of the Ministry of Economic Affairs for the consumption cooperation of shellfishers * 4133 90 a? B7__ V. Inventor (). At this time, the honeycomb structures 3: 32a, 332b may be arranged to be in close contact with each other; the honeycomb structures 332a, 332b may be arranged to be separated from each other in the internal space of the common cylindrical aluminum frame 335a, 335b, 335c, and 335d. In Fig. 19, the first filter portion 31a is formed by the honeycomb structure 332a and the outer frames 335a to d, and the second filter portion 311b is formed by the honeycomb structure 332b and the outer frames 335a to d. Fig. 20 is a perspective view showing the structure of a filter 311 according to another embodiment. In this embodiment, the honeycomb structure 380, which is a breathable support, is divided into two areas by the boundary interface (crossing the same distance from the two ends of the filter) as the boundary of the ventilation direction 383. In one area, a ball formed of synthetic zeolite or a synthetic zeolite powder is fixed on the surface of the honeycomb structure 380 to form a first filtering part. In another area, an inorganic adsorbent having an effective pore diameter larger than that of the synthetic zeolite is used. The pellet formed from the powder of the adsorbent or the inorganic adsorbent is fixed on the surface of the honeycomb structure 380 to form a second filtering portion. In this embodiment, about half of the undivided integrated honeycomb structure 380 with respect to the upstream side 381 of the ventilation direction 383 is immersed in a suspension in which the synthetic zeolite is dispersed, and then dried in the honeycomb structure 380. An inorganic material layer of a synthetic zeolite is formed on the surface of the upstream side 381, and approximately half of the honeycomb structure 380 with respect to the downstream side 382 of the ventilation direction 383 is immersed in an effective pore diameter having a larger effective pore diameter than the synthetic zeolite. Inorganic adsorbent (composed of diatomite, silica, alumina, silica. And alumina mixture, aluminum silicate, activated alumina, porous glass, ribbon-shaped hydrous magnesium silicate clay mineral , Activated white clay, acidic white clay, at least one component of activated bentonite) dispersed suspension 38 (read the precautions on the back before filling this page) The size of the paper is suitable for Sichuan Chumin Minjia # 家 (CNS ), \ 4 specifications (210 > ._ 公 f > ί 419390 Printed by the Consumer Cooperatives of the Central Bureau of Standards of the Ministry of Economic Affairs A 7 Β7 V. Description of the invention () Dry and form the inorganic adsorbent on the surface of the downstream side 382 The inorganic material layer of the agent. The inorganic material layer of the synthetic zeolite and the inorganic material layer of the inorganic adsorbent may overlap each other near the boundary between the upstream side 381 and the downstream side 382; and, the boundary between the upstream side 381 and the downstream side 382 Nearby, the original structure of the honeycomb structure 380 where the inorganic material layer of the synthetic zeolite and the inorganic material layer of the inorganic adsorbent are not formed may be exposed. The honeycomb structure 380 is made of cylindrical aluminum as shown in FIG. 19. The frame 311 forms the filter 311 of the present invention. The upstream side 381 of the honeycomb structure 380 surrounded by the outer frame is equivalent to the first filter portion 311a, and the honeycomb structure 380 surrounded by the outer frame. The portion on the downstream side 382 corresponds to 31 lb of the second filter portion. In this example, either of the first filter portion 31 a including the synthetic zeolite and the second filter portion 31 lb including the inorganic adsorbent is opposed to the filter. The ventilation direction of 311 may be arranged on the upstream side. According to the knowledge of the inventors, as will be described later, an inorganic material layer of synthetic zeolite is set as the first adsorption layer on the surface of the support, and then the inorganic adsorption is performed. The structure in which the inorganic material layer is provided as the second adsorption layer is superimposed thereon, and can be obtained with a smaller structure than the structure in which the respective adsorption layers are divided into the first filter portion 31 a and the second filter portion 31 lb. Equivalent. Removal performance of organic impurities. The manufacturing method of the filter sections 311a and 311b is not limited to the above method, and a synthetic zeolite processed into pellets or the inorganic adsorbent may be attached to a sheet (support), and the method is as described above. Figures 23 (a) and (b) show the filter 370 '(a) of (b) 39 of the other embodiment of the present invention formed by using a shell and filling a small ball (please read the back Matters needing attention fill in this 1)
本纸張尺度適用中國固家捸準(〔、?^)六4规格(2丨0/297公漦> 經濟部中央標準局負工消费合作社印製 ^ 419350 m 五、發明説明() A-A剖面,(b )係(a )之B-B剖面。在本實施例之過 濾器370,如圖所示,將合成沸石之小球371a充塡在內外 側面具有多個透氣口 373之中空圓筒形外殼372a而形成第 1過濾部370a,將該無機吸附齊ί之小球371b 一樣地充塡在 內外側面具有多個透氣口 373之中空圓筒形外殼372b而形 成第2過濾部370b_。但,因外殼372a之下面和外殼372b 之上面塞住,當所處理空氣由外殻372a之內側向外側流出 時,通過外殻372a內之小球371a之充塡層。其次’所處 理空氣通過由外殼372a之外側圓筒和外筒374所夾住之空 間,自外殼372b之之外側圓筒流入小球371b之充塡層。 然後,流入外殼372b之內側,向過濾器370之下方流出。 此外,所處理空氣之流通方向在圖23 ( b ),以箭頭375 表示。此外,在圖23,將第1過濾部370a配置在上游側、 將第2過濾部370b配置在下游側,但是將該順序顛倒的也 是本發明之實施例。 在使用小球之過濾器及其製造方法上也可舉例如下。 良口,藉著利用高速空氣將小球吹到預先令附著無機系且不 可燃性之黏接劑之支撐物,可製造如圖21、圖22所示之 本發明之過濾器。在支撐物上未必限定爲蜂巢構造物,可 列舉石綿等三次元網目構造物。在後者因所處理空氣穿過 網目構造物,空氣阻力大,但是和該合成沸石或該無機吸 附劑之小球之接觸機會反而比蜂巢構造物的多。將把合成 沸石或無機吸附劑之粉末和該無機系溶膠黏接劑混合造粒 而成之小球固接在支撐物時,例如將淸水與粉末和該無機 40 -5 / (請先閲讀背面之注意事項再填寫本頁)This paper size is applicable to China Gujia Standard ([,? ^) 6 4 specifications (2 丨 0/297 Gong > Printed by the Central Consumers Bureau of Ministry of Economic Affairs and Consumer Cooperatives ^ 419350 m 5. Description of invention () AA The cross section, (b) is the BB cross section of (a). In the filter 370 of this embodiment, as shown in the figure, the synthetic zeolite ball 371a is filled with a hollow cylindrical shape having a plurality of air vents 373 on the inner and outer sides. The outer casing 372a forms the first filtering portion 370a, and the inorganic adsorption-receiving small ball 371b is similarly filled with a hollow cylindrical outer casing 372b having a plurality of air vents 373 on the inner and outer sides to form the second filtering portion 370b. Because the bottom of the casing 372a and the top of the casing 372b are plugged, when the processed air flows out from the inside of the casing 372a to the outside, it passes through the filling layer of the small ball 371a in the casing 372a. Secondly, the processed air passes through the casing The space sandwiched by the outer cylinder 372a and the outer cylinder 374 flows into the filling layer of the small ball 371b from the outer cylinder of the outer shell 372b. Then, it flows into the inner side of the outer shell 372b and flows out below the filter 370. In addition, The flow direction of the treated air is shown in Figure 23 (b). It is indicated by an arrow 375. In FIG. 23, the first filter portion 370a is disposed on the upstream side and the second filter portion 370b is disposed on the downstream side. However, this order is also reversed according to the embodiment of the present invention. Using a ball The filter and its manufacturing method can also be exemplified as follows. Liangkou, by using high-speed air to blow the ball to the support of inorganic and non-flammable adhesive in advance, can be manufactured as shown in Figure 21, Figure The filter of the present invention shown in 22. The support is not necessarily limited to a honeycomb structure, and can include three-dimensional mesh structures such as asbestos. In the latter, the air resistance is large because the processed air passes through the mesh structure, but Synthetic zeolite or the beads of the inorganic adsorbent have more contact opportunities than honeycomb structures. The pellets made by mixing the powder of the synthetic zeolite or the inorganic adsorbent with the inorganic sol adhesive are fixed to For support, for example, water and powder and the inorganic 40 -5 / (Please read the precautions on the back before filling this page)
Α7 Β7 4193 90 五、發明説明() 系溶膠黏接劑之混合物混合,變成黏土狀,用造粒機造粒 成約0.3〜0.8之小球。 照這樣製造之過濾器311或37〇,因構成材料不含可 燃物,將過濾器3 η或過濾器370裝在無麈室或無麈操作 台之天花板面之情況’和將以係可燃物之活性炭爲基底之 習知之化學式過濾器裝在天花板面之情況相比’防災上之 安全性顯著提高。 在進行半導體之製造等之潔淨裝置發生之成爲基板表 面污染之原因之有機物只限於自密封劑發生之有機物矽氧 烷、自建材中之不易燃劑發生之磷酸酯、自建材中之可塑 劑產生之鄰苯二甲酸鹽、自光阻劑密接劑發生之HMDS、 自盒之防止氧化劑發生之BHT等高沸點•高分子有機化合 物。這些有機物之發生源係無麈室等潔淨裝置之構成材料 或位於潔淨裝置內部之用於製造之各種零件,由所吸入外 氣引起的很少。因此,過濾器311或370之作用主要係自 循環空氣中除去在潔淨裝置內部發生之成爲表面污染之原 因之高沸點•高分子有機化合物,降低潔淨裝置內部之這些 有機物濃度。 〔實施例〕 其次利用實施例說明上述本發明之實施例之潔淨裝置 和過濾器之作用效果。 首先,在潔淨裝置之一例上,在無塵室中,在利用各 自使用粒狀活性炭、纖維狀活性炭之市面上之化學式過濾 器2種和使用離子交換纖維之化學式過濾器所處理之無塵 !1-----If (請先閲讀背面之注意事項再填寫本頁) 丁 --° 經濟部中央標準局貝工消費合作社印製 本紙乐尺度適丨丨]中阑闷家桴苹((、沾)六4現格(2!〇Χ 297公荩) 經濟部中央標车爲員工消f合作社印製 4 193 90, 五、發明説明() 室空氣以及用液態氮將無塵室中之空氣冷卻並凝結除去雜 質後之乾;空氣之共4種環境中,附氧化膜砂晶片表面之 接觸角之隨著間變化之量測結果如圖24所示。 在表面滴下超純水所量測之接觸角係簡便評價表面之 有機物污染程度之方法。在剛洗淨後之無有機物污染之附 氧化膜砂晶片或玻璃表面具有易和水溶合之性質,即係親 7]C性,接觸角變小。可是在被有機物污染後之表面有排拒 水之性質,即係疏水性,接觸角變大。例如,已知以放置 在無塵室環境中之玻璃基板表面爲對象,滴下超純水之接 觸角之量測値和利用X射線電子分光法(XPS : X-ray Photoelectron Spectroscopy )所量測之有機物表面污染有圖 25所示之相關關係。對於附氧化膜矽晶片之表面,在基板 表面之水之接觸角之大小和有機物表面污染之間也有極強 之相關。 由圖24之結果得知如下事項。離子交換纖維本來係用 .以吸附除去水溶性無機雜質的,無法吸附有機物,相反地 產生氣體有機物。得知放置1天接觸角約增加1〇度。而在 乾燥空氣環境中,因幾乎不含氣體有機物,接觸角不增加。 本來應防止有機物表面污染之2種活性炭過濾器,放置1 天接觸角約增加1〇度,表示表面污染防止效果幾乎沒有。 利用了活性炭之2種化學式過濾器沒有效果之原因係’因 化學式過濾器之構成材料含有黏結劑、黏接劑、密封劑等 表面有機污染物質,原本的活性炭吸附效果被構成材料之 逸脫氣體抵消。而,在使用了充塡塔之情況,若充塡塔之 42 (請先閱讀背面之注意事項再填寫本頁) Q. 訂 本紙张尺度適;Π中阐阄家標夺(CNS丨Λ4規格(UO·〆297公筇) 經濟部中央橾準局貝工消#合作社印取 4193 90 A7 __ B7________ 五、發明説明() 容器等使用金屬材料,就沒有這種問題,但是如上述所示’ 充塡塔有壓力損失(通氣阻力)大之缺點。 其次,實際製造在圖1所說明之本發明之潔淨裝置’ 將剛洗淨後之無有機物污染之附氧化膜砂晶片基板放在處 理空間。過濾器在構造上係使疏水性沸石固接在蜂巢構造 物。然後分別量測剛洗淨後和放置3天後之接觸角’調查 放置3天後接觸角之增加量。每15天同樣地重複量測放置 3天後接觸角之增加量(洗淨量測接觸角->放置3天―量 測接觸角),量測了過濾器之吸附性能之隨著間的劣化。 設潔淨裝置內之循環空氣流量爲5000m3/min,爲了處理該 循環空氣所使用之疏水性沸石之使用量爲5000kg。即,設 爲每lm3/min通氣量之疏水性沸石使用量爲lkg。所吸入 外氣之量設爲循環空氣流量之4%之200m3/miri。無塵室整 體之內容積係3120m3,每小時之換氣次數爲100次。 又,爲了比較,將具有疏水性沸石之過濾器更換爲將 纖維狀活性炭和低融點聚酯之黏接劑複合而變成毛氈狀之 習知構造之化學式過濾器,每15天重複量測附氧化膜矽晶 ’片基板洗淨後放置3天之接觸角之增加量。此時也設爲每 lm3/min通氣量之活性炭使用量爲lkg。還對於都未設置本 發明之具有疏水性沸石之過濾器或習知構造之化學式過濾 器之情況,即對於潔淨裝置環境中所含氣體有機物未講求 特別之對策之情況也進行一樣的量測。 此外,剛洗淨後附氧化膜矽晶片之表面之接觸角係3 度。假設對用以防止因氣體有機雜質之污染而導致組件品 43 (請先間讀背面之注意事項再填寫本頁) 訂._ 本纸張乂度適州巾闽®家行4*· ( CNS ) Λ4规格(2⑴公筇) 經濟部中央標準局員工消費合作社印裝 4193 90 五、發明説明() 質降低之潔淨裝置環境要求之必要條件係曝露3天後附氧 化膜矽晶片之表面之接觸角保持在6度以下。 量測結果如圖26所示。比較了分別曝露在按照本發明 之潔淨裝置環境、設置了習知構造之化學式過濾器之潔淨 裝置環境、對於氣體有機物未講求特別對策之潔淨裝置環 境下3天後附氧化膜矽晶片之表面之接觸角之隨著間變 化。 曝露在對於氣體有機物未講求特別之對策之潔淨裝置 環境下之附氧化膜矽晶片之表面之接觸角,剛洗淨後係3 度,而放置3天後增加了 26〜30度。對於具有疏水性沸石 之過濾器,在剛開始使用後之狀態’放置3天後之附氧化 膜矽晶片之接觸角保持在4度以下。可是,隨著通氣時間 之增加,疏水性沸石之吸附性能降低,通過吸附層後之空 氣中所含氣體有機物之濃度也增加。即,隨著對疏水性沸 石之通氣時間增加’曝露在下游側之已處理空氣之附氧化 膜砂晶片之表面之接觸角也增加。得知到曝露在通過過濾 器後之空氣3天之附氧化膜矽晶片之表面之接觸角達到6 度爲止之過濾器之使用時間約6個月。而,對於習知之化 學式過濾器,連在剛開始使用後之狀態放置3天之附氧化 膜矽晶片之接觸角竟達到12度。其理由係’來自用以載持 纖維狀活性炭的低融點聚酯之黏接劑之逸脫氣體全部通過 化學式過濾器’污染了放置在下游側之砂晶片之表面。而 在本發明之過濾器’如在前面簡單說明製造方法之一例所 示,因構成材料不含有機物,由構成材料本身不會產生氣 44 ___ 本錄歧制彳,丨率() Λ4蚬格(210X 297公符) (請先閱讀背面之注意事項再填寫本頁)Α7 Β7 4193 90 V. Description of the invention () The mixture of the sol-based adhesive is mixed to become clay, and granulated by a granulator into pellets of about 0.3 to 0.8. In the case of the filter 311 or 37 manufactured as such, since the constituent material does not contain combustible materials, the case where the filter 3 η or the filter 370 is installed on the ceiling surface of a non-chamber or non-panel operating table 'will be combustible When the conventional chemical filter with activated carbon as the base is installed on the ceiling surface, the safety in disaster prevention is significantly improved. The organic substances that cause the surface contamination of substrates in clean equipment such as semiconductor manufacturing are limited to organic substances that occur from sealants, phosphates that originate from non-flammable agents in building materials, and plasticizers that originate from building materials. High boiling point and high molecular organic compounds such as phthalates, HMDS generated from photoresist adhesives, and BHT that prevents oxidants from occurring. The sources of these organic substances are the constituent materials of clean devices such as chambers or various parts used for manufacturing inside the clean devices, which are rarely caused by the inhaled air. Therefore, the function of the filter 311 or 370 is mainly to remove the high boiling point and high molecular organic compounds that cause surface contamination inside the clean device from the circulating air, and reduce the concentration of these organic substances in the clean device. [Embodiment] Next, the effect of the cleaning device and the filter of the embodiment of the present invention described above will be described using the embodiment. First of all, in an example of a clean device, in a clean room, two types of chemical filters on the market using granular activated carbon and fibrous activated carbon, and a chemical filter using ion exchange fiber are processed! 1 ----- If (Please read the precautions on the back before filling out this page) Ding-° The paper is printed by the Central Standards Bureau of the Ministry of Economy (Zhan) June 4th (2! 〇 × 297 public) The central ministry of the Ministry of Economy printed 4 193 90 for employees' cooperatives. V. Description of the invention () Room air and the use of liquid nitrogen in the clean room The air is cooled and condensed to remove the impurities and dried; in a total of 4 environments, the measurement results of the contact angle of the surface of the wafer with the oxide film on the surface are shown in Figure 24. The amount of ultrapure water dripped on the surface The measured contact angle is a simple and convenient method to evaluate the degree of organic pollution on the surface. After cleaning, the wafer or glass surface with an oxide film without organic pollution is easy to dissolve with water. The angle becomes smaller, but it is soiled by organic matter The surface after dyeing has a water-repellent property, that is, hydrophobic, and the contact angle becomes larger. For example, it is known to measure the contact angle of ultrapure water dripping on the surface of a glass substrate placed in a clean room environment. There is a correlation between the surface contamination of organic matter measured by X-ray Photoelectron Spectroscopy (XPS: X-ray Photoelectron Spectroscopy) and the contact angle of water on the surface of a substrate with an oxide film on a silicon wafer surface There is also a strong correlation between the size and surface contamination of organics. The results shown in Figure 24 show the following. Ion exchange fibers are originally used. Those that adsorb and remove water-soluble inorganic impurities cannot adsorb organics, and instead produce gaseous organics. It is known that the contact angle increases by about 10 degrees after being placed for one day. In a dry air environment, the contact angle does not increase because it contains almost no gaseous organic matter. Two types of activated carbon filters, which should prevent the surface pollution of organic matter, are placed for one day An increase of about 10 degrees indicates that the surface pollution prevention effect is almost non-existent. The reason why the two types of chemical filters using activated carbon have no effect is 'causalization' The constituent material of the filter includes organic pollutants on the surface, such as binders, adhesives, sealants, etc. The original activated carbon adsorption effect is offset by the escape gas of the constituent materials. However, if a charging tower is used, Tower No. 42 (Please read the notes on the back before filling out this page) Q. The size of the paper is appropriate; 阄 House Standards (CNS 丨 Λ4 Specification (UO · 〆297) 筇), Central Bureau of Standards, Ministry of Economic Affairs Beigongxiao # Cooperative cooperative print 4193 90 A7 __ B7________ 5. Description of the invention () The use of metal materials such as containers does not have this problem, but as shown above, the filling tower has the disadvantage of large pressure loss (ventilation resistance). Secondly, the cleaning device of the present invention described in FIG. 1 is actually manufactured. The wafer substrate with an oxide film sand without oxide pollution immediately after cleaning is placed in a processing space. The filter is structured so that the hydrophobic zeolite is fixed to the honeycomb structure. Then, the contact angles immediately after washing and after 3 days of standing were measured to investigate the increase in the contact angle after 3 days of standing. Repeatedly measure the increase in contact angle every 15 days after being left for 3 days (washing and measuring contact angle-> standing for 3 days-measuring the contact angle), and measured the adsorption performance of the filter over time. Degradation. The circulating air flow in the clean device is set to 5000m3 / min, and the amount of hydrophobic zeolite used to treat the circulating air is 5000kg. That is, the use amount of the hydrophobic zeolite per lm3 / min is 1 kg. The amount of inhaled outside air is set to 200m3 / miri which is 4% of the circulating air flow. The total internal volume of the clean room is 3120m3, and the number of air changes per hour is 100 times. In addition, for comparison, the filter with hydrophobic zeolite was replaced with a chemical structure filter with a conventional structure in which a fibrous activated carbon and a low-melting point polyester compound were compounded into a felt-like structure, and the measurement was repeated every 15 days. The amount of increase in the contact angle of the oxide film silicon crystal substrate after being cleaned for 3 days. At this time, the amount of activated carbon per lm3 / min ventilation was set to 1 kg. The same measurement is also performed in the case where neither the filter having a hydrophobic zeolite of the present invention nor the chemical filter of a conventional structure is provided, that is, no special measures are taken for the gaseous organic substances contained in the clean device environment. In addition, the contact angle of the surface of the silicon wafer with an oxide film immediately after cleaning was 3 degrees. Assume that it is used to prevent the component products caused by the pollution of gas and organic impurities. 43 (please read the precautions on the back before filling this page). _ This paper is suitable for Shizhou Towels® Family Line 4 * · (CNS) Λ4 Specifications (2mm) Printed by the Consumer Cooperatives of the Central Standards Bureau of the Ministry of Economic Affairs 4193 90 V. Description of the invention () The necessary condition for the environmental requirements of a clean device with reduced quality is to maintain the contact angle of the surface of the silicon wafer with an oxide film after 3 days of exposure Below 6 degrees. The measurement results are shown in Figure 26. The surface of the silicon wafer with an oxide film after three days of exposure to a clean device environment according to the present invention, a clean device environment equipped with a conventional chemical filter, and a clean device environment that does not require special measures for gaseous organic matter are compared. The contact angle varies with time. The contact angle of the surface of the silicon wafer with an oxide film exposed to a clean device that does not require special measures for gaseous organic matter is 3 degrees immediately after cleaning, and it increases 26 to 30 degrees after being left for 3 days. For a filter having a hydrophobic zeolite, the contact angle of the silicon wafer with an oxide film after being left for 3 days in the state immediately after use was kept below 4 degrees. However, as the aeration time increases, the adsorption performance of the hydrophobic zeolite decreases, and the concentration of gaseous organics in the air after passing through the adsorption layer also increases. That is, as the aeration time for the hydrophobic zeolite increases, the contact angle on the surface of the oxide-coated sand wafer exposed to the downstream side of the treated air also increases. It is known that the use time of the filter until the contact angle of the surface of the silicon wafer with an oxide film on the surface of the air exposed to the filter for 3 days reaches 6 degrees is about 6 months. However, for the conventional chemical filter, the contact angle of the silicon wafer with an oxide film even after being left for 3 days after being used has reached 12 degrees. The reason is that all the escape gas from the adhesive of the low melting point polyester for supporting fibrous activated carbon passes through the chemical filter and contaminates the surface of the sand wafer placed on the downstream side. In the filter of the present invention, as shown in the example of the manufacturing method briefly described above, because the constituent material does not contain organic matter, the constituent material itself does not generate gas. 44 ___ This record disproportionates 丨, the rate () Λ 4 蚬 grid (210X 297 characters) (Please read the notes on the back before filling in this page)
經濟部中央標準局負工消费合作社印製 / 419390 五、發明説明() 體有機雜質。在習知之化學式過濾器’也因活性炭之吸附 性能隨著通氣時間增加而降低,在使用6個月後到達20 度。 其次,對疏水性沸石進行各種檢討。沸石之主要成分 係二氧化矽(Si02 )和氧化鋁(Al2〇3 ),其含有重量比 .和水分吸附量之關係已如使用圖11之說明所示。此外,對 於Si02/Al203係40之疏水性沸石,在25 t之環境所量測 對水之吸附等溫線圖如圖27所示。爲了比較,在圖27也 表示了活性炭對水之吸附等溫線圖。在相對濕度50%,活 性炭(g )對水之吸附量(cc )係llcc/g,而疏水性沸石 (g ) Si水之吸附量(cc )係0_03cc/g。 又,細孔徑6埃之親水性及疏水性沸石、細孔徑8埃 之親水性及疏水性沸石、以椰子殼爲原始原料之天然物系 活性炭、以石油瀝青爲原始原料之合成物系活性炭共6種 吸附劑爲對象,比較了對在無麈室環境中(23 °C、 40%RH )所含成爲表面污染之原因之微量有機物之吸附性 肯g。將各吸附劑〇.〇4g充塡成截面積0.15cm2之圓柱,將無 塵室之循環空氣流量設爲31/min。實驗條件如表3所示。 不管吸附劑之種類,充塡量、圓柱截面積、循環空氣流量、 循環空氣風速都一樣,但是由於各吸附劑粉末之大小或密 度不同,充塡密度、充塡體積、充塡層厚度、接觸時間隨 各種類而異。通過吸附劑後之31/min之空氣自容器本身流 入不產生氣體有機雜質之容積1公升之容器之流入口後’ 由流出口流出去。將剛洗淨後之無有機物污染之附氧化膜 45 (諳先Μ讀背面之注意事項再填寫本頁) *1Τ- 本紙張尺度過川巾國码家標华i CNS ) Λ4规格(2!0>·297公择) 經濟部中央標準局員工消費合作社印製 ^19390_^___ 五、發明説明() 矽晶片基板只放在該容器內20小時後量測接觸角。連續重 複(洗淨—放置20小時—量測接觸角洗淨^放置20小時 —量測接觸角—…)後,量測了各種吸附劑之吸附性能之 隨著間劣化。 吸附劑之種類 形狀、大小 充塡密度 (g/cc ) 充塡量 圓柱截面積 充塡體積 (CC ) 細孔徑6埃之 塊狀 親水性沸石 0.3〜 0.58 0.069 細孔徑6埃之 0.85mm 疏水性沸石 細孔徑8埃之 塊狀 0.04g 0.15m2 親水性沸石 0.30- 0.42 0.096 細孔徑8埃之 0.85mm 疏水性沸石 以椰子殼爲原 塊狀 11 始原料之天然 0.30 〜 0.36 0.11 物系活性碳 0.85mm 以石油瀝青爲 塊狀 原始原料之合 0.30 〜 0.52 0.078 成物系活性碳 0.85mm 46 本紙張尺度巾囡阀家悻绛i CNS ) Λ4規格(210/ 297公沒) (請先閱讀背面之注意事項再填寫本頁) ___Γ· -nn· nf^i !, _ -- -1-1 aLm _ A7 B7 4 ¢939(¾ 五、發明説明() 吸附劑之種類 充塡層厚度 (mm ) 循環空氣 流量 循環空氣 風速 接觸時間 (sec ) 細孔徑6埃之 親水性沸石 細孔徑6埃之 疏水性沸石 4.6 3.01/min 3.4m/s 0.0014 細孔徑8埃之 親水性沸石 細孔徑8埃之 疏水性沸石 6.5 0.0019 以椰子殼爲原 始原料之天然 物系活性碳 7.4 0.0022 以石油瀝青爲 原始原料之合 成物系活性碳 5.2 0.0016 對於各種吸附劑之接觸角之變化如圖28所示。此外, 晶片表面之剛洗淨後之接觸角之量測値係約3度。在圖 28,曲線440係將剛洗淨後之無有機物污染之附氧化膜矽 晶片曝露在對吸附劑送風前之無塵室空氣之情況,曲線441 係曝露在對具有細孔徑ό埃之親水性沸石之吸附劑送風後 (請先閱讀背面之注意事項再填寫本頁) 、-° 經濟部中央標準局員工消費合作社印製 木紙张尺度適出中國囚家標绛(C'NS ) Λ4况格(210Χ 297公;i ) ^19390 B\7 _ 五、發明説明() 之無麈室空氣之情況’曲線442係曝露在對具有細孔徑8 埃之親水性沸石之吸附劑送風後之無麈室空氣之情況’曲 線445係曝露在對具有細孔徑6埃之疏水性沸石之吸附劑 送風後之無麈室空氣之情況,曲線446係曝露在對具有細 孔徑8埃之疏水性沸石之吸附劑送風後之無麈室空氣之情 況,曲線443係曝露在對以天然物系活性炭爲主成分之吸 附劑送風後之無麈室空氣之情況,曲線444係曝露在對以 合成物系活性炭爲主成分之吸附劑送風後之無麈室空氣之 情況。 由圖28得知如下事項。 1. 在吸附性能上之順序係曲線446 (細孔徑8埃之疏水性 ' 沸石)>曲線442 (細孔徑8埃之親水性沸石)>曲線443 (天然物系活性炭)>曲線445 (細孔徑6埃之疏水性沸石) >曲線441 (細孔徑6埃之親水性沸石)>曲線444 (合成 物系活性炭)。合成物系活性炭特別差。 經濟部中央標準局員工消費合作社印掣 (請先閱讀背面之注意事項再填寫本頁) 2. 細孔徑6埃之親水性沸石(曲線441 )自送風時間超過 30小時附近開始,又細孔徑6埃之疏水性沸石(曲線445 ) 和天然物系活性炭(曲線443 )自送風時間超過50小時附 近開始,各自的吸附性能開始降低。 3. 細孔徑8埃之親水性沸石(曲線442 )到送風時間120 小時爲止,又細孔徑8埃之疏水性沸石(曲線446 )和合 成物系活性炭(曲線444 )到送風時間超過200小時爲止, 吸附性能不降低。 4. 在吸附性能不降低之使用初期,比較細孔徑6埃之親水 48 本纸張尺度適π中闲1¾掌標净(CNS ) Μ规格(2丨0/29?公筇) 經濟部中央標牟局員工消f合作社印掣 419390 A7 ____ B7 五、發明説明() " 性沸石(曲線441 )和細孔徑8埃之親水性沸石(曲線 442 ),相對於細孔徑6埃之親水性沸石(曲線441 )之 變化爲3度->7,8度,細孔徑8埃之親水性沸石(曲線442 ) 之變化爲3度->3.5度。同樣地,在吸附性能不降低之使用 初期,比較細孔徑ό埃之疏水性沸石(曲線445 )和細孔 徑8埃之疏水性沸石(曲線446 ),相對於細孔徑6埃之 疏水性沸石(曲線445 )之變化爲3度—6.4度,細孔徑8 埃之疏水性沸石(曲線446 )之變化爲3度—3.1度。得知 細孔徑8埃之親水性和疏水性沸石可大致完全地吸附並除 去潔淨裝置環境中所含成爲表面污染之原因之微量有機 物,而細孔徑ό埃之親水性和疏水性沸石有因無法吸附除 去而通過之成爲表面污染之原因之微量有機物。 5.細孔徑8埃之親水性和疏水性沸石(曲線442和440 ) 及天然物系活性炭(曲線443 )之吸附性能遠比細孔徑6 埃之親水性和疏水性沸石(曲線441和445 )及合成物系 活性炭(曲線444 )之吸附性能好。沸石無法吸附比細孔 徑大之分子。因此,用細孔徑δ埃之親水性和疏水性沸石 (曲線442和446 )可大致完全地吸附並除去潔淨裝置環 境中所含成爲表面污染之原因之微量有機物,這表示在圖 28之實驗對象之潔淨裝置環境中所含成爲表面污染之原因 之大半的微量有機物的分子大小係8埃以下。另一方面表 示,細孔徑6埃之親水性及疏水性沸石和合成物系活性炭 相比,雖然具有可大致滿足之吸附性能,但是有極少量因 無法吸附除去而通過之成爲表面污染之原因之微量有機 49 本紙張尺度適用屮國闪本掠磾K NS ) Λ4規格(2丨0〆]97公韙) II-------ο — I {請先閱讀背面之注項再填寫本頁) 訂"-- 經濟部中央標準局男工消f合作社印繁 419390 A7 B7 五、發明説明() 物’該通過之微量有機物的分子大小係6埃以上8埃以下。 其次,調查了本發明之潔淨裝置以溫度23。(:、相對濕 度50%運轉時之濕度控制性。爲了比較,調查了按照本發 明裝了具有疏水性沸石之過濾器之潔淨裝置、和除了將圖1 所示之過濾器更換爲將纖維狀活性炭和聚酯不織布之黏接 劑複合後製成球形之習知構造之化學式過濾器以外條件完 全相同之習知之潔淨裝置之濕度控制性。濕度感測器設於 通過進行除麈'調溫、調濕之單元型空調機和過濾器後之 外氣吸入迴路。依據該濕度感測器調節設於單元型空調機 內之調濕機之供水閥。爲了判定濕度控制性是否良好,在 按照本發明之潔淨裝置和習知之潔淨裝置內部也各自設置 了濕度感測器。又,相對於循環空氣量5000m3/min,外氣 吸入量設爲僅僅200m3/min 〇 . 在圖29表示量測結果。在具有習知構造之化學式過濾 器之潔淨裝置,因化學式過濾器易吸附通過空氣中之水 分,在安裝化學式過濾器後,活性炭吸附水分而達到平衡 狀態爲止之約2週期間內,潔淨裝置內部之相對濕度變爲 比設定値50%低5%之45%。而,在具有令固接了疏水性 沸石之蜂巢構造物之過濾器之按照本發明之潔淨裝置內 部,因幾乎不吸附通過空氣中之水分,相對濕度保持在設 定値50%。在LSI或LCD之製程’濕度降到低於設定値時, 在晶片或玻璃基板易發生靜電,那些產品表面發生微粒子 污染或元件發生靜電破壞,良率就降低。在具有習知構造 之化學式過濾器之潔淨裝置,在安裝過濾器後經過了約2 50 (請先閱讀背面之注意事項再填寫本頁) 訂 本紙張尺店適川中國阀家找举U,NS ) Λ4現格(2丨公跻) A7 B7 經濟部中央標隼局—工消費合作社印製 4 193 90 五、發明説明() 週,產品之良率就降低。可是’在按照本發明之具有過爐 器之潔淨裝置內部,自安裝過濾器後開始相對濕度就保持 在設定値,未發現產品之良率降低。 此外,如圖30所示,調查了設置了載持纖維狀活性炭 之習知之化學式過濾器450之潔淨裝置A和完全未設置如 化學式過濾器般之過濾器之潔淨裝置B這2種潔淨裝置 A、B都以溫度23 °C、相對濕度50%蓮轉時之濕度控制 性。這些潔淨裝置A、B在天花板部之供氣增壓451和地 板下面部之回氣增壓452彼此相通,但是除此以外的用隔 間453 (壁)隔開。又在圖30,濕度感測器454設於設置 了習知之化學式過濾器450之潔淨裝置A內。在潔淨裝置 A內設置進行閘氧化膜前製程之處理裝置450,在潔淨裝 置B內設置進行矽化物製程之處理裝置457 〇 在此,表4係美國之SEMATECH於1995年5月31 曰發表之刊載在 Technology Transfer #95052812A-TR 「Forecast of Airborne Molecular Contamination Limits for the 0.25 Micron High Performance Logic Process」之在 ' 0.25μιη製程(199S以後)所需的化學污染容許濃度 (ppt )。 51 (請先閱讀背面之注意事項再填寫本頁)Printed by the Consumer Standards Cooperative of the Central Bureau of Standards of the Ministry of Economic Affairs / 419390 V. Description of Invention () Organic impurities. The conventional chemical filter 'also decreases due to the increase in aeration time of activated carbon, and reaches 20 degrees after 6 months of use. Second, various reviews were conducted on hydrophobic zeolites. The main components of zeolite are silicon dioxide (Si02) and alumina (Al203). The relationship between the content of weight ratio and the amount of adsorbed water is as shown in the description using FIG. 11. In addition, for the hydrophobic zeolite of Si02 / Al203 series 40, the adsorption isotherm diagram of water measured in an environment of 25 t is shown in FIG. 27. For comparison, Fig. 27 also shows an adsorption isotherm diagram of activated carbon for water. At a relative humidity of 50%, the adsorption amount (cc) of activated carbon (g) to water is llcc / g, and the adsorption amount (cc) of hydrophobic zeolite (g) to Si water is 0 to 03cc / g. In addition, the hydrophilic and hydrophobic zeolite with a pore size of 6 angstroms, the hydrophilic and hydrophobic zeolite with a pore diameter of 8 angstroms, a natural activated carbon using coconut shell as a raw material, and a synthetic activated carbon using petroleum pitch as a raw material Six kinds of adsorbents were used to compare the adsorptive capacity of trace organic substances contained in a chamber-free environment (23 ° C, 40% RH), which are the cause of surface contamination. 0.04 g of each adsorbent was filled into a cylinder having a cross-sectional area of 0.15 cm2, and the circulating air flow rate of the clean room was set to 31 / min. The experimental conditions are shown in Table 3. Regardless of the type of the adsorbent, the filling amount, the cross-sectional area of the cylinder, the circulating air flow rate, and the circulating air velocity are the same, but due to the size or density of each adsorbent powder, the filling density, filling volume, filling layer thickness, contact Time varies by class. After passing through the adsorbent, 31 / min of air flows from the container itself into the inlet of the container with a volume of 1 liter that does not generate gaseous organic impurities, and then flows out from the outlet. The oxide film 45 with no organic pollution immediately after washing (Please read the precautions on the back before filling out this page) * 1Τ- This paper is standardized with Sichuan towel country code and house standard China i CNS) Λ4 specification (2! 0 > · 297 public choice) Printed by the Consumer Cooperatives of the Central Bureau of Standards of the Ministry of Economic Affairs ^ 19390 _ ^ ___ V. Description of the Invention () The silicon wafer substrate was placed in the container for 20 hours and the contact angle was measured. After repeated (washing-leaving for 20 hours-measuring the contact angle washing ^ leaving for 20 hours-measuring the contact angle-...), the adsorption performance of various adsorbents was measured to deteriorate over time. Type and shape of adsorbent Filling density (g / cc) Filling volume Cylindrical cross-sectional area Filling volume (CC) Bulk hydrophilic zeolite with a pore size of 6 angstroms 0.3 to 0.58 0.069 0.85 mm with a pore diameter of 6 angstroms Hydrophobicity Zeolite with a pore size of 8 angstroms 0.04g 0.15m2 Hydrophilic zeolite 0.30-0.42 0.096 Fine pore size of 8 angstroms 0.85mm Hydrophobic zeolite with coconut shell as the original block 11 Natural 0.30 ~ 0.36 0.11 Natural activated carbon 0.85 mm 0.30 ~ 0.52 0.078 with petroleum tar as raw raw material 0.85mm of activated carbon 46 paper size paper towel valve 悻 绛 i CNS) 4 size (210/297) (please read the back Please fill in this page for the matters needing attention) ___ Γ · -nn · nf ^ i!, _--1-1 aLm _ A7 B7 4 ¢ 939 (¾ V. Description of the invention () Type of adsorbent filling layer thickness (mm) Circulating air flow Circulating air wind speed contact time (sec) Hydrophilic zeolite with a pore size of 6 angstroms and hydrophobic zeolite with a pore diameter of 6 angstroms 4.6 3.01 / min 3.4m / s 0.0014 Hydrophilic zeolite with a pore diameter of 8 angstroms and a pore diameter of 8 angstroms Hydrophobic zeolite 6.5 0.0019 Natural type activated carbon with coconut shell as raw material 7.4 0.0022 Synthetic type activated carbon with petroleum pitch as raw material 5.2 0.0016 The change in contact angle of various adsorbents is shown in Figure 28. In addition, The measurement of the contact angle of the wafer surface immediately after cleaning is about 3 degrees. In Figure 28, curve 440 is that the silicon wafer with an oxide film without organic pollution immediately after cleaning is exposed to the surface of the wafer before the adsorbent is blown. For the air in the clean room, curve 441 is exposed to the air after the adsorbent of hydrophilic zeolite with a fine pore diameter (please read the precautions on the back before filling this page),-° Consumers Cooperative of the Central Standards Bureau of the Ministry of Economic Affairs The scale of printed wood paper fits the standard of Chinese prisoner's standard (C'NS) Λ4 case (210 × 297 male; i) ^ 19390 B \ 7 _ V. Description of the invention () The condition of chamber-free air 'curve 442 The case of exposure to air without a chamber after supplying air to an adsorbent with a hydrophilic zeolite having a fine pore size of 8 Angstrom 'curve 445 Of air In addition, curve 446 is exposed to the chamberless air after the air is supplied to the adsorbent having a hydrophobic zeolite with a pore diameter of 8 angstroms, and curve 443 is exposed to the air after the air is supplied to an adsorbent containing natural activated carbon as the main component. In the case of chamber-free air, curve 444 is exposed to the chamber-free air after the air is supplied to the adsorbent mainly composed of synthetic activated carbon. The following matters are known from FIG. 28. 1. The order of adsorption performance is curve 446 (hydrophobic zeolite with a fine pore size of 8 angstroms) > curve 442 (hydrophilic zeolite with a fine pore diameter of 8 angstroms) > curve 443 (natural activated carbon) > curve 445 (Hydrophobic zeolite with a pore size of 6 angstroms) > Curve 441 (Hydrophilic zeolite with a pore diameter of 6 Angstroms) > Curve 444 (Synthetic activated carbon). Synthetic activated carbon is particularly poor. Printed by the Consumer Cooperatives of the Central Standards Bureau of the Ministry of Economic Affairs (please read the precautions on the back before filling this page) 2. Hydrophilic zeolite (curve 441) with a pore size of 6 angstroms has been around for 30 hours since the air supply time, and the pore size is 6 Since the zeolite hydrophobic (Curve 445) and natural carbon (Curve 443) of Aezhi have been around for more than 50 hours, the adsorption performance of each has begun to decrease. 3. Hydrophilic zeolite (curve 442) with a pore size of 8 Angstroms until the air supply time is 120 hours, and hydrophobic zeolite (curve 446) with a pore size of 8 Angstroms and synthetic activated carbon (curve 444) until the air supply time exceeds 200 hours. , Adsorption performance does not decrease. 4. In the early stage of use, when the adsorption performance is not reduced, the hydrophilic 48 papers with a pore size of 6 angstroms are compared. The size of the paper is moderate and the size is 1 ¾ palm standard net (CNS). M specifications (2 丨 0/29? Cm). Employees of the Mou Bureau eliminate the cooperatives ’seals 419390 A7 ____ B7 V. Description of the invention () " Zeolite (curve 441) and hydrophilic zeolite (curve 442) with a pore size of 8 angstroms, compared to hydrophilic zeolite with a pore diameter of 6 angstroms (Curve 441) has a change of 3 degrees-> 7,8 degrees, and a hydrophilic zeolite (curve 442) having a pore size of 8 angstroms has a change of 3 degrees-> 3.5 degrees. Similarly, in the initial use period when the adsorption performance does not decrease, the hydrophobic zeolite with a pore diameter of Angstrom (curve 445) and the hydrophobic zeolite with a pore diameter of 8 Angstrom (curve 446) are compared with the hydrophobic zeolite with a pore diameter of 6 Angstrom ( The change of curve 445) is from 3 degrees to 6.4 degrees, and the change of hydrophobic zeolite (curve 446) with a pore diameter of 8 angstroms is from 3 degrees to 3.1 degrees. It is known that hydrophilic and hydrophobic zeolites with a pore size of 8 angstroms can almost completely adsorb and remove trace organic substances that cause surface contamination in the environment of a clean device. Traces of organic matter that are removed by adsorption and cause surface contamination. 5. The adsorption performance of hydrophilic and hydrophobic zeolites with pore diameters of 8 angstroms (curves 442 and 440) and activated carbon (curve 443) is much better than that of hydrophilic and hydrophobic zeolites with pores of 6 angstroms (curves 441 and 445). And synthetic activated carbon (curve 444) has good adsorption performance. Zeolites cannot adsorb molecules larger than the pore diameter. Therefore, the hydrophilic and hydrophobic zeolites (curves 442 and 446) with a pore diameter of δ angstroms can substantially completely adsorb and remove the trace organic substances contained in the clean device environment, which cause the surface contamination. This is shown in Figure 28 as the experimental object. The molecular size of most of the trace organic substances contained in the clean device environment, which causes surface contamination, is 8 angstroms or less. On the other hand, it is shown that although the hydrophilic and hydrophobic zeolite with a pore size of 6 Angstroms has approximately satisfactory adsorption performance compared with synthetic activated carbon, a small amount of it passes through because it cannot be removed by adsorption, which causes surface contamination. Trace organic 49 The paper size is applicable to the national flash version (K NS) Λ4 specification (2 丨 0〆) 97mm 韪 II ------- ο — I {Please read the note on the back before filling in this Page) Order " --- Male Workers of the Central Bureau of Standards of the Ministry of Economic Affairs, Cooperatives and Cooperatives, Yinfan 419390 A7 B7 V. Description of the Invention () Objects The molecular size of the trace organic matter passing is 6 angstroms or more and 8 angstroms or less. Next, the cleaning device of the present invention was investigated at a temperature of 23. (:, Humidity controllability at 50% relative humidity operation. For comparison, a cleaning device equipped with a filter having a hydrophobic zeolite according to the present invention was investigated, and the filter shown in FIG. 1 was replaced with a fiber-like filter. The activated carbon and the polyester non-woven adhesive are compounded to form a spherical chemical filter with a conventional structure. The humidity controllability of a conventional clean device is the same except for a conventional filter. The humidity sensor is set by The humidity-adjusting unit type air conditioner and the outside air suction circuit after the filter. Adjust the water supply valve of the humidity regulator installed in the unit type air conditioner according to the humidity sensor. In order to determine whether the humidity control is good, The invented clean device and the conventional clean device are each provided with a humidity sensor. Also, the external air intake amount is set to only 200 m3 / min with respect to the circulating air amount of 5000 m3 / min. The measurement results are shown in FIG. 29. In the cleaning device of the chemical filter with a conventional structure, the chemical filter easily absorbs moisture in the air. After installing the chemical filter, the activated carbon absorbs Within about 2 weeks until the water reaches an equilibrium state, the relative humidity inside the clean device becomes 45% which is 5% lower than the set value of 50%. In addition, a filter having a honeycomb structure to which a hydrophobic zeolite is fixed is filtered. In the clean device of the device according to the present invention, the relative humidity is kept at a set value of 50% because it hardly absorbs moisture in the air. When the humidity of the LSI or LCD process drops below the set value, the wafer or glass substrate Static electricity is prone to occur, and the yield of those products is reduced due to particle contamination on the surface of the product or electrostatic damage to the components. After cleaning the filter device with a conventional chemical filter, about 2 50 (please read the first Please fill in this page again for the matters needing attention) The paper rule shop Shichuan Chinese valve house is looking for U, NS) Λ4 is now (2 丨 coming) A7 B7 Printed by the Central Bureau of Standards of the Ministry of Economy—Printed by Industrial and Consumer Cooperatives 4 193 90 5 2. Description of the invention () Week, the yield of the product will decrease. However, in the clean device with a furnace according to the present invention, the relative humidity has been maintained at the set value since the filter was installed, and no decrease in the yield of the product was found. In addition, as shown in FIG. 30, two types of cleaning devices A, a cleaning device A provided with a conventional chemical filter 450 carrying a fibrous activated carbon and a cleaning device B provided with no filter like a chemical filter at all, were investigated. Both B and B are humidity-controllable when the temperature is 23 ° C and the relative humidity is 50%. These cleaning devices A and B are connected to each other by a supply air booster 451 on the ceiling portion and a return air booster 452 on the lower portion of the floor, but are separated by a partition 453 (wall). Also in Fig. 30, a humidity sensor 454 is provided in a cleaning device A provided with a conventional chemical filter 450. A processing device 450 for performing the gate oxide film pre-processing process is provided in the cleaning device A, and a silicide processing device 457 is provided for the cleaning device B. Here, Table 4 is published by SEMATECH in the United States on May 31, 1995. Published in Technology Transfer # 95052812A-TR "Forecast of Airborne Molecular Contamination Limits for the 0.25 Micron High Performance Logic Process" in the '0.25μιη process (after 199S) required chemical pollution allowable concentration (ppt). 51 (Please read the notes on the back before filling this page)
本紙張尺戍適用中阀囡家棣準(CNS > Λ4規格(210 y 2〇7公楚) J 4193 90 五、發明説明() 表4 製程 最長等待時間 酸 鹼 有機物 摻雜劑 閘氧化膜前 4 13,000 13,000 1,000 0.1 製程 50% 50% 75% 90% 矽化物製程 1 180 13,000 35,000 1,000 50% 25% 75% 75% 配線 24 5 13,000 2,000 100,000 50% 25% 75% 75% 光鈾刻 2 10,000 1,000 100,000 10,000 75% 90% 50% 50% Ί1-------- (請先閱讀背面之注意事項再填寫本頁) 經濟部中央標率局貝工消费合作社印製 在表4中,附底線處係容許値嚴格,一定需要控制之 情況。又,%値係成爲容許値設定依據之資料的可靠性。 得知對於有機物,在閘氧化膜前製程需要1 ppb、在配線 製程需要2 ppb之嚴格控制,而在砍化物製程容許35ppb、 在光蝕刻容許lOOppb之高濃度,不需要控制環境中之有機 物。 在圖31表示圖30所示潔淨裝置a、B之量測結果。 .在在具有習知構造之化學式過濾器450之潔淨裝置A,化 S式過爐器45〇易吸附通過空氣中之水分。可是,因在潔 淨裝置A內設置濕度控制所需之濕度感測器454,在安裝 化學式過濾器後,活性炭吸附水分而達到平衡狀態爲止之 約2週期間內’自吸入外氣用之單元型空調機460只過度 加濕被化學式過濾器450吸附而失去之水分量。因而,用 52 本紙張尺度.適州中囷围家標辛(CNS ),\4规格(210X2y7公弟) 經濟部中央標準局貝工消f合作社印製 419390 A7 广 __.67---- 五、發明説明() 濕度感測器454所量測潔淨裝置A之相對濕度’在安裝化 學式過濾器450後開始保持在設定値50%。可是用濕度感 測器455量測了完全未設置如化學式過濾器般之過濾器之 潔淨裝置B時,自單元型空調機460過度加濕之影響原封 不動地出現,在安裝過濾器後經過了約2週,潔淨裝置B 內之相對濕度變爲比設定値50%高5°/。之55%。因而’和 相對濕度50°/。之情況相比,發現因在晶片表面過度吸附水 分而形成氧化膜之產品品質上之不良點。因此’將潔淨裝 置A之習知構造之化學式過濾器更換爲令疏水性沸石固接 之蜂巢構造物之過濾器後,潔淨裝置B內之相對濕度變成 保持在設定値,完全未發生上述之不良。 其次,在按照本發明之潔淨裝置,比較了在令固接了 疏水性沸石之蜂巢構造物之過濾器之下游側安裝只由不產 生氣體有機雜質之材料構成之除去粒狀雜質之除去粒子之 過濾器之情況,和過濾器構成材料會產生氣體有機雜質之 習知之除去粒狀雜質之除去粒子之過濾器之情況。在潔淨 裝置內放置了剛洗淨後之無有機物污染之附氧化膜矽晶片 基板。然後分別量測剛洗淨後和放置3天後之接觸角,求 放置3天後之接觸角之增加量。在安裝了只由不產生氣體 有機雜質之材料構成之除去粒子之過濾器之情況,放置3 天後晶片表面之接觸角由3.0度變爲4.0度,幾乎不增加。 這是由於在吸附層,成爲基板表面污染之原因幾乎都被吸 附並除去,而且配置在其下游側之除去粒子之過濾器不產 生氣體有機雜質。而,在過濾器構成材料會產生氣體有機 53 (請先閱讀背面之注意事項再填寫本頁) --I ---- 本紙疮尺度適ϋ國W掌疗办(CNS ) Λ4规格(2Κ),297公箱) 4t9390i A7 B7 五、發明説明() 雜質之習知之除去粒子之過濾器之情況,受到來自過濾器 構成材料之逸脫氣體之影響,放置3天後晶片表面之接觸 角由3.0度變爲5.0度,增加了,但是極少。 其次,在無麈室中,在各自使用粒狀活性炭、纖維狀 活性炭之市面上之化學式過濾器2種和使用離子交換纖維 之化學式過濾器所處理之無麈室空氣以及利用本發明之過 濾器所處理之無塵室空氣共4種環境中,量測附氧化膜砍 晶片表面之接觸角之隨著間變化。其量測結果如圖32所 示。本發明之過濾器之製造方法如下所示。在將作爲無機 吸附劑之有效細孔徑8埃、Si02/Al203係40之疏水性沸石 之4μιη之粉末和作爲該無機物之高嶺土之3 μιη之粉末混合 後,和作爲無機系固接輔助劑之矽膠一起分散之黏結劑中 浸入上述之多孔性蜂巢構造物後並乾燥,形成第1吸附 層。其次,在將作爲具有吸附氣體有機雜質性質之無機物 之有效細孔徑主要分布在20埃〜1〇〇〇埃之活性白黏土之 3pm之粉末和作爲無機系固接輔助劑之砂膠一起分散之黏 結劑中再浸入形成了第1吸附層之上述之多孔性蜂巢構造 物後並乾燥,形成第2吸附層。 由圖32之結果得知如下事項。離子交換纖維本來係用 以吸附並除去水溶性有機雜質的,無法吸附有機物,反而 產生氣體有機物。發現放置1天接觸角增加紛10度。本來 應防止有機物表面污染之活性炭過濾器2種,放置1天接 觸角增加約10度’結果表示表面污染防止效果幾乎沒有。 在利用活性炭之2種化學式過濾器沒有效果之原因係因在 54 本紙張尺度過川中® 1^惊準(C&s ) Μ規格(公箱) (請先閲讀背面之注意事項再填寫本頁) -卜^--The paper size is suitable for the standard of Chinese valve (CNS > Λ4 specification (210 y 207)) J 4193 90 V. Description of the invention () Table 4 The longest waiting time of the process acid-base organic dopant gate oxide film Top 4 13,000 13,000 1,000 0.1 Process 50% 50% 75% 90% Silicide process 1 180 13,000 35,000 1,000 50% 25% 75% 75% Wiring 24 5 13,000 2,000 100,000 50% 25% 75% 75% Light uranium engraving 2 10,000 1,000 100,000 10,000 75% 90% 50% 50% Ί1 -------- (Please read the notes on the back before filling out this page) The Central Standards Bureau of the Ministry of Economic Affairs, Shellfish Consumer Cooperative, is printed in Table 4, Attached bottom line is the case where strict tolerance is required and must be controlled. In addition, %% is the reliability of the data used to set the allowable threshold. It is learned that for organic matter, the process before the gate oxide film requires 1 ppb, and the wiring process requires 2 The ppb is strictly controlled, while 35 ppb is allowed in the chopping process and 100 ppb is allowed in the photo-etching process. There is no need to control the organic matter in the environment. Fig. 31 shows the measurement results of the clean devices a and B shown in Fig. 30. In chemistry with a known structure The clean device A of the filter 450 and the S-type furnace 45 are easy to absorb the moisture in the air. However, because the humidity sensor 454 required for humidity control is installed in the clean device A, after the chemical filter is installed During the period of about 2 weeks until the activated carbon adsorbed moisture and reached equilibrium, 460 unit-type air conditioners for inhaling outside air had only excessively humidified the amount of water lost by being absorbed by the chemical filter 450. Therefore, 52 paper sizes were used. .Shizhou Zhongliwei Family Standard Xin (CNS), \ 4 specifications (210X2y7 male brother) Printed by the Central Standards Bureau of the Ministry of Economic Affairs, Bei Gong Xiao F Cooperative 419390 A7 Guang __. 67 ---- V. Description of the invention () The relative humidity of the clean device A measured by the humidity sensor 454 is maintained at a setting of 値 50% after the chemical filter 450 is installed. However, the humidity sensor 455 was used to measure the absence of a filter like a chemical filter. In the clean device B of the air conditioner, the effect of excessive humidification from the unit type air conditioner 460 appeared intact. After about 2 weeks after the filter was installed, the relative humidity in the clean device B became higher than the set 値 50% 5 ° /。 55%. Because 'Compared to the case of relative humidity of 50 ° /., It is found that the quality of the product that has formed an oxide film due to excessive adsorption of moisture on the wafer surface. Therefore,' replace the chemical filter of the conventional structure of the cleaning device A with a After the filter of the honeycomb structure to which the hydrophobic zeolite was fixed, the relative humidity in the cleaning device B was maintained at the set value, and the above-mentioned defects did not occur at all. Next, in the cleansing device according to the present invention, it is compared to install particulate-removing particulate-removing particulate-removing particles composed of a material that does not generate gaseous organic impurities on the downstream side of a filter having a honeycomb structure to which hydrophobic zeolite is fixed. In the case of a filter, and in the case where a filter constituting material is conventionally known to generate gaseous organic impurities, a particulate-removing filter is known. A silicon wafer substrate with an oxide film without organic contamination immediately after cleaning was placed in the cleaning device. Then measure the contact angles immediately after washing and after 3 days of standing, and find the increase in the contact angle after 3 days of standing. In the case where a particle-removing filter composed of a material that does not generate gaseous organic impurities is installed, the contact angle on the surface of the wafer changes from 3.0 degrees to 4.0 degrees after being left for 3 days, with little increase. This is because the cause of contamination on the surface of the substrate in the adsorption layer is almost absorbed and removed, and the particle removing filter disposed on the downstream side does not generate gaseous organic impurities. However, the filter constituent material will generate gas organic 53 (Please read the precautions on the back before filling out this page) --I ---- The paper sores are suitable for the country W Palm Therapy Office (CNS) Λ4 Specification (2K) (297 boxes) 4t9390i A7 B7 V. Description of the invention () The filter of particles known as impurities is affected by the escaped gas from the material constituting the filter. The contact angle of the wafer surface after 3 days is 3.0 The degree becomes 5.0 degrees, which increases, but it is rare. Next, in the ballastless chamber, there are two types of chemical filters on the market using granular activated carbon and fibrous activated carbon, and the air of the chamberless air treated by the chemical filter using ion exchange fiber, and the filter using the present invention. In the four kinds of environments in which the clean room air is processed, the contact angle of the surface of the wafer with an oxide film is measured to change with time. The measurement results are shown in Figure 32. The manufacturing method of the filter of this invention is shown below. After mixing an effective pore diameter of 8 angstroms as an inorganic adsorbent, a powder of 4 μm of a hydrophobic zeolite of Si02 / Al203 series 40 and a powder of 3 μm of a kaolin as the inorganic substance, and a silicone gel as an inorganic fixing aid The above-mentioned porous honeycomb structure was immersed in the dispersed adhesive together and dried to form a first adsorption layer. Secondly, the active pores with an effective pore size of inorganic substances having the property of adsorbing gas and organic impurities are mainly distributed at 3 pm of activated white clay, and powder of 3 pm is dispersed together with mortar as an inorganic fixing aid. The adhesive is further immersed in the porous honeycomb structure having the first adsorption layer formed thereon, and then dried to form a second adsorption layer. The results shown in FIG. 32 reveal the following. Ion exchange fibers were originally used to adsorb and remove water-soluble organic impurities. They were unable to adsorb organic matter, but instead produced gaseous organic matter. It was found that the contact angle increased by 10 degrees after being placed for one day. There are two types of activated carbon filters that should prevent surface contamination of organic materials. The contact angle is increased by about 10 degrees after being left for one day. The reason why the two types of chemical filters using activated carbon do not work is because the paper size has passed through Chuanzhong ® 1 ^ surprise (C & s) Μ specifications (public box) (Please read the precautions on the back before filling this page ) -Bu ^-
Q 4193 90 at B7 五、發明説明() 化學式過濾器之構成材料含有黏結劑、固接輔助劑、密封 劑等表面有機污染物質,原本的活性炭吸附效果被本身構 成材料之逸脫氣體抵銷。而在本發明之過濾器,因吸附過 濾件不會產生氣體有機雜質,不污染有機物表面,接觸角 也不增加。 其次,在支撑物之表面將疏水性沸石作爲第1吸附 層、將活性白黏土作爲第2吸附層固接之蜂巢構造物之過 濾器中使分別包含數百ppb至數ppb之DOP、DBP、 BHT、五聚物之矽氧烷(D5 )之無麈室空氣流過時用氣 相色譜-質譜聯用儀(GC-MS )量測並比較設於過濾器之 上游側和下游側之各自的環境中之矽晶片表面之有機物污 染量,評價表面污染防止效果。其結果如表5所示。 (請先閱讀背面之注意事項再填寫本頁) 訂_ 經濟部中央標辛局員工消f合作社印製 表5 氣體有機雜質之 種類 本發明之過濾器 只具有以高嶺土爲黏接劑之 第1吸附層之過爐器 DOP 99%以上 95% DBP 99%以上 93% BHT 85% 40% D5 90% 43% 使用4英吋之p型矽晶片評價。在過濾器之上游側和 下游側各自曝露洗淨後之晶片後,量測了表面污染。使用 升溫逸脫氣體裝置和氣相色譜質-譜聯用儀之組合分析、量 55 ______ 本紙張尺度適川十國1¾家標卑((,NS ) Λ4規格(2丨〇Ζ:297公淹) 經濟部中央標準局貝工消費合作社印製 419390 A7 B7___ 五、發明説明() 測附著在晶片表面之有機物。又’依據氣相色譜按照如下 所示求表面污染防止率。 表面污染防止率=(1- ( B/A ) ) xlOO (%) Λ :自上游側之晶片表面所偵測到表面有機污染物質 之Peak之面積 B :自上游側之晶片表面所偵測到表面有機污染物質 之Peak之面積 過濾器例如如圖6所示,具有在相鄰之波形片之間夾 住無凹凸之薄板片之構造。過濾器之通氣方向之厚度係 10cm、空氣流速係〇.6m/s、向過濾器送風之所處理空氣接 觸之過濾器之每單位體積之薄片總面積係3000m2/xn3。本 發明之過濾器係,在將3μιη之高嶺土(高嶺礦物之一種) 之粉末作爲黏接劑和細孔徑8埃、大小3-4μηι之疏水性沸 石之粉末混合後,將矽膠作爲無機系固接輔助劑而令一起 分散之黏結劑中浸入上述多孔性蜂巢構造物後乾燥’將疏 水性沸石作爲第1吸附層固接在蜂巢構造物。還在使數μιη 之粉末狀之酸處理蒙脫石(活性白黏土)之黏接劑和係無 機系固接輔助劑之矽膠一起分散之黏結劑中浸入形成了第 1吸附層之多孔性蜂巢構造物後乾燥,固接成第2吸附層。 第1吸附層之厚度係,其重量成分比係疏水性沸 石:高嶺土:二氧化矽=70% : 25% : 5%,又第2吸附層 之厚度係ΙΟμιη,其重量成分比係疏水性沸石:二氧化石夕 =87% : 13°/。。過濾器整體之密度係230g/l,其中吸附層所 占密度係90g/l (過濾器整體之39%)。此外’在表5中爲 56 _ 本紙張尺度適川中1¾肉家枕準(C.NS ) Λ4规格(U0〆297公f ) (請先鬩讀背而之注項再填寫本頁)Q 4193 90 at B7 V. Description of the invention () The constituent materials of chemical filters contain surface organic pollutants such as adhesives, fixing aids, sealants, etc. The original activated carbon adsorption effect is offset by the outgassing of the constituent materials. In the filter of the present invention, since the filter element is adsorbed, no gaseous organic impurities are generated, the surface of the organic matter is not polluted, and the contact angle is not increased. Next, the filter of the honeycomb structure to which the hydrophobic zeolite is used as the first adsorption layer and the activated white clay is used as the second adsorption layer on the surface of the support is composed of DOP, DBP, BHT and pentamer of siloxane (D5) were measured with a gas-chromatograph-mass spectrometer (GC-MS) while passing through the chamber-free chamber air and compared with each of the filters provided on the upstream and downstream sides of the filter. The amount of organic contamination on the surface of the silicon wafer in the environment to evaluate the effect of preventing surface contamination. The results are shown in Table 5. (Please read the precautions on the back before filling this page) Order _ Printed by the staff of the Central Standards Bureau of the Ministry of Economic Affairs, printed by co-operative society 5 Types of gaseous organic impurities The filter of the present invention only has No. 1 with kaolin as the adhesive Adsorption layer furnace DOP over 99% 95% DBP over 99% 93% BHT 85% 40% D5 90% 43% Evaluation using a 4-inch p-type silicon wafer. After the cleaned wafers were exposed on the upstream and downstream sides of the filter, surface contamination was measured. Analysis using a combination of a temperature-evolving escaped gas device and a gas chromatograph mass spectrometer, quantity 55 ______ This paper scale is suitable for Sichuan, Shikoku, 1¾ family standard ((, NS) Λ4 specification (2 丨 〇Z: 297) Printed by the Central Standards Bureau of the Ministry of Economic Affairs, Shellfish Consumer Cooperative, 419390 A7 B7___ 5. Description of the invention () Measure the organic matter attached to the surface of the wafer. Also, based on the gas chromatography, find the surface pollution prevention rate as shown below. Surface pollution prevention rate = ( 1- (B / A)) x100 (%) Λ: Area of Peak of surface organic pollutants detected from the surface of the wafer on the upstream side B: Peak of surface organic pollutants detected from the surface of the wafer on the upstream side For example, as shown in FIG. 6, the area filter has a structure in which thin sheets without unevenness are sandwiched between adjacent corrugated sheets. The thickness of the filter in the ventilation direction is 10 cm, and the air velocity is 0.6 m / s. The total area of flakes per unit volume of the filter in contact with the treated air supplied by the filter is 3000m2 / xn3. The filter of the present invention uses 3 μm of powder of kaolin (a kind of kaolin mineral) as a binder and fine 8 Aperture After mixing the powder of hydrophobic zeolite with a size of 3-4 μm, the silica gel is used as an inorganic fixing aid and the dispersed adhesive is immersed in the porous honeycomb structure and dried. The hydrophobic zeolite is used as the first adsorption layer. It is connected to the honeycomb structure. It is also immersed in a powdered acid-treated montmorillonite (reactive white clay) adhesive with several μιη and an inorganic adhesive that is used as an adhesive to disperse the adhesive. The porous honeycomb structure of the adsorption layer is dried and fixed to form a second adsorption layer. The thickness of the first adsorption layer is based on the weight component ratio of hydrophobic zeolite: kaolin: silicon dioxide = 70%: 25%: 5% The thickness of the second adsorption layer is 10 μιη, and its weight component ratio is hydrophobic zeolite: stone dioxide = 87%: 13 ° / .. The density of the entire filter is 230 g / l, and the density of the adsorption layer is 90g / l (39% of the total filter). In addition, '56 in Table 5 _ This paper size is suitable for Sichuan Chuan 1¾ Butcher Pillow Standard (C.NS) Λ4 specification (U0〆297mm f) (Please read first (Please fill in this page for the back note)
419390 at Β7 五、發明説明() 了比較,也一倂表示對於將3 μιη之高嶺土之粉末作爲黏接 劑和上述有效細孔徑8埃之疏水性沸石之粉末混合後,將 矽膠作爲無機系固接輔助劑而令一起分散之黏結劑中浸入 上述多孔性蜂巢構造物後乾燥所製造之過濾器之量測結 果。高嶺土之通氣孔之主要的大小係1000埃以上,幾乎沒 有物理吸附的能力。而,活性白黏土之有效細孔徑主要分 布在20埃〜1000埃,物理吸附性能和活性炭相比,並無遜 色。該過濾器之蜂巢構造物之形狀、通氣條件等和表5所 示本發明之過濾器的完全相同,不同點係在蜂巢構造物之 表面固接的係和本發明完全相的之第1吸附層,但是未具 有相當於本發明之第2吸附層(活性白黏土層)的。由圖5 明白,自潔淨裝置內之基板表面所偵測到之表面有機污染 物之中量最大之種類之DOP和DBP,因其分子大小比8 埃小,在黏接劑之物理吸附性能不太好,也只靠疏水性沸 石之吸附性能吸附並除去。可是,對於ΒΗΤ或五聚物之矽 氧烷(D5 ),因其分子大小比8埃大,用疏水性沸石無 法除去,其吸附除去不得不仰賴具有物理吸附性能之第2 吸附層。 娌濟部中央標準局員工消費合作社印焚 {請先Μ讀背面之注^η項再填寫本頁) 其次,比較了按照本發明所製造之各種型式之過濾 器、只使用了疏水性沸石之過濾器、以及將第1吸附層和 第2吸附層對支撐物之固接順序對調之構造和本發明不同 之2種比較例之過濾器。其結果如表6所示。 57 419390 五、發明説明() 表6 氣體狀有 機雜質之 種類 本發明 A 只使用疏水 性沸石之過 濾器 本發明 B 本發明 C 比較例 D 比較例 E DOP 98% 95% 98% 99% 以上 95% 98% DBP 98% 95% 98% 99% 以上 95% 98% BHT 85% 30% 60% 85% 30% 60% D5 90% 35% 65% 90% 35% 65% (請先閱讀背面之注意事項再填寫本頁) 在表6,本發明A係第1吸附層由沸石、第2吸附層 由酸處理蒙脫石之黏接劑構成之蜂巢構造物之過濾器。第1 吸附層配置在支撐物側,第2吸附層配置在接近氣流側。 本發明B係使沸石和酸處理蒙脫石之黏接劑與係無機系固 接輔助劑之氧化鋁溶膠混合後在蜂巢構造物之表面形成了 吸附層之過濾器。本發明C係將酸處理蒙脫石之黏接劑在 本發明B之過濾器表面形成第2吸附層之過濾器。只使用 疏水性沸石之過濾器在蜂巢構造物之表面只形成沸石之吸 附層。比較例D係將本發明A之第1吸附層和第2吸附層 對支撐物之固接順序對調之過濾器,係第1吸附層由酸處 理蒙脫石之黏接劑、第2吸附層由沸石構成之蜂巢構造物 之過濾器。比較例E係將本發明C之第1吸附層和第2吸 附層對支撐物之固接順序對調之過濾器,係第1吸附層由 58 本纸張尺度適用中國1¾家標卒(CNS ) Λ4規格(公煃) 經濟部中炎標隼局員工消费合作社印製 419390 五、發明説明() 酸處理蒙脫石之黏接劑、第2吸附層由沸石和酸處理蒙脫 石之黏接劑構成之蜂巢構造物之過濾器。 在圖33〜38將這些過濾器之吸附層之構造放大,分別 以立體圖(a )和剖面圖(b )表示。這些圖33〜38係在 槪念上以模式圖表示了將如圖9或圖15所示之吸附層部分 地切出成以吸附層之厚度爲高度之圓筒形、係位於該圓筒 內之參與吸附之細孔之微小孔或中間孔之分布狀況。此 外,在這些圖33〜38省略了支撐物。本發明A如圖33所 示,在第1吸附層551形成沸石之約8埃之細孔’在第2 吸附層552形成酸處理蒙脫石之約15〜300埃之細孔。只使 用疏水性沸石之過濾器如圖34所示,在吸附層553形成沸 石之約8埃之細孔。本發明B圖35示,在吸附層554形成 沸石之約δ埃之細孔和酸處理蒙脫石之約15〜300埃之細 孔。本發明C如圖36所示,在第1吸附層555形成沸石之 約8埃之細孔和酸處理蒙脫石之約15〜300埃之細孔,在第 2吸附層556形成酸處理蒙脫石之約15〜300埃之細孔。而, 比較例D如圖37所示,在第1吸附層560形成酸處理蒙脫 石之約15〜300埃之細孔,在第2吸附層561形成沸石之約 8埃之細孔。比較例Ε如圖38所示,在第1吸附層562形 成酸處理蒙脫石之約15〜300埃之細孔,在第2吸附層563 形成沸石之約8埃之細孔和酸處理蒙脫石之約15〜300埃之 細孔。 對於這些過濾器和前面一樣調查了表面污染防止率之 結果,本發明之過濾器和只用疏水性沸石構成之過爐器相 59 -β (請先閱讀背面之注意事項再填寫本頁)419390 at Β7 V. Explanation of the invention () The comparison also shows that the powder of 3 μm kaolin is used as a binder and the powder of the hydrophobic zeolite with an effective pore diameter of 8 angstroms is mixed, and the silica gel is used as an inorganic fixing agent. The measurement result of the filter manufactured by immersing the porous honeycomb structure with the adhesive dispersed together with the auxiliary agent and drying it. The main size of the kaolin vent holes is more than 1000 angstroms, and there is almost no physical adsorption capacity. However, the effective pore size of activated white clay is mainly distributed in the range of 20 angstroms to 1000 angstroms, and the physical adsorption performance is not inferior to that of activated carbon. The shape and aeration conditions of the honeycomb structure of the filter are exactly the same as those of the filter of the present invention shown in Table 5. The difference is that the system fixedly attached to the surface of the honeycomb structure is the first adsorption phase of the present invention. But does not have a layer corresponding to the second adsorption layer (active white clay layer) of the present invention. It can be understood from FIG. 5 that the types of DOP and DBP with the largest amount of surface organic pollutants detected on the surface of the substrate in the cleaning device are smaller than 8 angstroms in molecular weight, and have no physical adsorption performance in the adhesive. Too good, it is only adsorbed and removed by the adsorption performance of hydrophobic zeolite. However, because the molecular size of BHT or pentamer (D5) is larger than 8 angstroms, it cannot be removed with a hydrophobic zeolite, and its adsorption and removal has to rely on a second adsorption layer having physical adsorption properties. Printed by the Consumers' Cooperative of the Central Standards Bureau of the Ministry of Economic Affairs {Please read the note on the back ^ η before filling out this page) Second, compare the various types of filters manufactured according to the present invention, using only hydrophobic zeolites. A filter and a filter of two comparative examples which are different from the present invention in a structure in which the order in which the first adsorption layer and the second adsorption layer are fixed to the support is reversed. The results are shown in Table 6. 57 419390 V. Description of the invention (Table 6) Types of gaseous organic impurities The present invention A A filter using only hydrophobic zeolite The present invention B The present invention C Comparative example D Comparative example E DOP 98% 95% 98% 99% or more 95 % 98% DBP 98% 95% 98% 99% above 95% 98% BHT 85% 30% 60% 85% 30% 60% D5 90% 35% 65% 90% 35% 65% (Please read the notes on the back first Please fill in this page again.) In Table 6, the present invention is a filter of a honeycomb structure composed of a first adsorption layer made of zeolite and a second adsorption layer made of an acid-treated montmorillonite adhesive. The first adsorption layer is disposed on the support side, and the second adsorption layer is disposed near the airflow side. In the present invention B, a filter in which an adhesive layer of zeolite and an acid-treated montmorillonite is mixed with an alumina sol which is an inorganic fixing aid is formed on the surface of a honeycomb structure. The present invention C is a filter in which an acid-treated montmorillonite adhesive is used to form a second adsorption layer on the surface of the filter of the present invention B. A filter using only a hydrophobic zeolite forms only an zeolite adsorption layer on the surface of the honeycomb structure. Comparative Example D is a filter in which the first adsorption layer and the second adsorption layer of the invention A are fixed to the support in order. The first adsorption layer is an acid-treated montmorillonite adhesive, and the second adsorption layer is a filter. Filter for honeycomb structure made of zeolite. Comparative Example E is a filter in which the first adsorption layer and the second adsorption layer of the invention C are reversely connected to the support in order. The first adsorption layer is composed of 58 papers and is suitable for China's 1¾ standard (CNS). Specification of Λ4 (public) Printed by the Consumer Cooperatives of the Ministry of Economic Affairs of the Ministry of Economic Affairs of the Ministry of Economic Affairs 419390 5. Description of the invention () Adhesive for the acid-treated montmorillonite, and the second adsorption layer by zeolite and the montmorillonite Filters for honeycomb structures made of chemicals. The structures of the adsorption layers of these filters are enlarged in Figs. 33 to 38, and are shown in a perspective view (a) and a sectional view (b), respectively. These figures 33 to 38 are model diagrams showing the adsorption layer shown in FIG. 9 or FIG. 15 as a schematic diagram partially cut into a cylindrical shape having a height of the thickness of the adsorption layer and located in the cylinder. The distribution of micropores or intermediate pores of the pores involved in adsorption. In addition, the support is omitted in these FIGS. 33 to 38. In the present invention A, as shown in FIG. 33, pores of about 8 angstroms of zeolite are formed in the first adsorption layer 551 and pores of about 15 to 300 angstroms of acid-treated montmorillonite are formed in the second adsorption layer 552. As shown in FIG. As shown in Fig. 34, a filter using only a hydrophobic zeolite has pores of about 8 angstroms formed in the adsorption layer 553. FIG. 35 of the invention B shows that pores of about δ angstroms of zeolite and pores of about 15 to 300 angstroms of acid-treated montmorillonite are formed in the adsorption layer 554. In the invention C, as shown in FIG. 36, pores of about 8 angstroms of zeolite and pores of about 15 to 300 angstroms of acid-treated montmorillonite are formed in the first adsorption layer 555, and acid-treated montenes are formed in the second adsorption layer 556. Fine stone pores of about 15 ~ 300 angstroms. In Comparative Example D, as shown in FIG. 37, pores of about 15 to 300 angstroms of acid-treated montmorillonite were formed in the first adsorption layer 560, and pores of about 8 angstroms of zeolite were formed in the second adsorption layer 561. Comparative Example E As shown in FIG. 38, pores of about 15 to 300 angstroms of acid-treated montmorillonite were formed in the first adsorption layer 562, and pores of about 8 angstroms of zeolite and acid-treated montene were formed in the second adsorption layer 563. Fine stone pores of about 15 ~ 300 angstroms. As for the results of investigating the surface contamination prevention rate of these filters as before, the filter of the present invention and the furnace phase composed of only hydrophobic zeolite 59 -β (please read the precautions on the back before filling this page)
本紙张尺度適用十闽阀家標苹(rNS; Λ4規栝(2KW 297公筇) 經濟部中夹標準局員工消費合作社印製 41939Q__B7____ 五、發明説明() 比,都在BHT、D5之吸附上優異。此外’在本發明中吸 附性之優異順序爲C、A、B 〇比較例D之吸附性能係 和只用疏水性沸石構成之過濾器同等。由表6之結果可理 解,對於如BHT或D5般分子徑比沸石之有效細孔徑大之 .氣體有機雜質之吸附性能,由在所處理對象氣體和直接接 觸之吸附層之接觸面如何分布很多有效細孔徑比沸石之有 效細孔徑大的細孔,換言之由如何增大其面積密度決定。 因此,吸附層由第1吸附層和第2吸附層之不同的2層構 成時,使適合吸附如BHT或D5般分子徑大之氣體有機雜 f之細孔之面積密度相對地變小而結果吸附性能差之吸附 層、適合吸附如BHT或D5般分子徑大之氣體有機雜質之 細孔之面積密度相對地變大而結果吸附性能優異之吸附層 固接在支撐物之順序爲,將吸附性能差之吸附層作爲直接 接觸支撐物之第1吸附層,將吸附性能優異之吸附層重疊 在該第1吸附層上,形成直接接觸所處理對象氣體之第2 吸附層,而得到了吸附性能優異之過濾器,若將固接在支 撐物之順序顛倒,因對如BHT或D5般分子徑大之氣體有 .機雜質之吸附性能變差,.需要注意。 又,如DOP或DBP般分子徑比沸石之有效細孔徑小 之氣體有機雜質之吸附性能,也由在所處理對象氣體和直 接接觸之吸附層之接觸面如何分布很多參與物理吸附之微 小孔或中等孔,換言之由如何增大其面積密度決定。因此, 直接接觸支撐物之第1吸附層不相關。那麼,只要直接接 觸所處理對象氣體之第2吸附層之吸附性能優異,不管直 60 (諳先閱讀背面之注意事項再填寫本頁) 訂- ο 本紙張尺戍適⑴屮(( ns )λ4現格(2]〇〆;:9?公;^ ) 經濟部中央標準局員工消f合作社印裝 4193801 五、發明説明() 接接觸支撐物之第1吸附層之構造爲何都可,但是並不是 這樣。在表6所量測之吸附性能意指,長時間使用過濾器 後因所處理對象氣體中所含氣體有機雜質而達到吸附飽和 之除去效率降低之前之表面污染防止率,在過濾器之性能 規格上,不僅該吸附性能,也包含因氣體有機雜質而達到 吸附飽和爲止之時間,即吸附性能不變之壽命。因決定壽 命的係吸附層整體之參與物理吸附之微小孔或中等孔之總 細孔容積或那些細孔表面積,不僅直接接觸所處理對象氣 體之第2吸附層,藉著直接接觸支撐物之第1吸附層也選 擇使得該細孔容積或細孔表面積變大之構造,可得到壽命 長的過濾器。 其次,實際製造在圖16所說明之本發明之潔淨裝置 後,將剛洗淨後之無有機物污染之附氧化膜矽晶片基板放 置在所處理空間。在所處理空間之天花板部配置具有風扇 單元、本發明之過濾器及除去粒子之過濾器之潔淨風扇單 元。在本發明之過濾器使用親水性沸石。然後,分別量測 剛洗淨後和放置3天後之接觸角,調查放置3天後接觸角 之增加量。每15天同樣地重複量測放置3天後接觸角之增 加量(洗淨->量測接觸角^放置3天->量測接觸角)’量 測了本發明之過濾器之吸附性能之隨著間的劣化。設潔淨 裝置內之循環空氣流量爲5〇〇〇m3/min,爲了處理該循環空 氣所使用之親水性沸石之使用量爲5〇〇〇kg 〇所吸入外氣之 量設爲循環空氣流量之4%之200m3/min。無麈室整體之內 容積係3120m3,每小時之換氣次數爲1〇〇次。 • 61 _________________—--------— 本纸張尺度適州十家揉卑((、\'5)八4規格(2丨〇/ 297公超) _(請先閲讀背面之注意事項再填寫本頁)This paper size is applicable to Shimin Valve ’s family standard apple (rNS; Λ4 regulations (2KW 297 gong)) Printed by the Consumers' Cooperative of the China Standards Bureau of the Ministry of Economic Affairs 41939Q__B7____ 5. The description of the invention () ratios are on the adsorption of BHT and D5 Excellent. In addition, the order of superiority of the adsorptivity in the present invention is C, A, and B. The adsorption performance of Comparative Example D is equivalent to that of a filter composed of only a hydrophobic zeolite. From the results in Table 6, it can be understood that, for example, BHT Or D5-like molecular diameter is larger than the effective pore diameter of zeolite. The adsorption performance of gaseous organic impurities is determined by how many effective pore diameters are distributed on the contact surface of the gas to be treated and the direct contact with the adsorption layer. The pores, in other words, are determined by how to increase the area density. Therefore, when the adsorption layer is composed of two different layers of the first adsorption layer and the second adsorption layer, it is suitable for adsorbing a gas having a large molecular diameter such as BHT or D5. The area density of the pores of f is relatively small and the adsorption performance is poor. The area density of the pores suitable for adsorbing gaseous organic impurities with large molecular diameters such as BHT or D5 is relatively large and the result is relatively large. The order of fixing the adsorption layer with excellent adsorption performance to the support is to use the adsorption layer with poor adsorption performance as the first adsorption layer that directly contacts the support, and superimpose the adsorption layer with excellent adsorption performance on the first adsorption layer to form By directly contacting the second adsorption layer of the target gas to be processed, a filter with excellent adsorption performance is obtained. If the order of fixing to the support is reversed, there is an organic impurity for gases with large molecular diameters such as BHT or D5. The adsorption performance deteriorates, so you need to pay attention. In addition, the adsorption performance of gas organic impurities such as DOP or DBP whose molecular diameter is smaller than the effective pore diameter of zeolite depends on the contact surface between the gas to be treated and the adsorption layer in direct contact. There are many small or medium pores involved in physical adsorption, in other words, it is determined by how to increase its area density. Therefore, the first adsorption layer directly contacting the support is not relevant. Then, as long as it directly contacts the second adsorption layer of the target gas to be processed Excellent adsorption performance, regardless of straight 60 (谙 Read the precautions on the back before filling this page) Order-ο The size of this paper is suitable ((ns) λ4 is now (2) 〆 ;: 9? Public; ^) Employees of the Central Standards Bureau of the Ministry of Economic Affairs, Cooperative Cooperative Printing 4193801 V. Description of the invention () Why the structure of the first adsorption layer contacting the support is all right, but it is not so. Table 6 The measured adsorption performance means that after long-term use of the filter, the surface pollution prevention rate before the adsorption efficiency is reduced due to the gaseous organic impurities contained in the gas to be treated, before the filter's performance specifications, not only The adsorption performance also includes the time until adsorption saturation is reached due to gaseous organic impurities, that is, the lifetime of the adsorption performance remains unchanged. Because the lifetime is determined by the entire adsorption layer, the total pore volume of micropores or medium pores involved in physical adsorption or The surface area of the pores is not only in direct contact with the second adsorption layer of the target gas to be processed, but also in a structure in which the pore volume or surface area of the pore is increased by directly contacting the first adsorption layer of the support, so that a long life can be obtained. filter. Secondly, after actually manufacturing the cleaning device of the present invention illustrated in FIG. 16, the silicon wafer substrate with an oxide film without organic contamination immediately after cleaning was placed in the processing space. A clean fan unit having a fan unit, the filter of the present invention, and a particle removing filter is disposed on the ceiling portion of the processed space. A hydrophilic zeolite is used in the filter of the present invention. Then, the contact angles immediately after washing and after 3 days of standing were measured, and the increase in the contact angle after 3 days of standing was investigated. Repeatedly every 15 days, the increase in the contact angle after being left for 3 days was measured (washing-> measuring the contact angle ^ leaving for 3 days-> measuring the contact angle) 'to measure the adsorption of the filter of the present invention Performance deteriorates over time. The circulating air flow in the clean device is set to 5000 m3 / min. The amount of hydrophilic zeolite used to treat the circulating air is 50000 kg. The amount of inhaled outside air is set to the circulating air flow. 4% of 200m3 / min. The volume of the whole chamber is 3120m3, and the number of air changes per hour is 100 times. • 61 _________________—--------— This paper is scaled by Shijia Shijia ((, \ '5), 8 and 4 specifications (2 丨 〇 / 297 Super League) _ (Please read the note on the back first (Fill in this page again)
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*1T A7 經濟部中央標率局員工消費合作社印製 4\mm 五、發明说明() 又,爲了比較,將具有親水性沸石之過濾器更換爲將 纖維狀活性炭和聚酯不織布之黏接劑複合而變成毛氈狀之 習知構造之化學式過濾器,每15天重複量測將附氧化膜矽 晶片基板洗淨後放置3天之接觸角之增加量。此時也設爲 每lm3/min通氣量之活性炭使用量爲lkg。還對於完全未 設置親水性沸石之過濾器或習知構造之化學式過濾器之情 況,即對於潔淨裝置環境中所含氣體有機物未講求特別之 對策之情況也進行一樣的量測。. 此外,剛洗淨後附氧化膜矽晶片之表面之接觸角係3 度。假設對用以防止因氣體有機雜質之污染而導致組件品 質降低之潔淨裝置環境要求之必要條件係曝露3天後附氧 化膜矽晶片之表面之接觸角保持在6度以下。 量測結果如圖39所示。比較了分別曝露在本發明之潔 淨裝置環境、設置了習知構造之化學式過濾器之潔淨裝置 環境、對於氣體有機物未講求特別對策之潔淨裝置環境下 之附氧化膜矽晶片之表面之接觸角之隨著間變化。 曝露在對於氣體有機物未講求特別對策之潔淨裝置環 境下之附氧化膜矽晶片之表面之接觸角,因放置3天而增 加了 26〜3〇度。對於本發明之過濾器,在剛開始使用後之 狀態,放置3天後之附氧化膜矽晶片之接觸角保持在4度 以下。可是,隨著通氣時間之增加’親水性沸石之吸附性 能降低,通過吸附層後之空氣中所含氣體有機物之濃度也 增加。即,隨著對親水性沸石之通氣時間增加,曝露在下 游側之已處理空氣之附氧化膜砍晶片之表面之接觸角也增 62 本紙张尺度適中网闲家標莩((、NS ) Λ4规格(210X297公筇) (請先閱讀背面之注意事項再填寫本頁)* 1T A7 Printed by the Consumer Cooperative of the Central Standards Bureau of the Ministry of Economic Affairs 4 \ mm V. Description of the invention () In addition, for comparison, the filter with hydrophilic zeolite was replaced with a fibrous activated carbon and a polyester non-woven adhesive The chemical filter with a conventional structure that is compounded into a felt shape is repeatedly measured every 15 days to increase the contact angle of the silicon wafer substrate with the oxide film after cleaning for 3 days. At this time, the amount of activated carbon per lm3 / min ventilation was set to 1 kg. The same measurement is also performed for a case where a filter of a hydrophilic zeolite or a chemical filter of a conventional structure is not provided at all, that is, a case where no special measures are required for gaseous organic substances contained in a clean device environment. In addition, the contact angle of the surface of the silicon wafer with an oxide film immediately after cleaning is 3 degrees. It is assumed that the necessary condition for the environmental requirements of a clean device to prevent the degradation of module quality due to the contamination of gaseous organic impurities is that the contact angle of the surface of the silicon wafer with an oxide film is maintained below 6 degrees after 3 days of exposure. The measurement results are shown in Figure 39. The contact angles of the surfaces of the silicon wafer with oxide film in the clean device environment exposed to the clean device environment of the present invention, the chemical filter equipped with a conventional structure, and the clean device environment without special measures for gaseous organic matter were compared. With time changes. The contact angle of the surface of the silicon wafer with an oxide film exposed to a clean device environment that does not require special measures for gaseous organic matter has increased by 26 to 30 degrees due to standing for 3 days. For the filter of the present invention, the contact angle of the silicon wafer with an oxide film after being left for 3 days was maintained at 4 degrees or less after being used. However, as the aeration time increases, the adsorption performance of the hydrophilic zeolite decreases, and the concentration of gaseous organics in the air after passing through the adsorption layer also increases. That is, as the ventilation time for the hydrophilic zeolite increases, the contact angle on the surface of the treated film exposed with the oxide film on the downstream side increases, and the contact angle on the surface of the treated paper also increases. 62 This paper is moderate in size. ((, NS) Λ4 Specifications (210X297): (Please read the precautions on the back before filling this page)
經濟部中央標準局負X;消贽合作社印製 4 mm a, B7 五、發明説明() 加。得知到曝露在通過過濾器後之空氣3天之附氧化膜矽 晶片之表面之接觸角達到6度爲止之本發明之過濾器之使 用時間約3個月。而,對於習知之化學式過濾器,連在剛 開始使用後之狀態放置3天之附氧化膜矽晶片之接觸角竟 達到12度。其理由係來自爲了載持纖維狀活性炭而使用聚 酯不織布之黏接劑之逸脫氣體全部通過化學式過濾器,污 染了放置在下游側之矽晶片之表面。在習知之化學式過濾 器,也因活性炭之吸附性能隨著通氣時間增加而降低,在 使用6個月後到達20度。 進一步說明親水性沸石對水之吸附特性。關於細孔徑 10埃之親水性沸石和以煤爲原料之活性炭,在25 °C之環 境所量測對水之吸附等溫線圖如圖40所示。關於活性炭, 只是相對濕度稍微增加,空氣中之水分吸附跑和重就急速 增加。例如,將幾乎未吸附水分之未使用之添加活性炭之 化學式過濾器保管在相對濕度20%之環境之容器內,因要 使用該化學式過濾器而自保管容器取出,馬上曝露在相對 濕度50%之潔淨裝置環境時,一直到活性炭達到吸附飽和 爲止大量地吸附空氣中之水分。活性炭在相對濕度20%(水 分吸附飽和量〇.〇〇4cc/g )和50% (水分吸附飽和量 0.114cc/g )之水分吸附飽和量之差高達〇.ncc/100g。而’ 在細孔徑10埃之親水性沸石,在相對濕度20%之水分吸附 飽和量多達〇.262pc/g,但是相對濕度由20%變爲50% ’水 分吸附飽和量之增加只不過〇.〇2cc/g。由圖40也可理解, 將具有在相對濕度約20%之環境下保管之未使用之1〇埃 63 (請先閱讀背面之注意事項再填{马本頁) Ό— 訂 本纸張尺度適丨丨】中阀(.NS )八4規格(21〇〆公.¾ ) 經濟部中央櫺隼局負工消費合作社印?^ 419390 A7 B7 五、發明説明(): 之親水性沸石之過濾器在相對濕度50%之潔淨裝置環境開 始使用時,在其上游側調節爲規定之相對濕度,也因該過 濾器所使用之親水性沸石幾乎不吸附空氣中之水分,沒有 潔淨裝置內之相對濕度低於規定値之不良。 不需要如添加了活性炭之化學式過濾器般在出貨前調 查使用處之環境溫濕度並特意使化學式過濾器之活性炭吸 附和該溫濕度平衡之水分後密封包裝才出貨之麻煩的作 業。因爲,相對濕度在20%以下之環境係在一般之作業環 境不可能之超乾燥狀態,在一般之作業環境一般爲數 10%,在具有親水性沸石之過濾器不必如添加了活性炭之 化學式過濾器般在出貨前特意吸附水分,而可直接包裝後 出貨。 其次調查了具有親水性沸石之過濾器之本發明之潔淨 裝置之濕度控制性,並和具有化學式過濾器之習知之潔淨 裝置比較。依據設於通過進行除麈、調溫、調濕之單元型 空調機和過濾器後之外氣吸入迴路之濕度感測器,調節設 於單元型空調機內之調濕機之供水閥。爲了判定濕度控制 性是否良好,在按照本發明之潔淨裝置和習知之潔淨裝置 內部也各自設置了濕度感測器。又,相對於循環空氣量 5.000m3/min,外氣吸入量設爲僅僅;200m3/min。在具有習 知構造之化學式過濾器之潔淨裝置,因化學式過濾器易吸 附通過空氣中之水分,在安裝化學式過濾器後,活性炭吸 附水分而達到平衡狀態爲止之約2週期間內,潔淨裝置內 部之相對濕度變爲比設定値50%低5%之45%。而,在具 64 (請先Μ讀背雨之注意事項再填寫本頁)Central Bureau of Standards, Ministry of Economic Affairs, negative X; printed by cooperatives 4 mm a, B7 5. Invention Description () Canada. It was learned that the filter of the present invention had a use time of about 3 months until the contact angle of the surface of the silicon wafer with an oxide film exposed to the air after passing through the filter for 3 days reached 6 degrees. However, for the conventional chemical filter, the contact angle of the silicon wafer with an oxide film that has been left for 3 days after being used immediately reaches 12 degrees. The reason is that all the escape gases from the adhesive using a polyester nonwoven fabric to support the fibrous activated carbon pass through the chemical filter and contaminate the surface of the silicon wafer placed on the downstream side. In the conventional chemical filter, the adsorption performance of activated carbon decreases with the increase of aeration time, reaching 20 degrees after 6 months of use. Further description of the adsorption characteristics of hydrophilic zeolites on water. Figure 40 shows the adsorption isotherm of water measured for a hydrophilic zeolite with a pore size of 10 angstroms and activated carbon using coal as the raw material at an environment of 25 ° C. Regarding activated carbon, only the relative humidity increased slightly, and the moisture absorption and weight in the air increased rapidly. For example, store an unused activated carbon-added chemical filter with almost no moisture absorption in a container with a relative humidity of 20%. Take out the chemical filter from the storage container and immediately expose it to a relative humidity of 50%. When the device environment is cleaned, a large amount of moisture in the air is adsorbed until the activated carbon reaches adsorption saturation. The difference between the saturated adsorption moisture content of activated carbon at relative humidity of 20% (water absorption saturation amount of 0.0004 cc / g) and 50% (water adsorption saturation amount of 0.114 cc / g) is as high as 0.1 ncc / 100 g. And 'hydrophilic zeolite with a pore size of 10 angstroms, the saturated amount of moisture adsorption at a relative humidity of 20% was as high as 0.262 pc / g, but the relative humidity changed from 20% to 50%. 〇2cc / g. It can also be understood from FIG. 40 that the unused 10 angstroms that have been stored in an environment with a relative humidity of about 20% 63 (please read the precautions on the back before filling in the {马 页) Ό—丨 丨】 China Valve (.NS) 8 4 specifications (21〇〆 公 .¾) Printed by the Central Government Bureau of the Ministry of Economic Affairs and Consumer Cooperatives? ^ 419390 A7 B7 V. Description of the invention (): When the filter of hydrophilic zeolite starts to be used in a clean device environment with a relative humidity of 50%, it is adjusted to the specified relative humidity on the upstream side, because of the filter used. The hydrophilic zeolite hardly adsorbs moisture in the air, and there is no disadvantage that the relative humidity in the clean device is lower than the specified value. The troublesome task of checking the ambient temperature and humidity of the place of use before shipment and deliberately adsorbing the activated carbon of the chemical filter with the moisture and temperature equilibrium of the chemical filter before shipment, as in the case of a chemical filter added with activated carbon, is not required. Because the environment with relative humidity below 20% is in an ultra-dry state that is impossible in ordinary operating environment, it is usually 10% in ordinary operating environment, and the filter with hydrophilic zeolite does not need to be filtered by chemical formula with activated carbon. The device intentionally absorbs moisture before shipment, and can be directly shipped after packaging. Next, the humidity controllability of the cleaning device of the present invention having a filter with a hydrophilic zeolite was investigated and compared with a conventional cleaning device having a chemical filter. Adjust the water supply valve of the humidifier installed in the unit type air conditioner based on the humidity sensor installed in the air intake circuit after the unit type air conditioner and filter that perform the dehumidification, temperature and humidity adjustment. In order to determine whether the humidity controllability is good, a humidity sensor is also provided inside the cleaning device according to the present invention and the conventional cleaning device. In addition, with respect to the circulating air amount of 5.000 m3 / min, the external air intake amount is set to only 200 m3 / min. In the clean device of the chemical filter with a conventional structure, the chemical filter easily absorbs moisture in the air. After the chemical filter is installed, the activated carbon absorbs moisture and reaches an equilibrium state within about 2 weeks. The relative humidity becomes 45% which is 5% lower than the setting 値 50%. And, with 64 (please read the precautions of back rain before filling out this page)
本紙浪尺度適州中國阎家掠萃(CNS )八4規格(2Ι()χ'297公苋) 經濟部中央標準局員工消費合作社印製 4J9390 五、發明説明() 有令固接了親水性沸石之蜂巢構造物之過濾器之按照本發 明之潔淨裝置內部,因幾乎不吸附通過空氣中之水分,相 對濕度保持在設定値.50%。在具有習知構造之化學式過濾 器之潔淨裝置,在安裝過濾器後經過了約2週,產品之良 率就降低。可是,在按照本發明之具有過濾器之潔淨裝置 內部,自安裝過濾器後開始相對濕度就保持在設定値,未 發現產品之良率降低。 其次,實際製造了已在圖18說明之本發明之過濾器 311 〇第1過濾部31 la之構造係使細孔徑爲δ埃之合成沸 石固接在蜂巢構造物。而第2過濾部31 lb之構造係使數μηι 之粉末狀酸處理蒙脫石(活性白黏土 )固接在蜂巢構造物。 此外,關於蒙脫石之特性已在前面說明了。 在,此自無塵室或無塵操作台等潔淨裝置內之基板表 面所偵測到之有機污染物之中量最多的種類係DOP和 DBP。這些在氯乙烯材料中含量很多,分子徑位於6埃〜8 埃之範圍內。因此’若將合成沸石之細孔徑設爲7埃以上, 用第1過濾部31 la就可除去成爲基板表面之有機物污染之 原因之大部分之氣體有機物。可是,自潔淨裝置內之基板 表面也偵測到某種程度之分子大小大於8埃之BHT或矽氧 烷,這些用第1過濾部無法除去,而用第2過濾部311b除 去。 本實施例之第1、第2過濾部311a、311b都如圖17 所示’具有在相鄰之波形片之間夾住無凹凸之薄板片之構 造°過濾器在通氣方向之厚度爲l〇cm,通氣風速爲 65 (請先閱讀背面之注意事項存填寫本育)The scale of this paper is Shizhou, China, Yan Jiacui (CNS) 8-4 specification (2Ι () χ'297) 苋 Printed by the Consumer Cooperatives of the Central Standards Bureau of the Ministry of Economic Affairs 4J9390 5. Description of the invention () Hydrophilicity is fixed by the order The filter inside the honeycomb structure of zeolite according to the present invention cleans the device. Since the moisture in the air is hardly absorbed, the relative humidity is kept at the set value of 5050%. In a cleaning device with a chemical filter having a conventional structure, about two weeks after the filter is installed, the product yield is reduced. However, in the cleaning device with a filter according to the present invention, the relative humidity has been maintained at the set value since the filter was installed, and no decrease in the yield of the product was found. Next, the structure of the filter 311 of the present invention described in FIG. 18 and the first filter portion 31a was actually manufactured so that synthetic zeolite having a pore diameter of δ angstroms was fixed to the honeycomb structure. On the other hand, the structure of the 31 lb of the second filtering part is made of several μm of powdered acid-treated montmorillonite (active white clay) fixed to the honeycomb structure. In addition, the characteristics of montmorillonite have been described above. Here, the most abundant types of organic pollutants detected from the surface of a substrate in a clean room such as a clean room or a clean operating table are DOP and DBP. These are abundant in vinyl chloride materials, and the molecular diameter is in the range of 6 to 8 angstroms. Therefore, if the pore diameter of the synthetic zeolite is set to 7 angstroms or more, most of the gaseous organic substances that cause the organic substance contamination on the substrate surface can be removed by the first filter portion 31a. However, BHT or siloxane having a molecular size greater than 8 angstroms was also detected on the surface of the substrate in the self-cleaning device. These were not removed by the first filter portion, but were removed by the second filter portion 311b. As shown in FIG. 17, the first and second filter sections 311 a and 311 b of this embodiment have a structure in which thin plates without unevenness are sandwiched between adjacent wave plates. The thickness of the filter in the ventilation direction is l0. cm, ventilation speed is 65 (please read the notes on the back and fill in this education)
,1T οι. 本紙張尺度適川屮闽囡家標毕(rNS ) Λ4現格(2川/2()7公婊) 經濟部中央標隼局負工消费合作社印製 419390 at B7 五、發明说明() 0.6m/s,接觸向過濾器通氣之所處理空氣之過濾器之每單 位體積之薄片總表積爲3〇〇〇m2/m3。 第1過濾部311 a之蜂巢構造物,係在將有效細孔徑S 埃、大小3μιη之疏水性合成沸石之粉末和作爲無機黏接劑 之高嶺礦物之3 μιη之粉末及矽膠一起分散之黏結劑中浸入 上述之多孔性蜂巢構造物後,乾燥製成。在無機黏接劑上, 除了高嶺礦物和矽膠之混合物以外,也可使用滑石、膨潤 土、矽酸蘇打、二氧化矽或氧化鋁等。其次,第2過濾部 311b之蜂巢構造物,係在將有效細孔徑主要分布在20埃 〜1〇〇埃之活性白黏土之3μιη之粉末和作爲無機黏接劑之 矽膠一起分散之黏結劑中浸入上述之多孔性蜂巢構造物 後,乾燥製成。此外,活性白黏土對氣體有機雜質之物理 吸附性能和活性炭相比,並無遜色。 該第1過濾部31 la之合成沸石之無機材料層之厚度係 ΙΟΟμπα ,其重量成分比係疏水性沸石:高嶺土:二氧化矽 =70% : 25% : 5%,又第2過濾部31 lb之活性白黏土之無 機材料層之厚度係ΙΟμιη,其重量成分比係活性白黏土 : 二氧化砂=87%: 13°/。。第1、第2過濾部311a、3 lib之 過濾器整體之密度都係約250g/l,其中無機材料層所占密 度在第1過濾部31 la係約90g/l (過濾器整體之約36%), 在第2過濾部3lib係約9g/l (過濾器整體之約3.6%)。 和第1過濾部31 la所具有之合成沸石之量相比,第2過濾 部311b所具有活性白黏土之無機吸附劑之量可減少到約 1/10之理由如下。因合成沸石對於相對濕度變化之水分吸 66 (請先閱讀背面之注意事項再填寫本頁) —C)· 訂 .01 本紙悵尺度適川巾阀丨句家標淨(CNS ) Λ4規格(公疗) 經濟部中央標準局貝工消費合作社印¾ 五、發明説明() 脫量少,和活性炭相比,不影響潔淨裝置內環境之濕度控 制。可是,如活性白黏土般之無機吸附劑係親水性’因具 有和活性炭同等之水分吸脫量’想減少其使用量。此外, 自潔淨裝置內之基板表面所偵測到之表面有機污染物之中 量最大之種類之DOP和DBP,這些用具有合成沸石之第1 過爐部31 la可除去。.另一方面,用第+1過濾部無法除去而 用第2過濾部3lib除去之BHT或D5 (五聚物之矽氧烷) 之空氣中濃度遠小於DOP或DBP之濃度’來自晶片表面 之偵測量也少。因此,第2過濾部31 lb所具有活性白黏土 之無機吸附劑之量也可比第1過濾部311a之合成沸石的 少。 如圖41所示,將該本發明之過濾器311和風扇593及 HEPA過濾器594 —起裝在放置在無麈室590內之保管庫 591之天花板。用風扇595將無塵室空氣599自無麈室590 內環境通過流入口 596取入保管庫591內,在用該過濾器 311所處理之無塵室空氣所充滿之處理室597之環境中, 只剛洗淨後之無有機物污染之附氧化膜砂晶片基板592只 放置3天後量測了接觸角。每15天同樣地重複量測在該環 境內放置3天後接觸角(洗淨—放置3天^量測接觸角— 择淨—放置3天—重測接觸角—…),量測了過爐器311 之吸附性能之隨著間的劣化。此外,該保管庫591使用不 會產生氣體有機雜質之材料構成,在其內部,尤其在處理 室597不會產生由保管庫本身弓丨起之氣體有機雜質。 處理室597內之空氣,沿著圖41中之箭頭所示流向, 67 本紙乐尺茂適/Π巾固闽家棉朵(('NS ί八4規格(2丨0, 2Q7公;1¾ ) (請先閲讀背面之注意事項再填寫本頁) -Q. 訂 οι. 經濟部中央標隼局員工消費合作社印製 遘 193 90 at _________B7 五、發明説明() 通過多孔板601,自地板下面部602經由回流通路603回 到天花板部604。設該保管庫591內之循環空氣流量爲 20m3/min,爲了處理該循環空氣598,將係過濾器311之 構成元件之第1過濾部311a所含合成沸石之使用量設爲 2kg,將一樣係構成元件之第2過濾部31 lb所含活性白黏 土之使用量設爲〇.2kg。將無麈室空氣599之吸入量設爲 循環空氣598之流量之4%之0.8m3/min。自流出口 600排 出和該吸入量平衡之空氣量。保管庫整體之內容積係 12m3,每小時之換氣次數爲100次。 又,爲了比較,對於在圖41之保管庫591,只留下具 有合成沸石之第1過濾部31 la而拆下了具有活性白黏土之 第2過濾部31 lb之情況,也將已洗淨之附氧化膜矽晶片基 板放置3天後量測接觸角,每15天重複量測接觸角。還對 於都未設置本發明之第1過濾部311a和第2過濾部311b 之情況,即對於無塵室空氣中所含氣體有機物未除去而直 接流入保管庫內之情況也進行一樣的量測。 此外,剛洗淨後附氧化膜矽晶片之表面之接觸角係3 度。假設對用以防止因氣體有機雜質之污染而導致組件品 質降低之保管寧環境要求之必要條件係曝露3天後附氧化 .膜矽晶片之表面之接觸角保持在6度以下。 量測結果如圖42所示。係對於保管庫591具有按照本 發明之過濾器311之情況、只具有第1過濾部31 la之情 況、對於氣體有機物未講求特別對策之情況共種情況,比 較了曝露在保管庫591內環境之附氧化膜砂晶片之表面之 68 _ 本紙尺度適則ΐί‘料螵举(CNS ) Α4規格(210/2〔;7公部·; (請先間讀背面之注意事項再填ΪΪ?本頁) 訂_ 經濟部中央標準局員工消費合作社印裝 419390 at B7_____ 五、發明説明() 接觸角之隨著間變化的。 曝露在對於氣體有機物未講求特別之對策之潔淨裝置 環境下之附氧化膜矽晶片之表面之接觸角,因放置3天而 增加了 26〜30度。對於具有按照本發明之過濾器311之潔 淨裝置,在》1開始使用後之狀態(經過時間0日)’放置3 天後之附氧化膜矽晶片之接觸角保持在4度以下。可是、’ 隨著通氣時間之增加,過濾器311之吸附性能降低,通過 過濾器後之空氣中所含氣體有機物之濃度也增加。即’隨 著對過濾器311之通氣時間增加,曝露在下游側之已處理 空氣固定時間後之附氧化膜矽晶片之表面之接觸角也會增 加。得知到曝露在通過過濾器311後之空氣3天之附氧化 膜石夕晶片之表面之接觸角達到6度爲止之過濾器311 0¾ 用時間約8個月。而,對於構成過濾器3 n之第1過濾部 311a和第2過濾部3lib之中只具有第1過濾部而缺 少第2過濾部31 lb之潔淨裝置’在剛開始使用後之狀態(經 過時間0日),放置3天後之附氧化膜矽晶片之接觸角已 超過5度。而且得知到曝露在通過具有合成沸石之第1過 濾部311 a後之空氣3天之附氧化膜矽晶片之表面之接觸角 達到6度爲止之第1過爐咅E 31 la之使用時間僅僅2個月。 爲了更詳細調查其原因,如圖43所示,對於將在圖41 所使用本發明之過濾器311 (由第1、第2過濾部31 la、 31 lb構成)裝在保管庫59Γ之無塵室空氣599之流入口 596 之情況和只將第1過濾部31 la裝在該流入口 596之情況’ 分別量測對於成爲基板表面污染之原因之4種氣體有機雜 69 (請先閲讀背面之注意事項再填寫本頁) 訂- 419390 at B7___ 五、發明说明() 質DOP、DBP、BHT、D5 (五聚物之砂氧烷)之基板 表面之污染防止效果’比較了 2種情況。在圖43 ’和圖41 不同,處理室597內之空氣,沿著圖43中之箭頭所示流向, 通過多孔板601,自地板下面部602直接由流出口 600排 出。即,圖43相當於圖41之循環路徑閉鎖之情況,保管 庫內之空氣不循環,而單方向流動。DOP、DBP之濃度 各自係數十ppb,而BHT、D5之濃度各自係數ppb。 各自將剛洗淨後之潔淨之附氧化膜矽晶片592放置在 圖43之無塵室590之環境中和保管庫591'內之環境中只4 小時後,量測並比較矽晶片表面之DOP、DBP、BHT、 D5所引起之有機物表面污染量,評價了有機物表面污染之 防止效果。其結果如表7所示·。 {諳先閱讀背面之注意事項再填寫本頁), 1T οι. The size of this paper is suitable for Sichuan, Fujian, and Fujian (rNS) Λ4 is present (2 Sichuan / 2 (7) public money) Printed by the Central Standards Bureau of the Ministry of Economic Affairs and Consumer Cooperatives 419390 at B7 V. Invention Explanation () 0.6m / s, the total sheet area per unit volume of the filter that comes in contact with the air to be processed to the filter is 3,000m2 / m3. The honeycomb structure of the first filter part 311 a is a binder that disperses a powder of hydrophobic synthetic zeolite with an effective pore size of 3 angstroms and a size of 3 μm, a powder of 3 μm of kaolin mineral as an inorganic binder, and silicone. The porous honeycomb structure is immersed in the medium and dried. On the inorganic adhesive, in addition to the mixture of kaolin mineral and silicone, talc, bentonite, silicate soda, silicon dioxide, or alumina can also be used. Next, the honeycomb structure of the second filter portion 311b is a binder in which a 3 μm powder of active white clay whose effective pore diameter is mainly distributed between 20 angstroms and 100 angstroms is dispersed together with silicone as an inorganic bonding agent. The porous honeycomb structure is immersed and dried. In addition, the physical adsorption performance of activated white clay on gaseous organic impurities is not inferior to that of activated carbon. The thickness of the inorganic material layer of the synthetic zeolite in the first filter section 31 la is 100 μπα, and the weight component ratio is hydrophobic zeolite: kaolin: silica = 70%: 25%: 5%, and the second filter section 31 lb The thickness of the inorganic material layer of the activated white clay is 10 μm, and its weight component ratio is that of the activated white clay: sand dioxide = 87%: 13 ° /. . The density of the entire filter of the first and second filter sections 311a and 3lib is about 250 g / l, and the density occupied by the inorganic material layer is about 90 g / l at the first filter section 31 la (about 36 of the entire filter). %), About 9 g / l in the second filter section 3lib (about 3.6% of the entire filter). The reason why the amount of the inorganic adsorbent of the activated white clay contained in the second filtering portion 311b can be reduced to about 1/10 compared with the amount of the synthetic zeolite contained in the first filtering portion 31a is as follows. Water absorption due to changes in relative humidity due to synthetic zeolite 66 (Please read the precautions on the back before filling this page) —C) · Order. 01 This paper 怅 size fits Sichuan towel valve 丨 sentence standard (CNS) Λ4 specification (public Treatment) Printed by the Shellfish Consumer Cooperative of the Central Standards Bureau of the Ministry of Economic Affairs Ⅴ. Description of the invention () Less off-load, compared with activated carbon, does not affect the humidity control of the environment in the clean device. However, an inorganic adsorbent, such as activated white clay, is hydrophilic because it has the same amount of water absorption and desorption as activated carbon. In addition, DOP and DBP, which are the largest types of surface organic contaminants detected from the surface of the substrate in the cleaning device, can be removed by the first furnace section 31a having a synthetic zeolite. . On the other hand, the concentration in the air of BHT or D5 (pentasil siloxane) that cannot be removed by the +1 filter and 3lib of the second filter is much lower than the concentration of DOP or DBP. The amount of detection is also small. Therefore, the amount of the inorganic adsorbent having the activated white clay in the second filtering portion 31 lb can be smaller than that of the synthetic zeolite in the first filtering portion 311a. As shown in FIG. 41, the filter 311, the fan 593, and the HEPA filter 594 of the present invention are mounted on the ceiling of a storage room 591 placed in a ballastless room 590. The fan 595 takes the clean room air 599 from the environment inside the clean room 590 into the storage 591 through the inlet 596, and in the environment of the processing room 597 filled with the clean room air processed by the filter 311, Only after cleaning, 592 wafer substrates with oxide film sand without organic contamination were left for 3 days, and the contact angle was measured. Repeat the measurement of the contact angle after being placed in the environment for 3 days every 15 days (washing—storing for 3 days ^ measurement of contact angle—choosing—storing for 3 days—retesting contact angle —...), The adsorption performance of the furnace 311 deteriorates with time. In addition, the storage 591 is made of a material that does not generate gaseous organic impurities. In the interior, especially in the processing chamber 597, no gaseous organic impurities are generated from the storage itself. The air in the processing chamber 597 flows in the direction shown by the arrow in Fig. 41. 67 paper ruler Mao Shi / Π towel Gumin cotton cotton (('NS ί eight 4 specifications (2 丨 0, 2Q7 male; 1¾) (Please read the notes on the back before filling this page) -Q. Order. Printed by the Employees' Cooperative of the Central Bureau of Standards of the Ministry of Economic Affairs 遘 193 90 at _________B7 V. Description of the invention () Perforated plate 601, from the bottom of the floor 602 returns to the ceiling portion 604 through the return path 603. The circulating air flow rate in the storage 591 is set to 20 m3 / min. In order to process the circulating air 598, the first filtering portion 311a which is a constituent element of the filter 311 is included The amount of synthetic zeolite was set to 2 kg, and the amount of activated white clay contained in 31 lb of the second filtering part of the same system component was set to 0.2 kg. The amount of inhaled air 599 was set to 598 The flow rate of 4% is 0.8m3 / min. The amount of air discharged from the outflow port 600 and the suction volume is balanced. The overall storage volume of the storage is 12m3, and the number of air changes per hour is 100 times. For comparison, for the comparison, 41 storage 591, only the first with synthetic zeolite In the case where the filter part 31 la was removed and the second filter part 31 lb with activated white clay was removed, the contact angle was measured after the cleaned silicon wafer substrate with an oxide film was left for 3 days, and the contact was repeatedly measured every 15 days In the case where neither the first filter portion 311a nor the second filter portion 311b of the present invention is provided, that is, the same amount is also applied to the case where the gaseous organic substances contained in the clean room air flow directly into the storage without being removed. In addition, the contact angle of the surface of the silicon wafer with an oxide film immediately after cleaning is 3 degrees. It is assumed that the necessary conditions for storage and environmental protection to prevent the deterioration of the quality of the module due to the contamination of gas and organic impurities are exposed for 3 days. The contact angle on the surface of the post-oxidized silicon silicon wafer is kept below 6 degrees. The measurement result is shown in FIG. 42. In the case where the storage 591 has the filter 311 according to the present invention, it has only the first filter 31. In the case of la, and the case where no special measures are required for gaseous organic matter, we compared the surface of the wafer with oxide film sand exposed to the environment in the storage 591. 68 _ The paper size is appropriate. ΐ '料 螵 举 (CNS) Α 4 specifications (210/2 [; 7 Ministry of Public Affairs ·; (please read the precautions on the back before filling out this page?) Order _ Printed by the Central Consumers Bureau of the Ministry of Economic Affairs Consumer Cooperatives 419390 at B7_____ 5. Description of the invention () The contact angle varies with time. The contact angle of the surface of the silicon wafer with an oxide film exposed to a clean device environment that does not require special measures for gaseous organic matter has increased by 26 to 30 degrees due to standing for 3 days. According to the cleaning device of the filter 311 according to the present invention, the contact angle of the silicon wafer with an oxide film after being left for 3 days in the state (elapsed time 0 days) after "1" is kept below 4 degrees. However, as the ventilation time increases, the adsorption performance of the filter 311 decreases, and the concentration of gaseous organics in the air after passing through the filter also increases. That is, as the ventilation time to the filter 311 increases, the contact angle of the surface of the silicon wafer with an oxide film after the fixed air exposed to the downstream side for a fixed time also increases. It was learned that the filter 311 0¾ exposed to the air with an oxide film on the surface of the wafer after 3 days of passing through the filter 311 had a contact angle of 6 degrees, and the use time was about 8 months. Meanwhile, the cleaning device 'with the first filter section 311a and the second filter section 3lib constituting the filter 3n having only the first filter section and lacking the 31 lb of the second filter section' is in a state immediately after use (elapsed time) Day 0), the contact angle of the silicon wafer with oxide film after being left for 3 days has exceeded 5 degrees. Moreover, it was learned that the exposure time of the first furnace 咅 E 31 la until the contact angle of the surface of the silicon wafer with an oxide film exposed to air for 3 days after passing through the first filter portion 311 a with synthetic zeolite reached 6 degrees was only 2 months. In order to investigate the cause in more detail, as shown in FIG. 43, the dust-free structure in which the filter 311 (consisting of the first and second filter sections 31a and 31 lb) of the present invention used in FIG. 41 is installed in the storage 59Γ The condition of the inlet 596 of the room air 599 and the case where only the first filter 31a is installed in the inlet 596 '. Measure the four kinds of organic impurities 69 that cause the surface contamination of the substrate. (Please read the Note: Please fill in this page again.) Order-419390 at B7___ V. Description of the invention () DOP, DBP, BHT, D5 (pentameric oxaxane) substrate surface pollution prevention effect 'Comparison of two cases. Unlike FIG. 43 'and FIG. 41, the air in the processing chamber 597 flows in the direction shown by the arrow in FIG. 43 and passes through the perforated plate 601 and is directly discharged from the lower part 602 of the floor through the outflow port 600. That is, Fig. 43 corresponds to the case where the circulation path in Fig. 41 is closed, and the air in the storage chamber does not circulate and flows in one direction. The concentrations of DOP and DBP are each coefficient ten ppb, while the concentrations of BHT and D5 are each coefficient ppb. The cleaned silicon wafer with oxide film 592 was placed in the environment of the clean room 590 in FIG. 43 and the environment in the storage 591 ′ only after 4 hours, and the DOP on the surface of the silicon wafer was measured and compared. , DBP, BHT, D5 caused the amount of organic surface pollution, and evaluated the prevention effect of organic surface pollution. The results are shown in Table 7. (谙 Please read the notes on the back before filling this page)
、tT 經濟部中央標準局負工消費合作社印x 表7 污染物之 種類 第1過濾部31 la和 第2過濾部31 lb 串聯配置 第1過爐部31 la單獨 配置 防 D0P 99%以上 99%以上 止 DBP 95% 95% 率 BHT 90% 35% D5 90% 40% οι. 使用4英吋之p型砂晶片評價有機物表面污染量。使 用升溫逸脫氣體裝置和氣相色譜質-譜聯用儀之組合分 析、量測附著在晶片表面之有機物。又,依據氣相色譜按 70 本紙张尺度適⑴中阁闽ΐ:櫟卑(CNS ) Λ4現格(2] f) y 297公好) 經濟部中央標準局員工消費合作杜印¾ 419390 五、發明説明() 照如下所示求表面污染防止率。 表面污染防止率=(卜(B/A ) ) χΙΟΟ (%) A :自無塵室環境中之晶片表面所偵測到有機污染物 質之Peak之面積 B :自保管庫環境中之晶片表面所偵測到有機污染物 質之Peak之面積 由表7得知,4種氣體有機污染物DOP、DBP、 BHT、D5之中,因DOP、DBP之分子大小都小於8埃, 利用具有有效細孔徑8埃之合成沸石之第1過濾部311a大 致完全除去。可是,因BHT、D5之分子大小都大於δ埃, 利用具有有效細孔徑8埃之合成沸石之第1過濾部31 la無 法除去,而利用具有有效細孔徑主要分布在2〇埃〜1〇〇〇埃 之活性白黏土之第2過濾部311b除去。即,如本發明之過 濾器311般,使用具有合成沸石之第1過濾部311a、配置 在該第1過濾部31 la之上游側或下游側之具有吸附氣體有 機雜質且具有有效細孔徑大於該合成沸石之有效細孔徑之 無機吸附劑之第2過濾部31 lb兩者,可完全防止由如無塵 室般之潔淨裝置環境引起之有機物表面污染,只使用具有 合成沸石之第1過濾部31 la時,因無法吸附比合成沸石之 細孔徑大之分子,無法完全防止由潔淨裝置環境引起之有 機物表面污染。這由圖42之量測結果也明白。 其次,說明在本發明疏水性沸石最好選擇有效細孔徑7 埃以上的之理由。 前面已說明了在無麈室或無塵操作台成爲有機物表面 71 (請先閱讀背面之注意事項再填寫本頁) —Ρ 丁 Γ "* 本紙恨尺度適用中因啟家桴净((,乂S ) Μ规格(2丨〇、,: 297公筇) 經濟部中央標隼局員工消費合作·社印t 419390 A7 B7 __ 五、發明説明,() 污染之原因之有機物’但是在無塵室或無麈操作台之空氣 環境中所處理之矽晶片雖有一些差異,都在表面形成自然 氧化膜,因此其晶片表面係親水性。又,在該空氣環境中 所處理之玻璃基板也因玻璃本身之物性而係親水性’這是 周知的。污染形成了這種自然氧化膜之矽晶片或玻璃基板 之親水性表面之來自空氣環境之有機物應具有和親水性表 面溶合之親水基。事實上,前面說明之成爲表面污染之原 因之有機物係具有炭元素之雙重結合或苯環之化學構造之 高沸點•高分子之疏水性有機物,具有疏水基,但是同時這 些有機物也具有成爲潔淨之親水性表面污染之原因之親水 基。可是,矽晶片或玻璃基板之親水性之潔淨表面一旦被 這些有機物污染後,所污染之表面部分變成和所附著之有 機物相同之疏水性。因在變爲疏水性之表面易和該疏水性 有機物之疏水基結合,有機物表面污染就急速進行,形成 有機物之多分子層。 成爲表面污染之原因之有機物係高沸點•高分子之疏 水性,因具有疏水基,所以最好選擇疏水性沸石之理由係 和該疏水基具有親和性。可是在次善之選擇上,因成爲這 些表面污染之原因之有機物也同時保有親水性,也可利用 和親水基具有親和性之親水性沸石。但,在利用疏水性沸 石之情況,因空氣中之水分吸附量比活性炭或親水性沸石 少,沸石多孔質構造所具有原本之氣體有機雜質之吸附容 量不會因吸附水分而減少。因此,在有機物之吸附材料上 利用疏水性沸石之情況,其壽命比一樣具有多孔質構造之 72 (錆先閱讀背面之注意事項再填寫本頁), TT Printed by the Central Bureau of Standards, Ministry of Economic Affairs, Consumer Cooperatives x Table 7 Types of pollutants The first filter section 31 la and the second filter section 31 lb are arranged in series. The first furnace section 31 la is separately configured with D0P 99% or more and 99% or more. Above DBP 95% 95% rate BHT 90% 35% D5 90% 40% οι. Using a 4-inch p-type sand wafer to evaluate the amount of organic surface contamination. A combination of a temperature-evolving fugitive gas device and a gas chromatography mass spectrometer was used to analyze and measure the organic matter adhering to the wafer surface. In addition, according to the gas chromatograph, the paper is suitable for 70 papers in accordance with the standard of 70 papers: Libei (CNS) Λ4 is present (2) f) y 297 is good) Consumption Cooperation between Employees of the Central Standards Bureau of the Ministry of Economic Affairs Du Yin ¾ 419390 V. Description of the invention () The surface contamination prevention rate is calculated | required as follows. Surface pollution prevention rate = (B / A) χΙΟΟ (%) A: Area of Peak where organic pollutants are detected from the surface of the wafer in the clean room environment B: From the surface of the wafer in the vault environment The area of Peak where organic pollutants are detected is shown in Table 7. Among the four kinds of gaseous organic pollutants DOP, DBP, BHT, and D5, because the molecular sizes of DOP and DBP are less than 8 angstroms, the effective pore diameter is 8 The first filtering part 311a of the zeolite synthetic zeolite was almost completely removed. However, since the molecular sizes of BHT and D5 are larger than δ angstroms, the first filtering section 31 a using a synthetic zeolite with an effective pore diameter of 8 angstroms cannot be removed, and the main pores with an effective pore diameter are mainly distributed at 20 angstroms to 100 angstroms. The second filtering portion 311b of the activated white clay of Angstrom was removed. That is, like the filter 311 of the present invention, a first filter portion 311a having a synthetic zeolite is used, and an organic gas having an adsorbed gas disposed on the upstream side or the downstream side of the first filter portion 31a has an effective pore diameter larger than that. Synthetic zeolite, the effective pore size of the inorganic adsorbent in the second filter part 31 lb both, can completely prevent the surface pollution of organic matter caused by a clean device environment like a clean room, only use the first filter part 31 with synthetic zeolite At la, it is not possible to adsorb molecules larger than the pore size of synthetic zeolite, which cannot completely prevent the surface pollution of organic matter caused by the clean device environment. This is also clear from the measurement results in FIG. 42. Next, the reason why the hydrophobic zeolite of the present invention preferably has an effective pore diameter of 7 angstroms or more is explained. It has been explained earlier that it becomes an organic surface in a clean room or a clean operation table. 71 (Please read the precautions on the back before filling out this page) —Ρ 丁 Γ " *乂 S) M specifications (2 丨 〇 ,,: 297 gong) Consumer Co-operation of the Central Bureau of Standards of the Ministry of Economic Affairs · Social Printing t 419390 A7 B7 __ 5. Description of the invention, () Organic matter of the cause of pollution 'but in dust-free Although there are some differences in the silicon wafers processed in the air environment of the chamber or the operation platform, the natural oxide film is formed on the surface, so the wafer surface is hydrophilic. Also, the glass substrates processed in this air environment are also The physical properties of glass itself are hydrophilic, which is well known. Organic materials from the air environment that contaminate the hydrophilic surface of the silicon wafer or glass substrate that forms this natural oxide film should have hydrophilic groups that are fused to the hydrophilic surface. In fact, the organic substances that have been described as the cause of surface contamination are high boiling points with a double bond of carbon elements or a chemical structure of a benzene ring. Polymeric hydrophobic organic substances with hydrophobic groups. But at the same time, these organics also have hydrophilic groups that cause the pollution of clean hydrophilic surfaces. However, once the hydrophilic clean surfaces of silicon wafers or glass substrates are contaminated by these organics, the contaminated surface parts become and adhered organics The same hydrophobicity. Because the surface that becomes hydrophobic is easy to combine with the hydrophobic group of the hydrophobic organic matter, the surface pollution of organic matter proceeds rapidly, forming a multi-molecular layer of organic matter. The organic matter that is the cause of surface pollution is high boiling point and high The hydrophobic nature of the molecule has a hydrophobic group, so the reason for choosing a hydrophobic zeolite is to have affinity with the hydrophobic group. However, in the second-best choice, the organic matter that is the cause of these surface contaminations also retains hydrophilicity. Hydrophilic zeolites with affinity to hydrophilic groups can also be used. However, in the case of using hydrophobic zeolites, the amount of moisture absorbed in the air is less than that of activated carbon or hydrophilic zeolites, and the zeolite porous structure has the original gas organic impurities The adsorption capacity will not decrease due to the adsorption of water. In the case of using hydrophobic zeolite as an adsorbent for organic matter, the life span is the same as that of porous structure 72 (锖 Please read the precautions on the back before filling in this page)
本紙張尺度鴻K丨中國闲家樣準{ CNS > A4規格(2丨丨)Χ2^7公龙) 經濟部中央橾华局員工消费合作社印製 41S390 五、發明説明() 活性炭或親水性沸石長。而,在具有多孔質構造之活性炭 或親水性沸石,因空氣中之水分吸附量多,多孔質構造原 本之吸附容量因吸附水分而大量,因只有扣除了水分吸附 量後剩下之吸附容量參與有機物之吸附,其壽命也比疏水 性沸石短。 其次,說明合成沸石對水之吸附特性。關於細孔徑10 埃之親水性合成沸石,在25 °C之環境所量測對水之吸附等 溫線圖也一併表示在圖27。在細孔徑10埃之親水性合成 沸石,在相對濕度20%之水分吸附飽和量多達〇.262cc/g, 但是相對濕度由20%變爲50%,水分吸附飽和量之增加只 不過0.02cc/g,只不過是活性炭時之增加量之27%。由圖 27也可理解,將具有在相對濕度約20%之環境下保管之未 使用之合成沸石之過濾器在相對濕度50%之潔淨裝置環境 開始使用時,在其上游側調節爲規定之相對濕度’也因該 過濾器所使用之合成沸石幾乎不吸附空氣中之水分’沒有 具有化學式過濾器之潔淨裝置內之相對濕度低於規定値之 含有活性炭之化學式過濾器之不良。 以上對於本發明之最佳實施例說明了係LSI或LCD之 製程全體所使用之無塵室和係小型潔淨機器之保管庫,但 是本發明未限定爲這樣的實施例。按照稱爲迷你環境之局 部的潔淨裝置或無塵操作台或無塵室或用以傳送潔淨產品 之潔淨傳送路等各種規模之潔淨裝置,以及過濾器之可處 理風量、循環風量和所吸入外氣之空氣量之比例、有無發 生來自潔淨裝置內部之氣體有機雜質等處理環境而可能有 73 木紙悵尺度坷川中國凼本檔卑(〔'NS ) 見格公接) (請先間讀背面之注意事項再填寫本頁) 丁 ·1 、-* 經濟部中央榡準局員工消費合作社印製 4 ^9390 A7 ___B7_ ___ 五、發明説明(). 多樣的實施例。又,本發明之過濾器之處理對象未限定爲 只有空氣,當然處理如氮或氬氣般之惰性氣體也一樣可產 生對半導體或LCD之製造等適合的惰性氣體。 例如預計自1999年開始使用直徑300mm之矽晶片製 造256MbitDRAM或lGbitDRAM。在這種半導體製造裝 置,將晶片引入該裝置內之房間後到反應製程開始之期 間,由惰性氣體供給裝置供給惰性氣體氮或氬氣,令充滿 該房間內。該惰性氣體係極高純度之規格,惰性氣體本身 不會引起晶片之表面污染。可是,爲了開閉惰性氣體之供 給,在惰性氣體供給裝置和房間之間設置閥,由該閥之構 成材料發生成爲晶片表面污染之原因之氣體有機物。藉著 在閥和房間之間之氣體流路設置本發明之過濾器,因該過 胃濾器本身不會發生氣體有機污染物,並除去由閥發生之各 種氣體有機污染物,有助於防止晶片之表面污染和提高品 質。 【產業上之利用性】 若利用本發明,防止在潔淨裝置所處理基板表面之有 機物污染時,對於環境中所含成爲基板表面污染之原因之 氣體有機物,藉著吸附並除去例如或DBP等分子徑 小於8埃之氣體有機雜質和例如BHT或矽氧烷等分子徑大 於8埃之氣體有機雜質兩者, A.可產生適合半導體或LCD之製造等之除去了成爲基板 表面之有機物污染之原因之氣體有機物之潔淨空氣。 74 本紙張尺度沔W屮闽肀((.NS ) Λ4^格ί 2】〇> 297公筇) (诸先聞讀背西之注意事項再填寫本貢) 訂 419390 A7 B7 經濟部中央標準局負工消費合作社印製 五、發明説明() B.在半導體或LCD之製造,藉著將潔淨空氣用作晶片表面 所曝露之潔淨裝置之環境,可防止基板表面之有機物污 染。 又’藉著適當地選擇、組合作爲用以吸附並除去分子 徑小於8埃之氣體有機雜質之吸附劑之沸石、作爲用以吸 附並除去分子徑大於δ埃之氣體有機雜質之吸附劑之各種 無機物, Α.可提供構成材料不含可燃物之過濾器,使用該過濾器構 成之潔淨裝置和使用習知之活性炭吸附劑之過濾器構成之 潔淨裝置相比,在防災上優異。 Β.可提供只由不產生成爲基板表面污染之原因之氣體有機 物之材料構成之過濾器,使用該過濾器構成之潔淨裝置和 使用習知之活性炭吸附劑之過濾器構成之潔淨裝置相比, 可更完全地防止基板表面之有機物污染。 .已可提供和習知之活性炭吸附劑之過濾器相比,更不易吸 附空氣中之水分、氣體有機雜質之吸附性能之持續時間更 長之過濾器,使用該過濾器構成之潔淨裝置和使用習知之 活性炭吸附劑之過濾器構成之潔淨裝置相比,可更簡便地 進行潔淨裝置內之濕度控制,而且可更長期地吸附並除去 環境中所含的氣體有機雜質。 ‘又,若使用具有合成沸石之過濾器,和包含在消防法 上所指定之可燃物之活性炭之習知之化學式過濾器相比, 在防災上極安全。此外,該過濾器藉著使合成沸石固接在 蜂巢構造物之構造,可減少所處理空氣之通氣阻力。又, Ί5 _ 本紙佐尺度饨州屮闽阀家標來((NS )八4规格(2i〇/.2P公筇) (諳先閣讀背面之注意事項再填寫本百〇 -Q. 訂 9. 4\δ39〇 ^ 4\δ39〇 ^ 經濟部中央標準局貝工消费合作社印¾ 五、發明説明() 在過濾器之上游側設置空你調濕裝置,也因合成沸石在相 對濕度20%以上不易吸濕,濕度控制容易。 【圖面之簡單說明】 圖1係槪略表示之本發明之實施例1之潔淨裝置之構 造之說明圖。 圖2係本發明之過濾器實例之槪略的分解分解圖。 圖3係由波形片和薄板片堆積而成之吸附層之模式部 分放大圖。 圖4係由山形片和薄板片堆積而成之吸附層之模式部 分放大圖。 圖5係槪略表示之本發明之實施例1之另一潔淨裝置 之構造之說明圖。 圖6係本發明之實施例2之過濾器之槪略的分解組立 圖。 圖7係在表面形成了吸附層之過瀘器之模式放大剖面 圖。 圖8係在表面固接了小球之過濾器之模式放大剖面 圖。 圖9係在本發明之吸附層剖面之模式部分放大圖。 +圖10係本發明之實施例2之另一過濾器之槪略的分解 組立圖。 圖η係表示二氧化矽和氧化鋁之重量比 (Si02/Al203 )和每100g沸石之水分吸附量(25 °c,相 76 本紙張尺度通/Π中阀Βίϋ皁(c—_NS ) Λ4規格(21〇>^97公没) (#先閱讀背面之注意事項再填寫本頁) ' n - - 419390The size of this paper is Hong K 丨 Sample of Chinese housekeepers {CNS > A4 size (2 丨 丨) × 2 ^ 7 male dragon) 41S390 printed by the Consumer Cooperatives of the Central China Bureau of the Ministry of Economic Affairs 5. Description of the invention () Activated carbon or hydrophilicity Zeolite is long. On the other hand, activated carbon or hydrophilic zeolite with a porous structure has a large amount of water adsorption in the air, and the original adsorption capacity of the porous structure is largely due to the adsorption of water. Only the adsorption capacity remaining after deducting the amount of water adsorption participates. The adsorption of organics has a shorter life than hydrophobic zeolites. Next, the adsorption characteristics of synthetic zeolite for water will be described. About the hydrophilic synthetic zeolite with a pore size of 10 angstroms, the adsorption isotherm of water measured at an environment of 25 ° C is also shown in FIG. 27. The hydrophilic synthetic zeolite with a pore size of 10 Angstroms has a saturated moisture absorption amount of 0.262cc / g at a relative humidity of 20%, but the relative humidity has changed from 20% to 50%, and the increase in the saturated moisture absorption amount is only 0.02cc. / g, is only 27% of the increase in activated carbon. It can also be understood from FIG. 27 that when a filter having unused synthetic zeolite stored in an environment with a relative humidity of about 20% is started to be used in a clean device environment with a relative humidity of 50%, its upstream side is adjusted to the specified relative The humidity is also due to the fact that the synthetic zeolite used in the filter hardly absorbs moisture in the air. The relative humidity in a clean device without a chemical filter is lower than that of a chemical filter containing activated carbon. The preferred embodiment of the present invention has been described above with respect to the clean room used for the entire LSI or LCD manufacturing process and the storage room for small clean machines, but the present invention is not limited to such an embodiment. According to local cleansing devices or cleanrooms or cleanrooms of various sizes called mini-environments, cleansing devices of various sizes, such as clean conveying paths used to convey clean products, as well as the filter's air volume, circulating air volume and external The ratio of the amount of air to the air, the presence or absence of gas, organic impurities from the inside of the clean device, and other processing environments may have 73 wood paper 怅 standard 坷 川 中国 凼 本 档 本 (['NS) See the grid connection) (Please read first Note on the back, please fill out this page again) Ding · 1,-* Printed by the Consumers' Cooperatives of the Central Government Bureau of the Ministry of Economic Affairs 4 ^ 9390 A7 ___B7_ ___ 5. Description of the invention (). Various embodiments. In addition, the processing object of the filter of the present invention is not limited to only air. Of course, the processing of an inert gas such as nitrogen or argon can also generate an inert gas suitable for the manufacture of semiconductors and LCDs. For example, it is expected to use a silicon wafer with a diameter of 300mm to manufacture 256MbitDRAM or 1GbitDRAM since 1999. In such a semiconductor manufacturing apparatus, after the wafer is introduced into a room in the apparatus and the reaction process is started, an inert gas nitrogen or argon gas is supplied from the inert gas supply apparatus to fill the room. This inert gas system has extremely high purity specifications. The inert gas itself will not cause surface contamination of the wafer. However, in order to open and close the supply of the inert gas, a valve is provided between the inert gas supply device and the room, and a gaseous organic substance that causes contamination of the wafer surface due to the constituent material of the valve. By providing the filter of the present invention in the gas flow path between the valve and the room, the gas-passing filter itself does not generate gaseous organic pollutants, and removes various gaseous organic pollutants generated by the valve, which helps prevent wafers Surface pollution and improve quality. [Industrial applicability] If the present invention is used to prevent the organic matter contamination on the surface of the substrate processed by the clean device, the gaseous organic matter contained in the environment that causes the surface contamination of the substrate will be adsorbed and removed by molecules such as DBP Both gaseous organic impurities with a diameter of less than 8 angstroms and gaseous organic impurities with a molecular diameter of more than 8 angstroms, such as BHT or siloxane, A. Can produce suitable for semiconductor or LCD manufacturing Clean air of gas organic matter. 74 Paper size (W. Min.) ((.NS) Λ4 ^ 格 ί 2] 〇 > 297 gong) (Please read the precautions before reading the West, then fill out the tribute) Order 419390 A7 B7 Central Standards of the Ministry of Economic Affairs Printed by the Bureau of Consumer Cooperatives 5. Description of the invention () B. In the manufacture of semiconductors or LCDs, by using clean air as the environment for the clean devices exposed on the surface of the wafer, organic matter on the surface of the substrate can be prevented from being contaminated. Also, by appropriately selecting and combining zeolites as adsorbents for adsorbing and removing gaseous organic impurities with a molecular diameter of less than 8 angstroms, and as adsorbents for adsorbing and removing gaseous organic impurities with a molecular diameter of more than δ angstrom Inorganic substances, A. Filters that do not contain combustible materials can be provided. The cleaning device using the filter is superior to the cleaning device using a conventional activated carbon adsorbent filter. Β. It is possible to provide a filter composed only of a material that does not generate gaseous organic matter which causes the surface of the substrate to be polluted. Compared with a cleaning device composed of a filter using a conventional activated carbon adsorbent, a cleaning device composed of the filter can be used. Prevent organic contamination on the substrate surface more completely. Compared with the conventional activated carbon adsorbent filters, filters that are more difficult to adsorb moisture in the air and gas and organic impurities and have a longer duration of adsorption performance have been provided. The clean device and use habits of the filter are used. Compared with the cleaning device composed of the known activated carbon adsorbent filter, the humidity control in the cleaning device can be more easily performed, and the gas and organic impurities contained in the environment can be adsorbed and removed for a longer period of time. 'Furthermore, if a filter having a synthetic zeolite is used, it is extremely safe against disasters compared with a conventional chemical filter containing activated carbon specified in the fire protection law. In addition, the filter has a structure in which synthetic zeolite is fixed to a honeycomb structure, thereby reducing the ventilation resistance of the treated air. Also, Ί5 _ This paper is attached to the standard 饨 州 屮 闽 屮 家家 来 ((NS) 规格 4 specifications (2i〇 / .2P 公 筇) (谙 Xiange read the precautions on the back before filling in this one hundred-Q. Order 9 4 \ δ39〇 ^ 4 \ δ39〇 ^ Printed by the Shellfish Consumer Cooperative of the Central Standards Bureau of the Ministry of Economic Affairs Ⅴ. Description of the invention () An air conditioning and humidity control device is installed on the upstream side of the filter, and the relative humidity of the synthetic zeolite is 20%. The above is not easy to absorb moisture, and the humidity control is easy. [Simplified description of the drawing] Fig. 1 is a diagram illustrating the structure of a cleaning device according to Embodiment 1 of the present invention, which is schematically shown. Fig. 2 is an outline of a filter example of the present invention. Exploded and exploded view. Figure 3 is an enlarged view of a model of an adsorption layer formed by stacking a corrugated sheet and a thin sheet. Figure 4 is an enlarged view of a mode of an adsorption layer formed by a stack of a chevron sheet and a thin sheet. Figure 5 The schematic diagram of the structure of another cleaning device according to the first embodiment of the present invention is shown in outline. Fig. 6 is a schematic exploded assembly view of the filter of the second embodiment of the present invention. Fig. 7 shows an adsorption layer formed on the surface. Figure 8 is an enlarged cross-sectional view of the model of the filter. Figure 9 is an enlarged cross-sectional view of the mode of the filter. Figure 9 is an enlarged view of the mode part of the adsorption layer section of the present invention. + Figure 10 is a schematic exploded assembly view of another filter of the second embodiment of the present invention. Figure η It means the weight ratio of silicon dioxide and alumina (Si02 / Al203) and the moisture absorption amount per 100g of zeolite (25 ° c, phase 76). This paper is standard / Π 中 阀 ΒίϋSoap (c—_NS) Λ4 specification (21 〇 > ^ 97 公 没) (#Read the precautions on the back before filling this page) 'n--419390
對濕度50%)之關係圖。 圖12係在25 t:之水對疏水性沸石和活性炭之吸附等 溫線圖。 圖13係本發明之其他實施例之過濾器之槪略的分解 組立圖。 圖14係在表面形成了第1吸附層和第2吸附層之過濾 器之模式放大剖面圖。 圖15係由第1吸附層和第2吸附層構成之複合吸附層 剖面之模式部分放大圖。 圖16係槪略表示之本發明之實施例2之潔淨裝置之構 造之說明圖。 圖Π係本發明之實施例3之過濾器之立體圖,(a )、 (b)分別表示分解圖、組立圖。 圖18係第1、2過濾器部之槪略的分解組立圖。 圖19係實施例3之另一過濾器之分解圖。 圖20係其他實施例之過濾器之說明圖。 圖21係由波形片和薄板片堆積而成之過濾器之模式 部分放大圖。 經濟部中央標準局員工消f合作社印f. (請先閱讀背面之注意事項再填寫本頁) 訂 圖22係由山形片和薄板片堆積而成之過濾器之模式 部分放大圖。 圖23係表示在外殼充塡小球而成之本發明之其他實 施例之過濾器’(a )係(b )之A-A剖面,(b )係(a ) 之B-B剖面。 圖24係表示曝露在利用化學式過濾器之處理空氣之 77 本紙張尺及適W中闷;(AS ) 現格(21()/297公筇) 經濟部中夾標隼局負工消贤合作社印奴 屢t939〇 五、發明説明() 晶片表面之接觸角之隨著間變化之圖。 圖25係表示按照本發明之接觸角和炭附著量之關係 圖。 圖26係表示剛洗淨之附氧化膜之矽晶片曝露在各種 環境3天時接觸角之隨著間變化之圖。 圖27係水對合成沸石和活性炭之吸附等溫線圖。 圖28係比較了成爲各種吸附劑之表面污染原因之微 量有機物之吸附性能之圖。 圖29係表示具有使用了疏水性沸石之吸附層之潔淨 裝置和具有習知之化學式過濾器之潔淨裝置之各自之相對 濕度之變化圖。 圖30係說明習知技術之濕度控制之不良之圖面。 圖31係表示圖30所示實驗之結果之圖。 圖32係表示曝露在利用化學式過濾器之處理空氣之 晶片表面之接觸角之隨著間變化之圖。 圖33係本發明A之第1吸附層和第2吸附層之模式放 大圖。 圖34係習知例之吸附層之模式放大圖。 圖35係本發明B之吸附層之模式放大圖。 圖36係本發明C之第1吸附層和第2吸附層之模式放 大圖。 圖37係比較例D之第1吸附層和第2吸附層之模式放 大圖。 圖38係比較例E之第1吸附層和第2吸附層之模式放 (請先閱讀背面之注意事項再填寫本頁)50%). Figure 12 shows the adsorption isotherm of hydrophobic zeolite and activated carbon at 25 t: water. Fig. 13 is a schematic exploded view of a filter according to another embodiment of the present invention. Fig. 14 is a schematic enlarged sectional view of a filter in which a first adsorption layer and a second adsorption layer are formed on a surface. Fig. 15 is an enlarged partial schematic view of a cross section of a composite adsorption layer composed of a first adsorption layer and a second adsorption layer. Fig. 16 is an explanatory diagram schematically showing the structure of a cleaning device according to a second embodiment of the present invention. Figure II is a perspective view of a filter according to Embodiment 3 of the present invention, and (a) and (b) respectively show an exploded view and an assembly view. Fig. 18 is a schematic exploded assembly view of the first and second filter sections. FIG. 19 is an exploded view of another filter of Embodiment 3. FIG. FIG. 20 is an explanatory diagram of a filter according to another embodiment. Fig. 21 is an enlarged view of a part of a filter pattern in which corrugated sheets and thin sheets are stacked. Employees of the Central Bureau of Standards of the Ministry of Economic Affairs of the People's Republic of China f. (Please read the precautions on the back before filling out this page) Order Figure 22 is a partially enlarged view of a filter pattern formed by stacking of mountain-shaped sheets and thin plates. Fig. 23 shows a filter '(a) of (b) a cross section A-A and (b) of a (a) cross section B-B of another embodiment of the present invention in which the housing is filled with small balls. Figure 24 shows 77 paper rulers exposed to the air treated with chemical filters and suitable for boring; (AS) Appears to be (21 () / 297 Gong) The Ministry of Economic Affairs, the Ministry of Economic Affairs, the Ministry of Economic Affairs, the Ministry of Economic Affairs, the Ministry of Economic Affairs and the Consumers Cooperative Yin Nu repeatedly t939 05. Description of the invention () The graph of the contact angle of the wafer surface changes with time. Fig. 25 is a graph showing the relationship between the contact angle and the amount of carbon deposited according to the present invention. Fig. 26 is a graph showing a change in contact angle of a silicon wafer with an oxide film that has just been cleaned and exposed to various environments for 3 days. Figure 27 isotherm plot of the adsorption of synthetic zeolite and activated carbon by water. Fig. 28 is a graph comparing the adsorption performance of the micro-organisms which are the cause of the surface contamination of various adsorbents. Fig. 29 is a graph showing changes in relative humidity of each of a cleaning device having an adsorption layer using a hydrophobic zeolite and a cleaning device having a conventional chemical filter. FIG. 30 is a diagram illustrating the disadvantages of humidity control in the conventional technology. FIG. 31 is a graph showing the results of the experiment shown in FIG. 30. Fig. 32 is a graph showing the variation in the contact angle of the surface of a wafer exposed to the processing air using a chemical filter. Fig. 33 is an enlarged view of a pattern of the first adsorption layer and the second adsorption layer of A of the present invention. FIG. 34 is an enlarged view of a conventional adsorption layer. FIG. 35 is a schematic enlarged view of an adsorption layer of the present invention B. FIG. Fig. 36 is an enlarged view of a pattern of the first adsorption layer and the second adsorption layer of the invention C. Fig. 37 is an enlarged view of a pattern of the first adsorption layer and the second adsorption layer of Comparative Example D. Figs. Figure 38 shows the pattern of the first adsorption layer and the second adsorption layer of Comparative Example E (Please read the precautions on the back before filling this page)
'1T 本紙掁尺度適州中囡拽家標净(n\,S ) Λ4^格(2丨0·〆297公漤) 二___ 二___ 經濟部中央標準局工消费合作社印裝 五、發明説明() 大圖。 圖39係表示剛洗淨之附氧化膜之矽晶片曝露在各種 環境3天時接觸角之隨著間變化之圖。 圖40係水對親水性沸石和活性炭之吸附等溫線圖。 圖41係將本發明之過濾器裝在設置在無塵室內之保 管庫之天花板之實施例之說明圖。 圖42係表示本發明之過濾器之效果之圖。 圖43係將本發明之過濾器裝在設置在無塵室內之保 管庫之無麈室空氣吸入口之另一實施例之說明圖。 【符號之說明】 1潔淨裝置 2處理空間 3天花板部 4地板下面部 5回氣通路 10風扇單元 η吸附層 12粒子過濾器 13潔淨風扇單元 (請先閱讀背面之注意事項再填寫本頁)'1T This paper is in the standard of Shizhou, and the standard of the home is (n \, S) Λ4 ^ grid (2 丨 0 · 〆297) 漤 Two ___ Two ___ Printed by the Industrial Standards and Consumer Cooperatives of the Ministry of Economic Affairs Description of the invention () Large picture. Fig. 39 is a graph showing the change in contact angle of a silicon wafer with an oxide film just cleaned when exposed to various environments for 3 days. Figure 40 isotherm plot of the adsorption of hydrophilic zeolite and activated carbon by water. Fig. 41 is an explanatory view of an embodiment in which the filter of the present invention is installed in a ceiling of a warehouse provided in a clean room. Fig. 42 is a diagram showing the effect of the filter of the present invention. Fig. 43 is an explanatory view of another embodiment in which the filter of the present invention is installed in a clean room air suction port of a maintenance room provided in a clean room. [Explanation of symbols] 1 Clean device 2 Processing space 3 Ceiling part 4 Under floor part 5 Return air passage 10 Fan unit η Adsorption layer 12 Particle filter 13 Clean fan unit (Please read the precautions on the back before filling this page)
本紙張尺度適州中闽阁家標準(CNS ) Λ4規格(2!0V297公狻)This paper is suitable for Zhongzhou Minjia Standard (CNS) Λ4 specification (2! 0V297)
Claims (1)
Applications Claiming Priority (3)
Application Number | Priority Date | Filing Date | Title |
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JP13430497 | 1997-05-08 | ||
JP22434897A JP3316166B2 (en) | 1997-05-08 | 1997-08-05 | Filter, manufacturing method thereof, and cleaning device |
JP26778497A JP3397653B2 (en) | 1997-09-12 | 1997-09-12 | Air purification filter and purification device |
Publications (1)
Publication Number | Publication Date |
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TW419390B true TW419390B (en) | 2001-01-21 |
Family
ID=27316866
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Application Number | Title | Priority Date | Filing Date |
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TW87107260A TW419390B (en) | 1997-05-08 | 1998-05-08 | Cleaning apparatus, filter and method of manufacturing the same |
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MY (1) | MY130226A (en) |
TW (1) | TW419390B (en) |
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US10908221B2 (en) | 2018-11-08 | 2021-02-02 | Acer Incorporated | Battery power estimating method and electronic device |
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1998
- 1998-05-08 MY MYPI9802067 patent/MY130226A/en unknown
- 1998-05-08 TW TW87107260A patent/TW419390B/en not_active IP Right Cessation
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
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US10908221B2 (en) | 2018-11-08 | 2021-02-02 | Acer Incorporated | Battery power estimating method and electronic device |
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MY130226A (en) | 2007-06-29 |
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