TWI235671B - Method of estimating elimination of microorganisms and apparatus for estimating elimination of microorganisms - Google Patents

Method of estimating elimination of microorganisms and apparatus for estimating elimination of microorganisms Download PDF

Info

Publication number
TWI235671B
TWI235671B TW92107911A TW92107911A TWI235671B TW I235671 B TWI235671 B TW I235671B TW 92107911 A TW92107911 A TW 92107911A TW 92107911 A TW92107911 A TW 92107911A TW I235671 B TWI235671 B TW I235671B
Authority
TW
Taiwan
Prior art keywords
microorganisms
microorganism
container
removal
item
Prior art date
Application number
TW92107911A
Other languages
Chinese (zh)
Other versions
TW200403081A (en
Inventor
Kazuo Nishikawa
Hisaharu Yagi
Yoshihiro Shimizu
Tetsuyuki Otani
Hideo Nojima
Original Assignee
Sharp Kk
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Priority claimed from JP2002326078A external-priority patent/JP2004159508A/en
Application filed by Sharp Kk filed Critical Sharp Kk
Publication of TW200403081A publication Critical patent/TW200403081A/en
Application granted granted Critical
Publication of TWI235671B publication Critical patent/TWI235671B/en

Links

Abstract

It is intended to estimate the antimicrobial effect of a sterilization treatment whereby microorganisms are irradiated with particles. Microorganisms are introduced into the space in a container (8) and then irradiated with particles (7) for sterilization. After the completion of the irradiation with the particles (7), the microorganisms are collected into a collection container (6) and measured to thereby estimate the effect. The microorganisms being sterilized may be one or more members selected form the group consisting of bacteria, fungi, viruses and allergens. As the particles, use can be made of cations, anions, a gas containing a mixture of cations with anions, charged particles such as alpha- and beta-rays, various plasmatic gas ions, ozone and radical particles, drug particles and so on.

Description

1235671 (1) 玖、發明說明 【發明所屬之技術領域】 本發明係關於評估對於空間浮游微生物之殺菌效果用 之評估微生物除去之方法及評估微生物除去之裝置β 【先前技術】 近年來’隨著居住環境之高氣密化,去除對於人體有 害之空氣中浮游微生物,以過著健康且快適地生活之要求 逐漸增強。因應此要求,開發附著各種抗菌劑之過濾器。 【發明內容】 發明所欲解決之課題 然而,上述之過濾器,因爲吸引空間之空氣,以過濾 空氣中微生物之方式,經長期使用後,交換過濾器等之維 護係不可或缺的,而且過濾器之特性並不充足,不能得到 令人滿足之性能,作爲除去微生物之方式,並不足夠。 因此,關於進行通常之浮游微生物除去評估,使含有 微生物之空氣通過過濾器,測定過濾器所過濾之微生物數 。依據此法時,不能測定對象空間中浮游微生物之濃度。 然而,除去微生物之方法,有將電離離子等之粒子照 射於微生物之殺菌處理方式,測定依此方式殺菌處理微生 物之除去能力而評估係以往所從未進行。 在此,本發明係以提供將微生物,尤其是病毒之殺菌 處理粒子,特別是將由正及負之離子所形成之離子粒子照 •Ί · (2) 1235671 射於微生物’評估其殺菌效果用之評估微生物除去之方法 及可使用該方法之評估微生物除去之裝置爲目的。 課題之解決手段 爲解決上述課題,本發明爲評估微生物除去之方法s 以供給微生物於容器內部空間,同時照射殺菌處理該微生 物用之正及負之離子所形成之粒子,於進行該粒子照射後 ’採取微生物’進行所採取之微生物之測定爲特徵。另外 ’本發明爲評估病毒除去之方法,供給作爲微生物之病毒 於容器內部空間’照射殺菌處理該病毒用之粒子,於進行 該粒子照射後,採取病毒,進行所採取之病毒之測定。 依據該方法時,於容器內部空間,照射上述粒子後, 採取微生物,進行該測定,所以可評估以照射粒子殺菌處 理微生物之除去能力,可定量地評估照射上述粒子之各種 條件。 因此,於上述之評估微生物除去之方法中,進行上述 粒子照射後,進行上述微生物之測定,並進而以與照射上 述粒子以殺菌處理微生物時之相同條件下,供給微生物, 不照射該粒子,使微生物自然衰退之後,採取微生物,進 行所採取之微生物之測定。 亦即,該發明係以一定時間照射上述粒子,進行殺菌 處理微生物,並以與殺菌處理該微生物時之相同條件下, 供給微生物,以與照射上述粒子相同時間,不照射上述粒 子’使微生物自然衰退之後,採取微生物,進行所採取之 -8- (3) 1235671 微生物之測定。 因此,分別測定對於照射上述粒子進行殺菌處理微生 物,以及不進行相關之殺菌處理使微生物自然衰退所採取 之微生物,對比其結果,基於照射上述粒子之殺菌處理微 生物之能力與自然衰退時之對比,可作相對的評估。 上述微生物之測定係上述微生物之濃度測定、細胞感 染率之測定或過敏反應之測定,依此,可進行微生物除去 評估。 另外,關於測定上述所採取之微生物,進而亦可測定 該粒子之照射時間之經時變化。依此,對於殺菌處理微生 物能力之經過時間,可進行定量的評估。 另外,關於測定上述所採取之微生物,亦可測定上述 粒子之濃度依賴性。依此,對於殺菌處理微生物能力之濃 度依賴性,可進行定量的評估。 另外,關於供給微生物於上述容器內部空間,係將分 散有微生物之溶液,以霧狀進行噴霧。依此,容易供給微 生物於容器內,容易進行微生物之殺菌處理。其次,有關 將相關微生物以霧狀噴霧時,可成爲本發明之評估對象。 另外,關於上述評估方法,係可使用於微生物之細胞 培養、微生物之紅血球凝集反應或微生物之過敏反應。依 此,可評估微生物之活性度或濃度。 另外,作爲殺菌處理上述微生物用之粒子,可使用任 —種之空氣中放電、空氣中放射線照射及勒納爾效應( Lenard effect)所生成之氣體。 (4) 1235671 另外’作爲殺菌處理上述微生物用之粒子,可使用放 射線、X光、7射線或電磁波。另外,作爲殺菌處理上述 微生物用之粒子,亦可使用正及/或負之離子。 在此’作爲殺菌處理微生物用之特殊粒子,使用正及 負之離子時’可殺菌處理微生物之理由,如以下所述。 亦即’於空氣中引起放電等之電離現象,使發生正離 子及負離子時,生成最安定的作爲正離子之H+( H20 ) η 及作爲負離子之0厂(Η20) η。 生成這些離子時,因化學反應生成活性源之過氧化氫 Η 202或自由基· 0Η,因爲該Η202或自由基· 0Η顯示極 強之活性,依此而可殺菌處理,除去空氣中之浮游微生物 〇 另外,作爲殺菌處理上述微生物用之粒子,可使用以 正或負離子之任一方爲主體之氣體。該情況時,依上述離 子具有之電荷,對於微生物之電作用係進行微生物細胞破 壞或表面蛋白質之破壞,可得到產生發生殺菌作用之效果1235671 (1) 发明 Description of the invention [Technical field to which the invention belongs] The present invention relates to a method for evaluating the removal of microorganisms and a device for evaluating the removal of microorganisms for evaluating the sterilization effect of space planktonic microorganisms [Previous technology] In recent years, with the The high airtightness of the living environment removes planktonic microorganisms in the air, which is harmful to the human body, and the requirements for a healthy and fast life are gradually increasing. In response to this demand, we have developed filters with various antibacterial agents. [Summary of the Invention] Problems to be Solved by the Invention However, because the above-mentioned filter attracts the air in the space and filters microorganisms in the air, after long-term use, the maintenance of the exchange filter is indispensable, and filtering The characteristics of the device are not sufficient, and satisfactory performance cannot be obtained, which is not enough as a way to remove microorganisms. Therefore, with regard to the usual evaluation of the removal of planktonic microorganisms, air containing microorganisms was passed through the filter, and the number of microorganisms filtered by the filter was measured. In this method, the concentration of planktonic microorganisms in the target space cannot be measured. However, there is a method for removing microorganisms by sterilizing the microorganisms by irradiating particles such as ionized ions, and measuring the removal ability of the microorganisms by sterilizing treatment in this way has never been performed before. Here, the present invention aims to provide microbes, especially viruses, with sterilizing treatment particles, especially ionic particles formed by positive and negative ions. • Ί (2) 1235671 is shot on microorganisms to evaluate their bactericidal effect. A method for evaluating microorganism removal and a device for evaluating microorganism removal using the method are intended. Means for solving the problem In order to solve the above-mentioned problem, the present invention is a method for evaluating the removal of microorganisms by supplying microorganisms to the internal space of the container, and simultaneously irradiating particles formed by positive and negative ions used for sterilizing the microorganisms. After the particles are irradiated, It is characterized by 'taken microorganisms' to carry out the determination of the taken microorganisms. In addition, "the present invention is a method for evaluating virus removal, supplying viruses as microorganisms to the container internal space" and irradiating particles for sterilizing the virus. After the particles are irradiated, the virus is collected and the virus is measured. According to this method, after the above particles are irradiated in the container's internal space, microorganisms are used to perform the measurement. Therefore, the ability to sterilize microorganisms by irradiating the particles can be evaluated, and various conditions for irradiating the particles can be quantitatively evaluated. Therefore, in the method for evaluating the removal of microorganisms, after the irradiation of the particles, the measurement of the microorganisms is performed, and further, the microorganisms are supplied under the same conditions as when the particles are irradiated to sterilize the microorganisms, and the particles are not irradiated, so that After the microorganisms have naturally decayed, the microorganisms are taken and the determination of the taken microorganisms is performed. That is, the invention irradiates the above-mentioned particles for a certain period of time to sterilize the microorganisms, and supplies the microorganisms under the same conditions as when the microorganisms are sterilized, to irradiate the particles for the same time as to irradiate the particles to make the microorganisms natural After the decline, the microorganisms were taken and the determination of the taken -8- (3) 1235671 microorganisms was performed. Therefore, the microorganisms that were sterilized by irradiating the above-mentioned particles and the microorganisms that were naturally degraded without the relevant sterilization treatment were measured, and the results were compared. Based on the comparison between the ability of the microorganisms that were irradiated with the above-mentioned particles to sterilize and the natural decay, A relative assessment can be made. The measurement of the microorganism is the measurement of the concentration of the microorganism, the measurement of the cell infection rate, or the measurement of the allergic reaction, and the removal of microorganisms can be evaluated. In addition, the measurement of the microorganisms collected as described above can be used to measure the change over time of the irradiation time of the particles. Based on this, the elapsed time of the ability to sterilize the microorganism can be quantitatively evaluated. In addition, for measuring the microorganisms collected as described above, the concentration dependence of the particles can also be measured. Based on this, the concentration dependence of the ability to sterilize the microorganisms can be quantitatively evaluated. The supply of microorganisms to the inner space of the container is a solution in which the microorganisms are dispersed and sprayed in a mist form. Accordingly, the microorganisms can be easily supplied into the container, and the microorganisms can be easily sterilized. Secondly, when the relevant microorganisms are sprayed in the form of a mist, they can be evaluated by the present invention. In addition, the above evaluation method can be used for cell culture of microorganisms, erythrocyte agglutination reaction of microorganisms, or allergic reactions of microorganisms. Accordingly, the activity or concentration of microorganisms can be evaluated. In addition, as the particles for sterilizing the microorganisms described above, any kind of gas generated by air discharge, radiation irradiation in the air, and Lenard effect can be used. (4) 1235671 In addition, as the particles for sterilizing the microorganisms described above, radiation, X-rays, 7-rays, or electromagnetic waves can be used. In addition, as the particles for sterilizing the microorganism, positive and / or negative ions may be used. Here, the reason why the sterilizing microorganisms can be sterilized by using positive and negative ions as special particles for sterilizing microorganisms is as follows. That is, the ionization phenomenon caused by discharge in the air causes positive and negative ions to generate H + (H20) η, which is the most stable, and zero plant (Η20) η, which is the negative ion. When these ions are generated, hydrogen peroxide Η 202 or radical · 0 活性, which is an active source due to a chemical reaction, because the Η 202 or free radical · 0 Η exhibits extremely strong activity, which can be sterilized to remove airborne microorganisms in the air. 〇 In addition, as the particles for sterilizing the microorganisms, a gas mainly composed of either positive or negative ions can be used. In this case, according to the charge of the above ions, the electric effect on the microorganism is the destruction of microbial cells or the destruction of surface proteins, and the effect of generating bactericidal effect can be obtained.

C 另外,使用關於殺菌處理上述微生物用之藥劑,亦可 照射藥劑粒子進行殺菌處理。使用藥劑殺菌處理時,與離 子或臭氧時相比較,可以簡單的裝置進行該粒子之供給。 因此,亦可評估相關藥劑之殺菌處理微生物之能力。 另外,作爲上述殺菌處理對象之微生物,該微生物可 至少一種或組合2種以上選自細菌、真菌、病毒及過敏原 物質所成群◊依此,關於各種微生物,可作爲本發明之除 •10- (5) 1235671 去評估之對象。 另外,供給微生物於上述容器內部空間時,對於該容 器內所供給之微生物,可由下側進行攪拌容器內部空間。 依此,關於供給微生物於容器內,可防止微生物因本身的 重量自然沈澱,照射上述粒子而有效地進行殺菌處理。另 外,進行攪拌時,亦可爲本發明之評估對象。 另外,本發明係提供作爲實現上述評估微生物除去之 方法用之裝置,具備有可供給微生物之內部空間及進行該 微生物之殺菌處理用之容器,及供給微生物於該容器內部 空間之微生物供給手段,及於上述容器內部空間,供給殺 菌處理微生物用之粒子之微生物除去手段,及以上述微生 物除去手段進行微生物之殺菌處理後,採取微生物之微生 物採取手段,測定以上述微生物採取手段所採取之微生物 而評估用之評估微生物除去之裝置。 依據該評估微生物除去之裝置,以上述微生物除去手 段,照射上述粒子進行微生物之殺菌處理後,以上述微生 物採取手段採取微生物,進行所採取微生物之測定,基於 該測定,可評估以上述微生物除去手段之殺菌處理微生物 之能力。另外,可定量地評估依據上述微生物除去手段, 照射粒子殺菌處理微生物之各種條件。 作爲其具體之型態,將上述微生物供給手段及上述微 生物除去手段及上述微生物採取手段係於含有微生物之空 氣通路,由上流側向著下流側,依次排列所構成。依此, 可流暢地執行微生物供給、微生物除去及微生物採取之一 -11 · (6) 1235671 連串步驟。 此時,若採用微生物供給手段及上述微生物採取手段 之間,介由形成含有微生物之空氣通路之風洞,該風洞之 內側配置著上述微生物除去手段之構成時,可於所限制之 風洞內進行含有微生物之空氣之供給、除去及採取。 另外,上述微生物除去手段及上述微生物採取手段係 以配置於上述微生物供給手段之垂直下方以外之區域之構 成爲宜。依據如此之配置,因爲由上述微生物供給手段所 放出之霧氣中,未成氣體狀之粒狀物體落下於垂直下方及 其周圍,所以上述微生物除去手段及上述微生物採取手段 不因上述之落下物質所污染,可提升評估裝置之信賴性。 爲獲得該效果,上述微生物供給手段之垂直下方,不配置 上述微生物除去手段及上述微生物採取手段係重要的,例 如配置上述微生物除去手段及上述微生物採取手段成水平 方向,或由上述微生物供給手段之垂直下方之偏離位置, 或於斜面方向配置上述微生物除去手段及上述微生物採取 手段等,而可得本效果。 另外,本發明中,於上述容器之外側,配置著可遮覆 上述容器之其他容器之評估微生物除去之裝置而可進行。 於如此之裝置構成,可使上述容器所漏出之微生物,或未 成氣體狀之粒狀物體爲上述其他容器所遮蔽,而難漏出於 外部。 另外,關於上述評估微生物除去之裝置,於上述容器 內部空間,對於上述所供給之微生物,可設有由下方攪拌 -12· (7) 1235671 上述容器內部空間用之攪拌手段。依此,由上述微生物供 給手段供給微生物於容器內時,防止微生物因本身重量之 自然沈澱,可有效地進行以微生物除去手段之殺菌手段。 另外,上述評估微生物除去之裝置中,係可構成以該 微生物供給手段作微生物之供給,使分散微生物之溶液成 霧狀,噴霧於該容器內部空間。 另外,上述評估微生物除去之裝置中,殺菌處理上述 微生物用之粒子,係由任一種之空氣中放電、空氣中放射 線照射及勒納爾效應(L e n a r d e f f e c t )所生成之氣體所放 出而可構成。另外,上述評估微生物除去之裝置中,殺菌 處理上述微生物用之粒子爲任一種之放射線、X光、r射 線或電磁波,放出這些而可構成。 另外,上述評估微生物除去之裝置中,上述微生物除 去手段係照射作爲殺菌處理微生物用粒子之正及/或負離 子而可構成。另外,上述評估微生物除去之裝置中,上述 微生物除去手段係照射作爲殺菌處理微生物用粒子之藥劑 粒子而可構成。 發明之實施型態 以下係說明關於本發明之實施型態。 〈第1實施型態〉 首先,說明關於可實施本發明方法之評估微生物除去 之裝置。圖1爲評估微生物除去之裝置之一例之評估微生 -13- (8) 1235671 物除去之裝置1 〇之槪略構成圖。 於評估微生物除去之裝置10中,設有容器8、構成 微生物供給手段之微生物注入管5、構成微生物除去手段 之離子發生裝置1、構成微生物採取手段之微生物採取管 3及微生物採取器6。 容器8係該內部空間爲阻斷外界空氣之構造,使微生 物存在於其內部空間並可進行該微生物之殺菌處理。 另外,容器8中,以未特別圖示之空調系統等,可任 意地調節其內部空間之溫度或濕度,可任意地設定對於微 生物之環境。 另外,容器8如圖1所示,係採取高度方向之尺寸比 水平方向之尺寸爲大所形成之型態。依此,因爲可增大取 得容器8內之空間容積,所以可增大評估微生物除去之裝 置1 〇之處理容量。 微生物注入管5係設於容器8所定之位置,介由該微 生物注入管5,可供給微生物於容器8之內部空間,而可 使微生物浮游於容器8之內部空間。 該微生物注入管5係由未特別圖示於圖1中之微生物 供給源,送入微生物。因此,由微生物注入管5之向著容 器8內之微生物注入口 5 a,注入微生物於容器8內。 關於由微生物注入管5注入微生物於容器8內,可以 注入微生物單體,亦可使分散微生物之溶液成霧狀,噴霧 於容器內。 離子發生裝置1係照射作爲殺菌處理微生物用粒子之 -14 - (9) 1235671 離子7。該離子發生裝置1係設於容器8內,面對著由微 生物注入口 5a注入於容器8內之微生物,由離子發生口 2照射離子7。 該離子發生裝置1係於其內部具備有離子發生元件’ 於該離子發生元件之電極間外加交流電壓時,因放電等之 電離現象,發生正離子及負離子所形成之離子7。 隨著相關離子發生裝置1之放電等所發生離子7係不 受容器8內之氣壓狀態影響。另外,離子7之強度(濃度 )係可調節外加運作電壓於離子發生裝置1之離子發生元 件,而可使其改變。 於容器8內空間,配設採取微生物用之微生物採取管 3。該採取管3係如圖1所示,沿著容器8之高度方向之 垂直方向所配設之部份及沿著容器8之水平方向所配設之 部份所構成。 其次,沿著採取管3之水平方向所配設之部份係貫通 容器8之側面,延伸至容器8之外部,與容器8之外部之 稍後說明之微生物採取器6相連接。採取管3之垂直方向 之上端形成微生物採取口 3a,由採取口 3a將容器8內之 微生物取入採取管3內。 微生物採取器6係配置於容器8之外部,與上述採取 管3構成微生物採取手段。微生物採取器6係介由微生物 採取管3,吸引容器8內之空間,將容器8內之微生物, 以微生物採取口 3 a取入採取管3內,並採取於微生物採 取器6。 -15 - (10) 1235671 關於採取微生物用之微生物採取 樣器而構成。另外,關於微生物採取 發泡器採取微生物而構成。 於該評估微生物除去之裝置1 0 器8內之下方設有攪拌機4。該攪拌 部空間之攪拌手段,可使用以旋轉風 流而攪拌空間者。 設置該攪拌機4以攪拌容器8內 物因本身重量自然沈澱於下方,可使 生裝置1所照射之離子7之有效存在 離子7之殺菌處理。 尤其,微生物爲質量重之種類者 澱,設有攪拌機4,可防止自然沈澱 7之殺菌處理。 另外,實施本發明時,並非一定 設有攪拌機4時,依據上述理由,可 之殺菌處理。 使用上述評估微生物除去之裝置 去之方法係可如下所述實施。首先, 注入口 5注入定量微生物於容器8內 裝置1運作’向著所注入的微生物照 進行殺菌處理。一定時間照射離子7 6採取微生物。 對於所採取微生物,可測定其菌 器6,可使用氣體取 器6,亦可介由溶液 中,如圖1所示,容 機4係攪拌容器8內 扇使周圍空間形成氣 之空間時,防止微生 微生物浮游於離子發 範圍,可有效地進行 時,容易發生自然沈 ,可有效地進行離子 要設有攪拌機4,但 更有效地進行離子7 10之評估微生物除 如上所述,由微生物 。其次,使離子發生 射離子7,對微生物 後,以微生物採取器 數。關於測定微生物 •16- (11) 1235671 菌數,亦可將所採取微生物於培養皿,以所定之培養基上 ,以一定的時間培養後再進行。依此,可正確地測定所採 取微生物之菌數。另外,微生物菌數之測定,亦可將上述 培養皿上之微生物以顯微鏡進行觀察。 如此,使用上述評估微生物除去之裝置1 〇,測定微 生物採取器6所採取微生物,可評估照射離子7時,對於 微生物殺菌處理能力。 另外,關於使用上述評估微生物除去之裝置1 〇,進 行微生物除去評估,亦可進行以下之測定及評估。首先, 如上所述,注入一定量微生物於容器8內,照射離子7, 進行一定時間之殺菌處理,之後,以微生物採取器6採取 微生物,進行測定所採取微生物之菌數。 其次,以與進行上述照射離子7之殺菌處理相同的條 件,注入同量的微生物於容器8內。其次,不照射離子7 ,經過與上述照射離子7之相同時間後,使微生物自然衰 退。之後,以微生物採取器6採取微生物,進行測定所採 取微生物之菌數。 其次,進行上述照射離子7之殺菌處理後所採取微生 物之菌數,與上述自然衰退後所採取微生物之菌數相比較 ,離子7對於微生物之殺菌處理能力,與自然衰退時之對 比,可相對地評估。 另外,關於進行測定以上之以微生物採取器6所採取 微生物’對於從開始照射離子7之經過時間或使微生物開 始自然衰退之經過時間,亦可測定微生物菌數之經時變化 •17- (12) 1235671 另外,關於進行以上之微生物測定時,亦 拌機4進行攪拌,及未進行攪拌進行測定。 另外,關於進行以上之微生物測定時,亦 微生物之離子7強度,進行對於離子7之各強 之微生物之測定。依此,可評估因應離子7強 物之殺菌處理能力。 〈第2實施型態〉 其次,參考圖2說明有關本發明之評估微 裝置之第2實施型態。圖2爲評估微生物除去 2實施型態之評估微生物除去之裝置20之槪略 於圖2所示之評估微生物除去之裝置20 器18、構成微生物供給手段之微生物注入管 生物除去手段之離子發生元件12、構成微生 之採取管13及微生物採取器6。亦即,將微 段之微生物注入管15、及微生物除去手段之 件1 2 '及微生物採取手段之採取管χ 3及微生 係於含有微生物之空氣通路,由上流側向著下 排列所構成。 谷益1 8係該內部空間爲阻斷外界空氣之 生物存在於其內部空間並可殺菌處理該微生物 知,該容器1 8係採取高度方向之尺寸比水平 爲小之型態。 可對於以攪 可改變照射 度時所採取 度對於微生 生物除去之 之裝置之第 構成圖。 中,設有容 15、構成微 物採取手段 生物供給手 離子發生元 物採取器6 流側,依次 構造,使微 。由圖2可 方向之尺寸 -18- (13) 1235671 微生物注入管1 5係於容器1 8之外部,與微生物噴霧 器1 1相連接,由該微生物噴霧器11送入微生物。微生物 噴霧器11係將含有一定濃度之微生物氣體,以一定的速 度送入微生物注入管15。其次,由微生物噴霧器11送入 微生物注入管15之含有微生物之氣體係由向著容器18內 之微生物注入口 15a,注入於容器18內。 關於由微生物噴霧器11供給微生物於容器1 8內,可 以使空氣中含有微生物單體,送入微生物注入管15,亦 可使分散微生物之溶液成霧狀,噴霧送入微生物注入管 15 ° 離子發生元件12係配設於微生物注入管15之垂直下 方區域以外之容器18內之底面上。該離子發生元件12係 由所配設成一定之大約平面狀之離子發生器12a,發生正 離子及負離子所形成之離子7。由該離子發生元件12所 發生之離子7,處理由微生物注入管15所注入之微生物 〇 該離子發生元件12係與圖1所示之離子發生裝置i 所具備之離子發生元件相同,發生離子7之運作係與關於 離子發生裝置1之說明內容相同。 採取微生物用之微生物採取管1 3係配設於微生物注 入管1 5之垂直下方區域以外,沿著水平方向,其一端形 成向著容器18內之微生物採取口 13a,另一端則是於容 器1 8之外部,連接於微生物採取器6。 容器1 8之外部所配置之微生物採取器6係介由微生 -19· (14) 1235671 物採取管13,吸引容器18內之空間,將容器玉8 生物,以微生物採取口 13 a取入採取管13內,並 微生物採取器6。 關於採取微生物用之微生物採取器6,可使用 樣器。另外,關於微生物採取器6,亦可介由溶液 採取微生物而構成。 使用上述評估微生物除去之裝置20,本發明 係可如下所述實施。首先,由微生物注入口 15注 量微生物於容器18內。其次,使離子發生元件12 向著所注入的微生物照射離子7,對微生物進行殺 。一定時間照射離子7後,以微生物採取器6採取 〇 其次,進行微生物採取器6所採取微生物之測 於測定所採取微生物,可測定所採取微生物之菌數 測定該微生物之菌數,亦可將所採取微生物於培養 所定之培養基上,以一定的時間培養後再進行。另 採取微生物菌數之測定,亦可進行使用顯微鏡觀察 如此,測定使用評估微生物除去之裝置20, 採取器6所採取微生物,可評估照射離子7時,對 物殺菌處理能力。 另外,關於該評估微生物除去之裝置20係可 由微生物注入口 1 5注入微生物於容器1 8內,及照 發生元件1 2之離子7,進行微生物之殺菌處理, 介由微生物採取口 1 3 a採取微生物所形成之一連串 內之微 採取於 氣體取 發泡器 之方法 入一定 運作, 菌處理 微生物 定。關 。關於 皿,以 外,所 〇 微生物 於微生 依照介 射離子 之後, 的處理 -20, (15) 1235671 之一種大約實施通路。 因此,關於該評估微生物除去之裝置20 ’可不必考 慮容器1 8內之微生物自然衰退,所以可進行除去高濃度 之空氣中浮游微生物之評估。 另外,關於該評估微生物除去之裝置20 ’裝置可小 型化,於密閉空間可進行評估,所以即使是有害之微生物 亦可評估。 另外,使用關於該評估微生物除去之裝置20,實施 本發明之方法時,與實施圖1所示之評估微生物除去之裝 置1 〇時之說明相同地,可進行以下之測定及評估。 亦即,不照射離子7,使供給於容器18內之微生物 自然衰退,以及照射離子7進行殺菌處理,進行採取器6 所採取微生物之測定,可比較其結果。 另外,關於進行所採取微生物之測定,對於從開始照 射離子7之經過時間或使微生物開始自然衰退之經過時間 ,亦可測定微生物菌數之經時變化。 另外,改變照射微生物之離子7強度,測定對於離子 7之各強度時所採取之微生物,可評估因應離子7強度對 於微生物之殺菌處理能力。 另外,於以上之說明係舉例作爲照射殺菌處理微生物 用之粒子之正離子及負離子所形成之離子7而說明之。 另外,殺菌處理微生物用之粒子,亦可使用藥劑粒子 。使用藥劑粒子時,將圖1所示之評估微生物除去之裝置 10之離子發生裝置1或圖2所示之評估微生物除去之裝 • 21 - (16) 1235671 置20之離子發生元件12,更改爲噴射藥劑粒子用之手段 ,而可實施本發明。使用上述之藥劑粒子時,作爲藥劑, 可使用醇類或醛類藥劑、抗病毒劑及殺蟲劑等。 〈第3實施型態〉 其次,參考圖8說明有關本發明之評估微生物除去之 裝置之第3實施型態。圖8係表示評估微生物除去之裝置 之第3實施型態之槪略構成圖,相對於第2實施型態,設 有風洞及於密閉內部容器之外側再設有其他容器爲特徵。 亦即,本型態之評估微生物除去之裝置3 0,如圖所 示,具備有容器18、構成微生物供給手段之微生物注入 管15、構成微生物除去手段之離子發生元件12、構成微 生物採取手段之採取管13及微生物採取器6。其次,容 器1 8之內部,由注入管15至採取管1 3之空間設有風洞 31,該風洞31內,配置有離子發生元件12。 容器1 8係該內部空間爲阻斷外界空氣之構造,係採 取高度方向之尺寸比水平方向之尺寸爲小之型態。該容器 18之單側壁上,介由密封墊3 2,注入管15由外部導出至 容器內,另外,相對於該注入管15之相反側之側壁上, 採取管13介由密封墊32,導出至容器內。 微生物注入管1 5係於容器1 8之外部,與微生物噴霧 器1 1相連接,由該微生物噴霧器1 1送入微生物。微生物 噴霧器1 1係將含有一定濃度之微生物氣體,以一定的速 度送入微生物注入管15。其次,由微生物噴霧器1 1送入 -22- (17) 1235671 微生物注入管1 5之含有微生物之氣體係由向著容器1 8內 之微生物注入口 15 a,注入於容器18內。另外,此時可 以使空氣中含有微生物單體,送入微生物注入管15,亦 可使分散微生物之溶液成霧狀,噴霧送入微生物注入管 15。 容器1 8內之風洞3 1係形成圓筒狀,大約成水平設置 ,其兩端向著注入管15及採取管13配置。 離子發生元件12係配設於微生物注入管15之垂直下 方區域以外,風洞3 1內之略爲上流側之底面上。該離子 發生元件1 2係由所配設成一定之大約平面狀之離子發生 電極,發生正離子及負離子,殺菌處理由微生物注入管 1 5所注入之微生物。 該離子發生元件1 2係與圖1所示之離子發生裝置1 所具備之離子發生元件相同,發生離子7之運作係與關於 離子發生裝置1之說明內容相同。 採取微生物用之微生物採取管1 3係配設於微生物注 入管1 5對側之水平方向,其一端形成向著容器1 8內之微 生物採取口 1 3 a,另一端則是於容器1 8之外部,連接於 微生物採取器6。 微生物採取器6係於內部收放著發泡液,由下沈於該 發泡液之微生物採取管1 3之末端部份,將所取入之空氣 發泡後回收。其次,包容器18、微生物噴霧器11及採取 器6之噴霧試驗系統全部均爲其他容器35所覆蓋。 另外,本實施型態中,由注入口 1 5 a所放出之霧狀係 -23· (18) 1235671 噴霧於風洞31之內部,注入口 15 a及風洞31之間,設有 些許空間,不用的水滴就落於容器1 8。 另外,注入口 15a所放出之氣體,依噴霧而具有一定 的速度,以該速度,如圖8之箭頭所示方向,通過風洞 3 1。依此機制,由離子發生元件1 2之放電電極所放出之 離子所形成之粒子與微生物反應,當到達採取器6時,可 確認微生物之離子除去效果。另外,評估微生物之方法, 並無特別的限制,可以使用瓊脂培養基之評估、細胞培養 之評估、紅血球凝集反應、生物或細胞等之過敏反應及顯 微鏡觀察等所有的評估方法。 另外,含有微生物之霧氣中未氣化而急速地落下成水 滴狀之成份或未採取之微生物成份,累積於風洞3 1內’ 雖然將其內裝之容器1 8爲難以漏出於外部之構造,但是 因爲再以其他容器3 5覆蓋其外側,更不容易對於位於外 部之人類等造成影響。因此’即使風洞3 1及容器1 8非完 全密閉容器,仍可大幅降低發生生物災害(biohazard )等 事故之發生率。另外,因其他容器35之遮蔽效果’可以 抑制從外部混入不需要的污染物質,所以可得到提升評估 精確度之效果。 〈第4實施型態〉 圖9係表示評估浮游微生物除去之裝置之槪略構成圖 ,於第3竇施型態所示之評估裝置中,取代粒子放出部份 ,改爲針型放電裝置者。 -24· (19) 1235671 亦即’本實施型態係取代第3實施型態之離子發生元 件12,改設針型放電裝置4 0者。針型放電裝置4 0係於 風洞3 1內,由其上流側區域所配置之針型放電電極40a 及其之相反側所配置之對抗平板電極40b所構成。因爲其 他之構成與第3實施型態相同5所以省略其說明。 · 本實施型態中,於針型電極40a,外加數kV左右之 · 正或負高電壓時,於針的尖端部份周圍引起放電,放出以 作爲離子成份之正或負之帶電離子爲主體之氣體。 · 依據上述組成,放出以正或負之離子爲主體之氣體, 照射於微生物注入管1 5所放出之含有微生物之霧氣,殺 菌而除去微生物,所以可進行該微生物除去評估試驗。 另外,本實施型態時,所放出之粒子7並不限於以離 ' 子爲主體,自由基、臭氧或其他具有殺菌作用之粒子皆可 〈第5實施型態〉 φ 圖1 〇係表示評估浮游病毒除去之裝置之槪略構成圖 。本實施型態中,於第3實施型態所示之評估裝置中,取 代由離子發生元件12所形成之粒子放出部份,改爲紫外 ^ 線燈及催化劑之自由基放出機制。 亦即,本實施型態係取代第3實施型態之離子發生元 . 件12,設有自由基放出機制50。自由基放出機制50係於 . 風洞3 1內之上流側區域,由約中心部所配置之紫外線燈 5〇a及其周圍之相反側所配置之催化劑50b所構成。因爲 •25· (20) 1235671 其他之構成與第3實施型態相同,所以省略其說明。 催化劑5 Ob係以包含鉑、金及氧化鈦等之材質所構成 ,因紫外線燈50a所放射之放射線能量,將其能量應用於 生成自由基,具有將所生成之自由基放出於空間之作用。 另外,催化劑50b並不限於包含鉑、金及氧化鈦等之 材質者,只要能放出活性氣體,當然亦可實現同樣的除去 評估試驗。 另外,本實施型態中,除去催化劑5 Ob之裝置亦可進 行評估。此時,由外線燈50a所放射之微粒子之光子7, 可對空間中存在的微生物進行殺菌。 另外,燈50a係以本例表示其發生放射線,作爲其放 射線,具有5eV至20eV能量之光線,其殺菌性能優異, 含有該光線之放射線適用於本評估裝置,可期待所得之評 估結果。另外,作爲上述放射線,亦可配置放射X光或 7射線之元件於紫外線燈50a之位置,同樣地可進行試驗 〇 另外’本評估方法及評估裝置係使用上述之放射線之 試驗爲有效的使用方法,當然亦可使用其他粒子,例如紅 外線等之熱線及可視光,可依據本發明進行評估。此時, 於原理上可考量係以熱控制殺菌性能,需要強力熱線及可 視光時,希望另外設置放熱機制或光遮蔽板。 另外,使用放射線時,2GHz至200GHz之電磁波可 進行殺菌。此時’並不一定需要催化劑,使微生物之構成 要素吸收電磁波之能量,而可破壞微生物至分子程度。因 -26- (21) 1235671 此,作爲所需之電磁波’可舉例如容易爲: 2.45GHz左右之電磁波,例如可使用2GHz左 側之電磁波。 另外,於2GHz以上頻率中,認爲容易爲 構成微生物要素所吸收之更高頻率範圍之電磁 高頻率元件之現狀下,作爲可能之頻率,1 20 0GHz爲可應用於殺菌之頻率。 另外,如圖1 〇所示之裝置中,於紫外線; 置係可設置電磁波放出元件或光纖等之光導波 器等。 〈對象微生物〉 另外,成爲本發明所進行之殺菌處理對象 、細菌、病毒及誘發過敏原物質(蛋白質等) 於實施本發明,可以使用這些真菌、細菌、病 物質之單體,亦可由其中任選複數組合使用。 另外,關於病毒,因爲進入一般微生物之 發明中,將抑制其增殖之效果,以殺菌或除去 。一般抑制病毒增殖之作用多使用不活化之語 於病毒,於本說明書中,亦可使用不活化之語 殺菌或除去之語句。 另外,同樣地,關於過敏原物質,於本發 誘發人體等過敏反應之效果,以殺菌或除去之 一般上述效果係可以失活之語句取代,於本說 欠所吸收之 右至短波長 蛋白質等之 波爲候補, 系可考慮至 登50a之位 元件及電熱 係包含真菌 。其次,關 毒及過敏原 範圍,於本 之語句表示 句,所以關 句,以取代 明中,抑制 語句表示。 明書中,亦 -27- (22) 1235671 可使用失活之語句,以取a _ 取代過敏原物質之枚ffl或除去之語C In addition, the sterilization treatment may be performed by irradiating the medicament particles by using a medicament for sterilizing the microorganisms. In the case of a sterilization treatment using a chemical agent, the particles can be supplied in a simpler device as compared with the case of ionization or ozone. Therefore, the ability of related agents to sterilize microorganisms can also be evaluated. In addition, as the microorganism to be subjected to the sterilization treatment, the microorganism may be at least one kind or a combination of two or more members selected from the group consisting of bacteria, fungi, viruses, and allergens, and various microorganisms may be used as addition to the present invention. -(5) 1235671 Subjects to be evaluated. When the microorganisms are supplied to the inner space of the container, the inner space of the container can be stirred from the lower side with respect to the microorganisms supplied in the container. Accordingly, the supply of the microorganisms into the container can prevent the microorganisms from naturally precipitating due to the weight of the microorganisms, and can effectively sterilize by irradiating the particles. In addition, when stirring, it can also be the evaluation target of the present invention. In addition, the present invention provides a device for realizing the above-mentioned evaluation of microorganism removal, comprising an internal space capable of supplying microorganisms, a container for sterilizing the microorganism, and a microorganism supply means for supplying microorganisms to the internal space of the container, And the microorganisms removal means for supplying the particles for sterilizing the microorganisms in the above container internal space, and after the microorganisms are sterilized by the microorganisms removing means, the microorganisms are taken by the microorganisms and the microorganisms are measured by the microorganisms Apparatus for evaluation to evaluate the removal of microorganisms. According to the apparatus for evaluating the removal of microorganisms, the above-mentioned microorganism removal means irradiates the above-mentioned particles for sterilization of the microorganisms, and then the microorganisms are taken by the above-mentioned microorganisms taking means, and the measured microorganisms are measured. Based on the measurement, the above-mentioned microorganisms removing means can be evaluated Ability to sterilize microorganisms. In addition, various conditions for sterilizing microorganisms by irradiating particles in accordance with the above-mentioned microorganism removal means can be quantitatively evaluated. As a specific form, the microbial supply means, the microbial removal means, and the microbial take means are connected to the air passage containing the microorganisms, and are arranged in order from the upstream side to the downstream side. According to this, a series of steps of microbial supply, microbial removal, and microbial collection can be performed smoothly. At this time, if a microbial supply means and a microbial take-up means are used to form a wind tunnel containing an air passage containing microorganisms, and the microbial removal means is arranged inside the wind tunnel, it can be contained in the restricted wind tunnel. Supply, removal and collection of air from microorganisms. The microorganism removing means and the microorganism taking means may be arranged in a region other than a region directly below the microorganism supplying means. According to such a configuration, since the gaseous particulate matter falls vertically below and around the mist released by the above-mentioned microorganism supply means, the above-mentioned microorganism removing means and the above-mentioned microorganism taking means are not polluted by the above-mentioned falling substances. , Which can improve the reliability of the evaluation device. In order to obtain this effect, it is important that the microorganism removal means and the microorganism removal means are not disposed vertically below the microorganism supply means, for example, the microorganism removal means and the microorganism removal means are arranged horizontally, or the microorganism supply means This effect can be obtained by a deviation position vertically below, or by disposing the above-mentioned microorganism removal means and the above-mentioned microorganism taking means in an oblique direction. In addition, in the present invention, it is possible to arrange a device for evaluating the removal of microorganisms in other containers that can cover the above-mentioned container on the outer side of the container. With such a device structure, the microorganisms leaked out of the above-mentioned container, or the particulate matter that is not gasified can be shielded by the above-mentioned other containers, and it is difficult to leak from the outside. In addition, the apparatus for evaluating the removal of microorganisms may be provided with a stirring means for stirring the microorganisms supplied from below in the internal space of the container. -12 · (7) 1235671 Accordingly, when the microorganisms are supplied into the container by the microorganism supply means described above, the microorganisms are prevented from naturally precipitating due to their own weight, and the sterilization means by the microorganism removal means can be effectively performed. In addition, the apparatus for evaluating the removal of microorganisms may be configured to supply microorganisms by the microorganism supply means, so that the solution in which the microorganisms are dispersed is atomized, and sprayed on the inner space of the container. In addition, in the apparatus for evaluating the removal of microorganisms, the particles used for sterilizing the microorganisms may be constituted by the release of gas generated by any of air discharge, radiation in the air, and Lener effect (L e n a r d e f f e c t). In addition, in the apparatus for evaluating the removal of microorganisms, particles for sterilizing the microorganisms may be any of radiation, X-rays, r-rays, or electromagnetic waves, and may be constructed by emitting these. In the apparatus for evaluating microorganism removal, the microorganism removal means may be configured to irradiate positive and / or negative ions as particles for sterilization treatment of microorganisms. In the apparatus for evaluating removal of microorganisms, the means for removing microorganisms may be constituted by irradiating pharmaceutical particles as particles for sterilization treatment of microorganisms. Embodiments of the Invention The following describes the embodiments of the present invention. <First Embodiment> First, an apparatus for evaluating the removal of microorganisms capable of carrying out the method of the present invention will be described. Fig. 1 is a schematic diagram showing the evaluation of an example of a device for removing microorganisms. (8) 1235671 A schematic diagram of a device 10 for removing microorganisms. The apparatus 10 for evaluating the removal of microorganisms is provided with a container 8, a microorganism injection tube constituting a microorganism supply means 5, an ion generating device constituting a microorganism removal means 1, a microorganism acquisition tube 3 constituting a microorganism acquisition means, and a microorganism extractor 6. The container 8 has a structure in which the internal space blocks the outside air, so that microorganisms can exist in the internal space and the microorganism can be sterilized. In addition, the container 8 can be arbitrarily adjusted with the temperature or humidity of the internal space by an air conditioning system or the like not shown in the drawing, and the environment for the microorganisms can be arbitrarily set. In addition, as shown in FIG. 1, the container 8 has a shape in which the size in the height direction is larger than the size in the horizontal direction. Accordingly, since the volume of the space in the acquisition container 8 can be increased, the processing capacity of the apparatus 10 for evaluating microorganism removal can be increased. The microorganism injection tube 5 is provided at a predetermined position of the container 8. Via the microorganism injection tube 5, the microorganisms can be supplied to the internal space of the container 8, and the microorganisms can float in the internal space of the container 8. The microorganism injection tube 5 is fed with microorganisms from a microorganism supply source not particularly shown in Fig. 1. Therefore, the microorganisms are injected into the container 8 from the microorganisms injection port 5a in the container 8 through the microorganisms injection pipe 5. Regarding the injecting of microorganisms into the container 8 from the microorganism injecting tube 5, a microbial monomer may be injected, or a solution in which the microorganisms are dispersed may be sprayed into the container. The ion generator 1 irradiates ions -14-(9) 1235671, which are particles for sterilizing microorganisms. The ion generating device 1 is installed in the container 8 and faces the microorganisms injected into the container 8 through the microorganism injection port 5a, and ions 7 are irradiated from the ion generating port 2. The ion generating device 1 is provided with an ion generating element inside thereof. When an AC voltage is applied between the electrodes of the ion generating element, ions 7 formed by positive ions and negative ions are generated due to an ionization phenomenon such as a discharge. Ions 7 generated by the discharge or the like of the related ion generating device 1 are not affected by the state of the gas pressure in the container 8. In addition, the intensity (concentration) of the ions 7 can be adjusted by adjusting the applied voltage to the ion generating element of the ion generating device 1. In the space inside the container 8, a microorganism collecting tube 3 for collecting microorganisms is provided. The take-up tube 3 is constituted by a portion arranged in a vertical direction along the height direction of the container 8 and a portion arranged in a horizontal direction of the container 8 as shown in FIG. 1. Next, a portion provided along the horizontal direction of the collecting tube 3 penetrates the side of the container 8 and extends to the outside of the container 8 and is connected to a microorganism collecting device 6 described later on the outside of the container 8. A microorganism collecting port 3a is formed at the upper end in the vertical direction of the collecting tube 3, and microorganisms in the container 8 are taken into the collecting tube 3 through the collecting port 3a. The microorganism collecting device 6 is arranged outside the container 8 and the collecting tube 3 constitutes a microorganism collecting device. The microorganisms collector 6 is adapted to suck the space in the container 8 through the microorganisms collection tube 3, and the microorganisms in the container 8 are taken into the collection tube 3 through the microorganisms collection port 3a and collected in the microorganisms collection device 6. -15-(10) 1235671 Contains a microbial sampler for collecting microorganisms. About microorganism collection The foamer is composed of microorganisms. A stirrer 4 is provided below the apparatus 10 for evaluating the removal of microorganisms. As the means for agitating the space of the agitating portion, a person who agitates the space by rotating air flow can be used. The stirrer 4 is provided to stir the contents of the container 8 naturally due to its own weight, which can effectively sterilize the ions 7 irradiated by the biological device 1. In particular, microorganisms are of a heavy quality, and a stirrer 4 is provided to prevent sterilization of the natural sedimentation 7. In addition, when the present invention is carried out, it is not always necessary to provide a stirrer 4, and the sterilization treatment can be performed for the reasons described above. The method using the above apparatus for evaluating microorganism removal can be carried out as described below. First, the injection port 5 injects a certain amount of microorganisms into the container 8 and the device 1 operates' to sterilize the photos of the injected microorganisms. Irradiate ions 7 6 for a certain period of time to take microorganisms. For the microorganisms taken, the bacteria container 6 can be measured, the gas extractor 6 can be used, or the solution can be used. As shown in Figure 1, when the internal fan of the container 4 is a stirring container 8 to make the surrounding space form a gas space, To prevent micro-organisms from floating in the ion generation range, when it can be effectively carried out, natural sinking is likely to occur. Ion can be effectively provided with a stirrer 4, but it is more effective to evaluate the ions 7 and 10. . Next, the ions are irradiated with ions 7, and the microorganisms are collected by the microorganisms. About the determination of microorganisms • 16- (11) 1235671 The number of microorganisms can also be cultured in a Petri dish with a predetermined culture medium and cultured for a certain period of time. This allows accurate measurement of the number of microorganisms collected. In addition, for the measurement of the number of microorganisms, the microorganisms on the above-mentioned culture dish can be observed with a microscope. In this way, using the apparatus 10 for evaluating the removal of microorganisms, the microorganisms collected by the microorganisms collector 6 can be measured, and the ability to sterilize the microorganisms when the ions 7 are irradiated can be evaluated. In addition, with respect to the microorganism removal evaluation using the apparatus 10 for evaluating microorganism removal described above, the following measurement and evaluation can also be performed. First, as described above, a certain amount of microorganisms are injected into the container 8 and ions 7 are irradiated to perform a sterilization treatment for a certain period of time. After that, the microorganisms are collected by the microorganisms collector 6 to measure the number of microorganisms of the collected microorganisms. Next, the same amount of microorganisms were injected into the container 8 under the same conditions as the sterilization treatment of the above-mentioned irradiated ion 7. Second, without irradiating the ions 7, the microorganisms naturally decay after the same time as the above-mentioned irradiating ions 7. Thereafter, the microorganisms are collected by the microorganism extractor 6 and the number of bacteria of the collected microorganisms is measured. Secondly, compared with the bacterial counts of the microorganisms taken after the above-mentioned sterilization treatment with ion 7 irradiation, compared with the bacterial counts of the microorganisms taken after the natural decay, the bacterial sterilization treatment capacity of the ion 7 with respect to the natural decay can be compared Assessment. In addition, regarding the measurement of the microorganisms collected by the microorganism extractor 6 described above, it is also possible to measure the change over time of the number of microorganisms with respect to the elapsed time from the start of irradiation with ions 7 or the elapsed time for the microorganisms to naturally decay. 17- (12 ) 1235671 In addition, when performing the above microorganism measurement, the mixer 4 is also used for stirring, and the measurement is performed without stirring. In addition, when the above-mentioned microorganism measurement is performed, the ion 7 strength of the microorganism is also measured, and the measurement of each of the strong microorganisms of the ion 7 is performed. Based on this, it is possible to evaluate the sterilization treatment ability of the corresponding ion 7 strong substance. <Second Embodiment> Next, a second embodiment of the evaluation microdevice according to the present invention will be described with reference to FIG. FIG. 2 is a device 20 for evaluating the removal of microorganisms according to the implementation type 2 of the device 20 for evaluating the removal of microorganisms. The device 20 is similar to the device 20 for evaluating the removal of microorganisms shown in FIG. 2. 18. 12. The take-up tube 13 and the microbial take-up device 6 constituting the micro-biology. That is, the micro-organism injecting tube 15 and the micro-organism removing means 12 'and the micro-organism taking means χ 3 and the micro-organism are connected to the air path containing the micro-organisms, and are constituted by the upstream side facing downward. Gu Yi 18 is that the internal space is to block the outside air from the existence of organisms in its internal space and can sterilize the microorganism. It is known that the container 18 adopts a height-type size smaller than the level. The structure diagram of the device for removing micro-organisms can be used to change the irradiation intensity. The container is provided with a capacity of 15, which constitutes a means for taking micro-organisms, a biological supply hand, and an ion-generating element collector. Dimensions in the direction from Fig. 2 -18- (13) 1235671 The microbial injection tube 15 is connected to the outside of the container 18 and is connected to the microbial sprayer 11 to feed the microorganisms from the microbial sprayer 11. The microbial sprayer 11 sends a microbial gas containing a certain concentration into the microbial injection pipe 15 at a certain speed. Next, the microorganism-containing gas system fed into the microorganism injection tube 15 from the microorganism sprayer 11 is injected into the container 18 through the microorganism injection port 15a in the container 18. Regarding the supply of microorganisms into the container 18 by the microbial sprayer 11, the microbial monomers in the air can be sent to the microbial injection tube 15, or the solution of dispersed microorganisms can be misted, and the spray can be sent to the microbial injection tube 15 °. Ion generation The element 12 is disposed on the bottom surface inside the container 18 other than the region directly below the microorganism injection tube 15. The ion generating element 12 is an ion generator 12a arranged in a certain approximately flat shape, and generates ions 7 formed by positive ions and negative ions. The ions 7 generated by the ion generating element 12 process the microorganisms injected by the microbial injection tube 15. The ion generating element 12 is the same as the ion generating element provided in the ion generating device i shown in FIG. 1 and generates ions 7 The operation is the same as that described for the ion generating device 1. The microbial collection tube 1 3 for collecting microorganisms is arranged outside the area vertically below the microbial injection tube 15. Along the horizontal direction, one end forms a microbial collection port 13 a toward the container 18, and the other end is in the container 18. The outside is connected to the microbe extractor 6. The microbial collector 6 arranged outside the container 1 8 is via the micro-biology -19 · (14) 1235671 material collection tube 13 to attract the space in the container 18, and the container 8 organisms are taken in through the microorganism collection port 13 a. Take inside the tube 13 and the microbial taker 6. As the microbial collector 6 for collecting microorganisms, a sampler can be used. The microorganism extractor 6 may be configured to collect microorganisms through a solution. Using the apparatus 20 for evaluating microorganism removal described above, the present invention can be implemented as described below. First, the microorganism is injected into the container 18 from the microorganism injection port 15. Next, the ion generating element 12 is irradiated with the ions 7 to the injected microorganisms to kill the microorganisms. After a certain period of time, the ion 7 is irradiated, and the microorganism is taken by the microorganism extractor 6. Then, the microorganism taken by the microorganism taker 6 is measured to determine the number of microorganisms taken. The selected microorganisms are cultured on a predetermined culture medium, and then cultured for a certain period of time. In addition, the measurement of the number of microorganisms can also be performed by observation with a microscope. Thus, the measurement uses the device 20 for evaluating the removal of microorganisms, and the microorganisms collected by the collector 6 can be used to evaluate the sterilization treatment ability of the object when the ion 7 is irradiated. In addition, the device 20 for evaluating the removal of microorganisms can be injected into the container 18 by the microorganism injection port 15 and the ions 7 of the photo-generating element 12 to sterilize the microorganisms. A series of micro-organisms formed by micro-organisms are taken into a certain operation by the method of taking a gas bubbler, and the micro-organisms are treated by bacteria. turn off . Regarding the dish, in addition to the micro-organisms in the micro-sheng according to the treatment of the ions after the -20, (15) 1235671, one of the approximate implementation pathways. Therefore, the apparatus 20 'for evaluating the removal of microorganisms does not need to consider the natural degradation of microorganisms in the container 18, and therefore, it is possible to perform the evaluation for removing high-concentration airborne microorganisms. In addition, the device 20 'for evaluating the removal of microorganisms can be miniaturized and can be evaluated in a confined space, so even harmful microorganisms can be evaluated. In addition, when the method of the present invention is performed using the apparatus 20 for evaluating microorganism removal, the following measurement and evaluation can be performed in the same manner as described when the apparatus 10 for evaluating microorganism removal shown in FIG. 1 is implemented. That is, the microorganisms supplied into the container 18 are naturally degraded without being irradiated with ions 7, and the ions 7 are irradiated for sterilization treatment, and the results of the measurement of the microorganisms collected by the collector 6 can be compared. In addition, as for the measurement of the collected microorganisms, the elapsed time from the start of irradiation of the ions 7 or the elapsed time for the microorganisms to naturally decay can also be measured over time. In addition, by changing the intensity of the ions 7 of the irradiated microorganisms, and measuring the microorganisms used for each intensity of the ions 7, the sterilization treatment ability of the microorganisms in accordance with the intensity of the ions 7 can be evaluated. In addition, the above description is described as an example of ions 7 formed by irradiating positive and negative ions of particles for sterilizing microorganisms. In addition, for particles used for sterilizing microorganisms, pharmaceutical particles can also be used. When using pharmaceutical particles, change the ion generating device 1 of the evaluation microorganism removal device 10 shown in FIG. 1 or the evaluation microorganism removal device shown in FIG. 2 • 21-(16) 1235671 Change the ion generating device 12 at 20 to The present invention can be implemented by means for spraying the medicine particles. When the above-mentioned pharmaceutical particles are used, as the medicine, alcohol or aldehyde medicines, antiviral agents, insecticides, and the like can be used. <Third embodiment> Next, a third embodiment of the apparatus for evaluating microorganism removal according to the present invention will be described with reference to Fig. 8. Fig. 8 is a schematic configuration diagram showing a third embodiment of the apparatus for evaluating the removal of microorganisms. Compared with the second embodiment, a wind tunnel and other containers are provided outside the closed inner container. That is, as shown in the figure, the apparatus 30 for evaluating microorganism removal of this type is provided with a container 18, a microorganism injection tube 15 constituting a microorganism supply means, an ion generating element 12 constituting a microorganism removal means, and Take the tube 13 and the microorganism taker 6. Next, inside the container 18, a space from the injection pipe 15 to the collection pipe 13 is provided with a wind tunnel 31. Inside the wind tunnel 31, an ion generating element 12 is arranged. The internal space of the container 18 is a structure that blocks outside air, and adopts a form in which the size in the height direction is smaller than the size in the horizontal direction. On the single side wall of the container 18, a gasket 32 is passed through, and the injection pipe 15 is led out from the outside into the container. In addition, on the side wall opposite to the injection pipe 15, a pipe 13 is led through the gasket 32 and led out. Into the container. The microorganism injection tube 15 is connected to the outside of the container 18 and is connected to the microorganism sprayer 11 and the microorganisms are fed by the microorganism sprayer 11. The microbial sprayer 11 sends a microbial gas containing a certain concentration into the microbial injection pipe 15 at a certain rate. Secondly, the microbe sprayer 11 feeds -22- (17) 1235671 The microbe-containing gas system of the microbe injection tube 15 is injected into the container 18 from the microbe injection port 15a in the container 18. In addition, at this time, the microbial monomer may be contained in the air and sent to the microbial injection pipe 15, or the solution in which the microorganisms are dispersed may be misted and sprayed into the microbial injection pipe 15. The wind tunnel 31 in the container 18 is formed in a cylindrical shape and is arranged approximately horizontally, and its two ends are arranged toward the injection pipe 15 and the taking pipe 13. The ion generating element 12 is disposed on the bottom surface on the slightly upstream side in the wind tunnel 31 outside the vertical downward region of the microorganism injection tube 15. The ion generating element 12 is an ion generating electrode arranged in a certain approximately flat shape, generating positive ions and negative ions, and sterilizing the microorganisms injected by the microorganism injection tube 15. The ion generating element 12 is the same as the ion generating element provided in the ion generating device 1 shown in FIG. 1, and the operation of generating the ion 7 is the same as the description of the ion generating device 1. The microbial collection tube 1 3 for collecting microorganisms is arranged horizontally on the opposite side of the microbial injection tube 15. One end of the collection tube 1 3 a forms a microbial collection port 1 3 a toward the inside of the container 18, and the other end is outside the container 18. , Is connected to the microbial collector 6. The microbial extractor 6 stores the foaming liquid inside, and the microorganisms sinking in the foaming liquid take the end portion of the tube 13 to foam the taken-in air and recover it. Secondly, the spray test systems of the container 18, the microbial sprayer 11 and the collector 6 are all covered by other containers 35. In addition, in this embodiment, the mist system -23 · (18) 1235671 released from the injection port 15a is sprayed inside the wind tunnel 31, and there is a little space between the injection port 15a and the wind tunnel 31. The water drops fell on the container 18. In addition, the gas released from the injection port 15a has a certain speed depending on the spray, and at this speed, passes through the wind tunnel 31 at the direction shown by the arrow in Fig. 8. According to this mechanism, the particles formed by the ions emitted from the discharge electrodes of the ion generating element 12 react with the microorganisms, and when they reach the collector 6, the ion removal effect of the microorganisms can be confirmed. In addition, the method for evaluating microorganisms is not particularly limited, and all evaluation methods such as evaluation of agar medium, evaluation of cell culture, erythrocyte agglutination reaction, allergic reaction of organisms or cells, and microscopic observation can be used. In addition, in the mist containing microorganisms, the components that have not been vaporized and rapidly dropped into a droplet shape or the unused microorganism components are accumulated in the wind tunnel 3 1 '. Although the container 18 contained therein has a structure that is difficult to leak out, However, because the outer side is covered with other containers 35, it is less likely to affect humans and the like located outside. Therefore, even if the wind tunnel 31 and the container 18 are not completely closed, the incidence of accidents such as biohazard can be greatly reduced. In addition, the shielding effect 'of the other container 35 can prevent unwanted contamination from being mixed in from the outside, so that an effect of improving the accuracy of evaluation can be obtained. <Fourth implementation type> Fig. 9 is a schematic configuration diagram showing a device for evaluating the removal of planktonic microorganisms. In the evaluation device shown in the third sinus application type, the particle discharge part is replaced with a needle discharge device. . -24 · (19) 1235671 That is, ‘this embodiment replaces the ion generating element 12 of the third embodiment, and a needle discharge device 40 is installed. The needle-type discharge device 40 is located in the wind tunnel 31 and is composed of a needle-type discharge electrode 40a arranged on the upstream side region and an anti-plate electrode 40b arranged on the opposite side. Since the other configuration is the same as that of the third embodiment, 5 its explanation is omitted. · In this embodiment, a few kV is applied to the needle electrode 40a. · When a positive or negative high voltage is applied, a discharge is caused around the tip of the needle, and the positive or negative charged ions that are ionic components are mainly emitted. Of gas. · Based on the above composition, a positive or negative ion-based gas is emitted, and the microbial-containing mist emitted by the microbial injection tube 15 is irradiated to sterilize and remove microorganisms. Therefore, the microorganism removal evaluation test can be performed. In addition, in the present embodiment, the released particles 7 are not limited to ionomers. Free radicals, ozone, or other particles with bactericidal effects can be used. <Fifth Embodiment> φ Figure 10 represents evaluation A schematic structural diagram of a device for removing plankton virus. In this embodiment, in the evaluation device shown in the third embodiment, the particle emission portion formed by the ion generating element 12 is replaced with a radical emission mechanism of an ultraviolet lamp and a catalyst. That is, the present embodiment replaces the ion generating element 12 of the third embodiment, and is provided with a radical emission mechanism 50. The free radical emission mechanism 50 is located in the upstream side region of the wind tunnel 31, and is composed of an ultraviolet lamp 50a arranged at the center and a catalyst 50b arranged on the opposite side of the ultraviolet lamp 50a. Since • 25 · (20) 1235671 is the same as the third embodiment, the description is omitted. The catalyst 5 Ob is made of a material including platinum, gold, titanium oxide, and the like. Because of the radiation energy radiated from the ultraviolet lamp 50a, the energy is used to generate free radicals, which has the effect of releasing the generated free radicals into space. In addition, the catalyst 50b is not limited to those containing materials such as platinum, gold, titanium oxide, and the like. Of course, as long as an active gas can be emitted, the same removal evaluation test can be realized. In addition, in this embodiment, the device for removing the catalyst 5 Ob can also be evaluated. At this time, the photons 7 of the fine particles emitted from the outside light 50a can sterilize the microorganisms existing in the space. In addition, the lamp 50a uses this example to show that it emits radiation. As its radiation, it has light with an energy of 5eV to 20eV, which has excellent sterilization performance. The radiation containing this light is suitable for this evaluation device, and the evaluation result obtained can be expected. In addition, as the above-mentioned radiation, an X-ray or 7-ray-emitting element may be disposed at the position of the ultraviolet lamp 50a, and the test can be performed in the same manner. In addition, 'the evaluation method and the evaluation device are effective using the above-mentioned test using the radiation. Of course, other particles can also be used, such as infrared rays and other hot rays and visible light, which can be evaluated according to the present invention. At this time, in principle, it can be considered that the sterilization performance is controlled by heat. When a strong hotline and visible light are required, it is desirable to provide a heat release mechanism or a light shielding plate. In addition, when radiation is used, electromagnetic waves from 2 GHz to 200 GHz can be sterilized. At this time, a catalyst is not necessarily required, and the constituent elements of microorganisms can absorb the energy of electromagnetic waves, and the microorganisms can be destroyed to a molecular level. Because -26- (21) 1235671, the required electromagnetic wave 'can easily be, for example, an electromagnetic wave of about 2.45 GHz, and for example, an electromagnetic wave of 2 GHz can be used. In addition, in the frequency above 2GHz, it is considered that it is easy to be an electromagnetic high-frequency element of a higher frequency range absorbed by the microbial element. As a possible frequency, 120 GHz is a frequency that can be used for sterilization. In addition, in the device shown in FIG. 10, in the ultraviolet light; the device can be provided with an electromagnetic wave emitting element or an optical waveguide such as an optical fiber. <Target microorganism> In addition, the bacteria, bacteria, viruses, and allergen-inducing substances (proteins, etc.) to be subjected to the sterilization treatment in the present invention can be used in the practice of the present invention, and monomers of these fungi, bacteria, and disease substances can be used, Use plurals in combination. In addition, the virus is incorporated into the invention of general microorganisms, and the effect of suppressing its proliferation is sterilized or removed. In general, the effect of inhibiting the proliferation of the virus is to use inactivated words for viruses. In this specification, inactivated words can also be used for sterilization or removal. In addition, similarly, regarding the effect of allergen substances on inducing allergic reactions in the body and the like, the general effect of sterilization or removal is replaced by the statement that the above-mentioned effect can be inactivated, and the right-to-short-wavelength proteins that are not absorbed in this report The wave is a candidate, and it can be considered that the 50a position element and the electric heating system include fungi. Secondly, the scope of drugs and allergens is expressed in this sentence, so the sentence is replaced by the sentence of suppression in the Ming. In the book, also -27- (22) 1235671 can use inactivated sentences to take a _ to replace or remove the ffl of the allergen substance

句C 【實施方式】 實施例 [實施例1 ] 作爲實施例1 ’以下述之條件實施。關於進行微生物 除去評估係使用圖1所示之評估微生物除去之裝置i 〇。 該評估微生物除去之裝釐1〇之容器8係使用內部空間之 尺寸爲長2.0m ’見2.5m及高2.7m者。 其次’容器8內部之環境空氣係溫度爲25 °C,相對 濕度爲4 2 %。另外,容器8內部空間係由攪拌機4所攪 拌。關於以攪拌機4攪拌係以風量爲4m3/ min進行。 使用大腸菌作爲微生物。關於供給該大腸菌於容器8 內時,係以霧狀供給微生物注入口 5 a。其次,大腸菌係 以5 0 0至1,5 0 0個/ m 3左右之濃度散佈於容器8。 另外,關於採取器6係使用Biotest Hyton RCS 氣體 取樣器而構成。以氣體取樣器採取微生物時,係以40L/ 每分進行採取4分鐘。 其次,照射離子發生裝置1所發生正離子及負離子所 形成之離子7,於此實施例1中改變各種離子濃度,關於 各離子濃度係照射1小時之離子7,進行殺菌處理。離子 濃度係距離離子發生裝置1之離子送出部份(離子發生口 -28 - (23) 1235671 2 ) 10cm之空間之數値。 其次’將大腸园以上述條件供給於谷益:內後’以 之離子濃度照射1小時之離子7,之後,以上述之氣 樣器採取大腸菌,測定所採取之大腸菌之菌數。其次 變各種離子7之離子濃度,對於各離子濃度,重覆進 關之測定。 圖3係表示關於實施例1之測定結果。圖3中, 係對應於以對數表示之離子7之離子濃度(個/cm: 另外,於圖3中,縱軸係對應於浮游菌殘存率(% ) 浮游菌殘存率係照射離子7後,未殺菌所殘存菌數, 分比表示者。 如圖3所示結果,增大離子發生裝置1所放出之 離子濃度時,確認空氣中浮游細菌之殘存率降低。另 正負離子若爲1萬個/ cm3以上時,亦確認殘存率急 低。 其次,一般室內之離子濃度爲500至1,5 00個/ ,作爲有效除去微生物效果之大致上標準,認爲送出 個/ cm3以上之正負離子濃度爲適當的。 [實施例2] 作爲實施例2,以下述之條件實施。關於進行微 除去評估係使用圖1所示之評估微生物除去之裝置 該評估微生物除去之裝置1 〇之容器8係使用內部空 尺寸爲長2.0m ’寬2.5m及高2·7ηι者。 一定 體取 ,改 行相 橫軸 )° 。該 以百 正負 外, 速降 ,cm3 1萬 生物 10 〇 間之 -29 - (24) 1235671 其次,容器8內部之環境空氣係溫度爲251,相對 濕度爲42%。另外’容器8內部空間係由攪拌機4所攪 拌。關於以攪拌機4攪拌係以風量爲4 m 3 /印丨n進行。 使用大腸菌作爲微生物。關於供給該大腸菌於容器8 內時,係以霧狀供給微生物注入口 5 a。其次,大腸菌係 以1,000個/ m3左右之濃度散佈於容器8內。 另外’關於採取器6係使用Biotest Hyton RCS氣體 取樣器而構成。以氣體取樣器採取微生物時,係以4 0 L / 每分’進彳了採取4分鐘。 其次,關於照射離子發生裝置1之離子7,進行送出 離子,以及未照射離子發生裝置1之離子7,不進行送出 離子,使其自然衰退,以上述之氣體取樣器進行採取。進 行送出離子時,離子濃度係距離離子送出部1 〇cm之空間 ,正負離子分別爲5萬個/ cm3。 其次,分別對於上述之進行送出離子及未進行送出離 子時,以上述之氣體取樣器,每隔15分鐘採取大腸菌, 進行所採取大腸菌之菌數測定。 圖4係關於實施例2之測定結果,表示浮游菌殘存率 (% )之經時變化。圖4中,橫軸係對應經過時間,縱軸 係與圖3同樣地對應於浮游菌殘存率(% )。 未進行送出離子時,經過1小時後之自然衰退之菌殘 存率爲80%。另一方面,進行送出離子時,經過1小時 後之菌殘存率爲10%。 關於以上之測定,作爲判斷除去微生物效果爲有效之 -30· (25) 1235671 大致上標準,若考慮微生物之採取精確度及濃度測定精確 度時,認爲與自然衰退之殘存率有10%之差異時爲有意 差。另外,若考慮試驗之精確度時,未送出離子時之自然 衰退,經過1小時後之菌殘存率爲5 0 %以上之試驗條件 .~ 爲適宜的。 / 圖5係表示分別對於進行離子放出及不進行離子放出 ~ ,攝影經過1 5分鐘後所採取之大腸菌之照片。圖5 ( a ) 爲進行離子放出者,圖5(b)爲不進行離子放出者。 · 另外,關於進行圖5所示之大腸菌之攝影,上述各情 況下所採取之大腸菌,於瓊脂培養基上,以34 °C,濕度 10.0% RH下,培養48小時後,進行攝影。另外,圖5中 ,培養皿之大小爲9cm。 ~ 進行離子送出時,如圖5(a)所示,未見有大腸菌 之菌落生成。另一方面,未進行離子送出時,如圖5(b )所示,可觀察到大腸菌之菌落。由圖5所示的結果可知 ,以離子可滅菌。 &lt;1 [實施例3] 作爲實施例3係以下述之條件實施。關於進行微生物 除去評估係使用圖1所示之評估微生物除去之裝置〗〇。 該評估微生物除去之裝置〗〇之容器8係使用內部空間之 尺寸爲長2·0ηι,寬2.5m及高2.7m者。其次,容器8內 部之環境空氣係溫度爲2 5 °C,相對濕度爲4 2 %。 另外’本實施例3,如後述發明,於容器8內進行攪 •31 - (26) 1235671 泮及不攪拌的比較,攪拌容器8內之空間係以攪拌機4 , 風量爲4m3 / min進行攪拌。 使用一種真菌之黑黴(Cladosporium)作爲微生物。 關於供給該黑黴於容器8內時,係以霧狀由微生物注入口 5 a供給。其次,黑黴濃度係以1,〇 〇 〇個/ m 3左右散佈於 容器8內。 ^ 另外,關於採取器6係使用Biotest Hyton RCS氣體 取樣器而構成。以氣體取樣器採取微生物時,係以40L/ φ 每分,進行採取4分鐘。 其次,分別對於以攪拌機4進行攪拌及不以攪拌機4 進行攪拌,以上述氣體取樣器,每隔15分鐘採取空氣中 浮游菌,進行測定所採取菌之菌數。 ‘ 圖6係關於實施例3之測定結果,表示依攪拌的有無 之自然衰退之空氣中浮游真菌殘存率(% )之經時變化。 圖6中,橫軸係對應經過時間,縱軸係與圖3同樣地對應 於浮游菌殘存率(% ) 。 · 未進行攪拌時,經過45分鐘後,菌爲檢出限界之菌 殘存率爲12%。另一方面,進行攪拌時,因經過1小時 後之自然衰退,菌殘存率爲80%。 ^ 由以上結果,增加攪拌手段可抑制菌之自然落下,可 容易進行浮游微生物之除去評價。尤其,菌之質量大時, , 進行攪拌係有效的。 [實施例4;] -32- (27) 1235671 作爲實施例4係以下述之條件實施。關於進行微生物 除去δ平估係使用圖1所示之評估微生物除去之裝置1 〇。 該評估微生物除去之裝置10之容器8係使用內部空間之 尺寸爲長2.0m,寬2.5m及高^刀爪者。 其次’容器8內部之環境空氣係溫度爲25°C,相對 濕度爲42%。另外,容器8內部空間係由攪拌機4所攪 拌。關於以攪拌機4攪拌係以風量爲4 m 3 / m i η進行。 使用 種真囷之黑徽(Cladosporium)作爲微生物。 關於供給該黑黴於容器8內時,係以霧狀供給微生物注入 口 5a。其次,黑黴濃度係以l5〇0〇個/ m3左右散佈於容 器8內。 另外,關於採取器6係使用Biotest Hyton RCS氣體 取樣器而構成。以氣體取樣器採取微生物時,係以4 〇 L / 每分,進行採取4分鐘。 其次’關於照射離子發生裝置1之離子7,進行送出 離子,以及未照射離子發生裝置1之離子7,不進行送出 離子,使其自然衰退’以上述之氣體取樣器進行採取。進 行送出離子時,離子濃度係距離離子送出部l〇cm之空間 ,正負離子分別爲5萬個/ cm3。 其次’分別對於上述之進行送出離子及未進行送出離 子時,以上述之氣體取樣器,每隔15分鐘採取黑黴,進 行測定所採取菌之菌數。 圖7係關於實施例4之測定結果,表示浮游細菌殘存 率(% )之經時變化。圖7中,橫軸係對應經過時間,縱 •33- (28) 1235671 軸係與圖3同樣地對應於浮游菌殘存率(% ) ° 未進行送出離子時,經過1小時後之自然衰退之菌殘 存率爲75 %。另一方面,進行送出離子時5經過1小時 後之菌殘存率爲10%。 關於以上之測定,作爲判斷除去微生物效果爲有效之 大致上標準,若考慮微生物之採取精確度及濃度測定精確 度時,認爲與自然衰退之殘存率有10%之差異時爲有意 差。另外,若考慮試驗之精確度時,未送出離子時之自然 衰退,經過 1小時後之菌殘存率爲5 0 %以上之試驗條件 爲適宜的。 [實施例5] 作爲實施例5係以下述之條件實施。關於進行微生物 除去評估係使用圖2所示之評估微生物除去之裝置20。 該評估微生物除去之裝置20之容器1 8係使用內部空間之 尺寸爲底邊8cxn及長30cm之四角柱狀所形成者。其次, 容器8內部之環境空氣係溫度爲25 °C,相對濕度爲50% 〇 权囷處理微生物係使用小兒麻痒病毒(P 〇 1 i 〇 v】· r u S ) 。其次’將每cc分散數萬個小兒麻痺病毒之水溶液與空 氣混合成霧狀,以0 · 1 c c / m i η之比率,以1 · 6 m / s e c之 風速,由注入口 1 5 a供給於容器18內。 另外,關於照射離子7於上述之病毒以殺菌處理係距 離離子發生元件12之離子送出部份]〇cni之空間,使正 -34 - (29) 1235671 負離子分別爲10萬個/ cm3。 另外’關於採取照射上述離子7之殺菌處理後之小兒 麻痺病毒於採取器6,以溶液發泡器分離捕捉病毒。 其次,採取照射上述離子7殺菌處理後之小兒麻痺病 毒於採取器6,進行菌數之測定時,病毒之除去率爲78% [實施例6] 作爲實施例6係以下述之條件實施。圖8係本實施例 之評估浮游病毒除去之裝置之槪略構成圖,圖1 1係表示 依據離子濃度之流行性感冒病毒之細胞感染頻率圖,圖 12係表示依據離子濃度之克沙奇病毒(Coxsakie virus) 之細胞感染頻率圖,圖1 3係表示依據離子之小兒麻痺病 毒之細胞感染頻率圖。圖14係表示離子發生元件所生成 之正離子及負離子之質量光譜圖。圖15係未使離子發生 元件運作及使離子發生元件運作時,進行比較之評估試驗 流程圖。本實施例中,如圖15之流程圖所示,製作含微 生物之溶液後,使用試驗裝置,噴霧該溶液於空間中,進 行採取其空氣。另外,噴霧後,對於所噴霧之含有微生物 之空氣,進行放出具有殺菌作用之粒子及使其作用之步驟 。另外,進行放出該粒子及不進行放出時之試驗。以上之 方法所採取之溶液,例如以對照法,紅血球凝集反應等, 進行微生物濃度測定或活性度等之評估,評估殺菌或不活 化之效果,進行使粒子作用及不使其作用時之比較,可確 -35- (30) 1235671 定粒子之效果。另外,改變粒子之濃度或粒子之作用時間 ,對於殺菌或不活化程度,可調查照射時間依賴性或粒子 濃度依賴性。 本實施例係使用如圖8所示之評估微生物除去之裝置 30。 離子發生元件12係使用長3 7mm,寬15mm之平板狀 之表面放電元件。電極間交互外加正負高電壓,引起表面 電極部份表面放電,於大氣壓下之放電等離子生成正及負 離子。 離子發生元件係加裝固定於內徑爲 55mm、長爲 200mm之丙烯酸製圓筒型容器31之一端,內藏以上之容 器1 8之一側加裝病毒液噴霧器1 1,另一側則加裝病毒液 回收用之採取器6。 流行性感冒係接種於發育雞蛋之尿囊膜腔,以孵卵器 培養後,採取尿囊液,以此爲試驗病毒液。將 10ml之試 驗病毒液放出於玻璃製噴霧器(病毒液噴霧器11),連 接於容器18之一端。容器18之另一端係連接放入10ml 之PB S ( —)之玻璃製塵埃測定器(採取器6 )。噴霧器 中之來自氣體取樣器之壓縮空氣之吐出壓力,係以表壓調 整爲0.48hPa,由注入口噴霧試驗病毒於容器18內之風洞 31。 噴霧量爲 3.0ml (噴霧流量 〇·1ιβ1/ minx噴霧時間 3 Om i n ) 〇 此時,控制離子發生元件1 2爲不運作之狀態,對於 離子濃度爲20萬個/ cm3、10萬個/ cm3及5萬個/ cm3 進行比較。 -36- (31) 1235671 塵埃測定器係以每分鐘1 0L之吸引流量吸引捕集試驗 裝置內空氣30分鐘。塵埃測定器所吸引捕集試驗裝置內 空氣之PBS (-)爲試驗液,流行性感冒病毒係使用 main darby canine kidney (MDCK) cells 之對照法進 行測定。另外,克沙奇病毒及小兒麻痺病毒係以抗癌細胞 (Hela cell)之對照法進行測定。 另外,所謂對照法係將含病毒之液體,以與細胞相接 之方式注入,爲一種確認細胞感染病毒之方法,可調查病 毒之活性度,即感染病毒之頻率或病毒於細胞中增殖能力 之方法。 離子濃度係由設置如上述之離子發生元件 12之圓筒 型風洞 3 1之一側,以送風扇(未圖示),以風速4m / sec,使風流動,於另一側之距離該離子發生元件l〇cm處 ,設置 DAN科學製空氣離子計數器(產品號碼 83 -1001B ),測定該空間之離子濃度。空間環境溫度爲 25t ,相對濕度爲60 % RH。另外,關於離子發生係確認於溫 度爲〇°C、相對濕度爲1〇%至溫度爲4〇°C、相對濕度爲 90%之範圍。另外,上述送風扇係爲確認離子濃度而使用 ,於實際之微生物除去評估時,不使用送風扇,於圓型風 洞31之內部,設定由上述噴霧器11之噴霧所產生的風。 如圖11所示,未使離子發生元件運作時之流行性感 冒病毒之細胞感染頻率爲1〇〇%時,發生5萬、10萬及 20萬(個/ cm3 )離子時,大幅降低細胞感染頻率至3.8% 、2 · 6 %及0.5 %,確認因離子濃度增加,可提高除去流行 -37· (32) 1235671 性感冒病毒之性能。 另外,如圖12所示,未使離子發生元件運作時 沙奇病毒之細胞感染頻率爲100%時,發生5萬、10 20萬(個/ cm3 )離子時,大幅降低細胞感染頻率至 '2.6%及1。1%,確認因離子濃度增加,可提高除去 奇病毒之性能。 另外,如圖13所示,未使離子發生元件運作時 兒麻痺病毒之細胞感染頻率爲100%時,產生5萬、 及20萬(個/ cm3 )離子時,大幅降低細胞感染頻 1·0%、0.5%及0·4%,確認因離子濃度增加,可提高 小兒麻痺病毒之性能。 發生離子之組成係如圖14所示,正離子係以等 放電,電離空氣中之水分子,產生氫離子Η+,因溶 能量使空氣中之水分子與氫離子聚集(chstering) 另外’負離子係以等離子放電,電離空氣中之氧分子 分子,產生氧離子Ο厂,因溶媒及能量使空氣中之水 與氧離子聚集(clustering)者。 送出空間之正負離子包圍浮游於空氣中之病毒, 毒表面’因正負離子化學反應而生成活性源之過氧 Η 2 〇2或自由基· OH,破壞蛋白質而殺死。依此方法 有效地殺菌除去空氣中之病毒。 另外,調查病毒活性度之方法,可使用紅血球凝 應。紅血球凝集反應係將含有病毒之溶液,注入如含 血之溶液,觀察其血液凝集之方法。利用病毒存在時 之克 萬及 3.3% 克沙 之小 10萬 率至 除去 離子 媒及 者。 或水 分子 於病 化氫 ,可 集反 有雞 ,存 -38· (33) 1235671 在於病毒表面之紅血球凝集素,作用於多數之紅血球,使 紅血球發生凝集現象而可確認病毒之存在。 另外’調查病毒濃度之方法,以水溶液稀釋病毒成多 種濃度,分別確認是否產生紅血球凝集反應,相對地,亦 可調查活性病毒濃度,即具有活動紅血球凝集素之感染力 之病毒濃度。 [實施例7] φ 圖1 6係評估浮游病原性細菌除去之裝置之槪略圖。 圖17係表示20萬個/ cm3之離子濃度下之空氣中浮游葡 萄球菌(Staphylococcus)濃度之經時變化圖。離子發生 裝置係使用與實施例6相同物。圖18係表示於離子發生 — 元件及紫外線式臭氧發生裝置之空氣中浮游葡萄球菌濃度 之經時變化圖。空間環境係溫度爲25 °C,相對濕度爲60 % PH。另外,關於離子發生係確認於溫度爲0艺、相對濕 度爲10%至溫度爲4〇°C、相對濕度爲90%之範圍。 鲁 爲檢測離子發生元件對於存在於一定空間中之浮游葡 萄球菌之除去效果,本試驗係使用槪略構成與圖1所示相 同者。亦即,容器8係使用1 m3之空間之1 m X 1 m X 1 m之 FRP製容器之雨端加裝丙烯酸製板者。此容器內,於風量 爲2m3/ min之送風扇之上方空氣吹出口部份,加裝離子 .Sentence C [Embodiment] Example [Example 1] As Example 1 ', the following conditions were implemented. As for the evaluation of the removal of microorganisms, an apparatus i 0 for evaluating the removal of microorganisms as shown in FIG. 1 was used. The container 8 containing 10% of the microorganisms to be evaluated for this evaluation is the one having an internal space of 2.0 m in length and 2.5 m in height and 2.7 m in height. Secondly, the temperature of the ambient air inside the container 8 is 25 ° C, and the relative humidity is 42%. The internal space of the container 8 is stirred by the mixer 4. The stirring system with the mixer 4 was performed with an air volume of 4 m3 / min. Use of coliform bacteria as microorganisms. Regarding the supply of this coliform in the container 8, the microorganism injection port 5a is supplied in a mist form. Secondly, the coliforms are dispersed in the container 8 at a concentration of about 500 to 1,500 / m 3. The collector 6 is configured using a Biotest Hyton RCS gas sampler. When collecting microorganisms with a gas sampler, the collection was performed at 40 L / min for 4 minutes. Next, the ions 7 formed by the positive ions and the negative ions generated by the ion generating device 1 are irradiated. In this embodiment 1, various ion concentrations are changed, and each ion concentration is irradiated with the ions 7 for one hour to perform a sterilization treatment. The ion concentration is the distance of 10 cm from the ion sending part of the ion generating device 1 (ion generating port -28-(23) 1235671 2). Next, "coelenteritis was supplied to Guyi: Neihou" under the above-mentioned conditions, and the ions 7 were irradiated with the ion concentration for 1 hour, and then the coliform bacteria were collected by the above-mentioned gas sampler, and the number of the coliform bacteria was measured. Next, the ion concentration of various ions 7 is changed, and the measurement of each ion concentration is repeated. FIG. 3 shows the measurement results of Example 1. FIG. In FIG. 3, it corresponds to the ion concentration of ions 7 expressed in logarithm (number / cm: In addition, in FIG. 3, the vertical axis system corresponds to the phytoplankton residual rate (%). The phytoplankton residual rate is after the ion 7 is irradiated. The number of remaining bacteria that have not been sterilized is expressed in terms of ratio. As shown in FIG. 3, when the ion concentration emitted from the ion generator 1 is increased, it is confirmed that the residual rate of airborne bacteria in the air is reduced. If the number of positive and negative ions is 10,000 When the rate is above / cm3, the residual rate is also confirmed to be extremely low. Secondly, the general indoor ion concentration is 500 to 1,500 /, as a general standard for effective removal of microorganisms, it is considered to send positive and negative ion concentrations above / / cm3. It is appropriate. [Example 2] As Example 2, it was implemented under the following conditions. The micro-removal evaluation was performed using the apparatus for evaluating microorganism removal shown in Fig. 1. The container 8 for evaluating the micro-removal device 10 was used. The internal dimensions are 2.0m in length, 2.5m in width, and 2.7m in height. Be sure to take the measurement and change the horizontal axis) °. In addition to the positive and negative values, the rate of rapid decline is between cm3 and 10,000 creatures, and between -29 and (24) 1235671. Second, the ambient air temperature inside the container 8 is 251, and the relative humidity is 42%. The internal space of the container 8 is stirred by the mixer 4. The stirring with the mixer 4 was performed with an air volume of 4 m 3 / in. Use of coliform bacteria as microorganisms. Regarding the supply of this coliform in the container 8, the microorganism injection port 5a is supplied in a mist form. Next, the coliforms were dispersed in the container 8 at a concentration of about 1,000 pieces / m3. In addition, the collector 6 is configured using a Biotest Hyton RCS gas sampler. When the microorganism was collected by the gas sampler, it was collected at 40 L / min 'for 4 minutes. Next, the ions 7 irradiated with the ion generating device 1 are sent out, and the ions 7 not irradiated with the ion generating device 1 are not sent out. The ions are naturally decayed, and they are collected by the above-mentioned gas sampler. When the ions are sent out, the ion concentration is a distance of 10 cm from the ion sending part, and the positive and negative ions are 50,000 / cm3, respectively. Next, when the above-mentioned ion delivery and non-ion delivery are performed respectively, coliform bacteria are collected every 15 minutes by the above-mentioned gas sampler, and the number of bacteria of the collected coliform bacteria is measured. Fig. 4 shows the measurement results of Example 2 and shows the change with time of the residual rate (%) of the planktonic bacteria. In FIG. 4, the horizontal axis system corresponds to the elapsed time, and the vertical axis system corresponds to the phytoplankton residual rate (%) as in FIG. 3. When the ion is not sent out, the residual bacteria decay rate after natural lapse of 1 hour is 80%. On the other hand, when the ion was sent out, the residual bacteria rate after 10 hours had passed was 10%. Regarding the above measurement, -30 · (25) 1235671 is a general standard for judging the effect of removing microorganisms. If the accuracy of the microorganisms and the accuracy of concentration measurement are considered, it is considered that the residual rate of natural decay is 10%. Differences are intentional. In addition, if the accuracy of the test is considered, the natural decay when the ions are not sent out, and the test conditions of 50% or more of residual bacteria rate after 1 hour are suitable. / Figure 5 shows the photos of coliforms taken 15 minutes after the ion release and non-ion release ~. FIG. 5 (a) is a person who performs ion emission, and FIG. 5 (b) is a person who does not perform ion emission. In addition, regarding the photography of the coliforms shown in FIG. 5, the coliforms taken in each of the above cases were cultured on an agar medium at 34 ° C and 10.0% RH for 48 hours, and then photographed. In addition, in FIG. 5, the size of the petri dish is 9 cm. ~ When ion delivery was performed, as shown in Fig. 5 (a), no colony formation of coliform bacteria was observed. On the other hand, when ion delivery was not performed, as shown in FIG. 5 (b), colonies of coliform bacteria were observed. It can be seen from the results shown in FIG. 5 that sterilization is possible with ions. &lt; 1 [Example 3] Example 3 was implemented under the following conditions. As for the evaluation of the removal of microorganisms, an apparatus for evaluating the removal of microorganisms shown in FIG. 1 was used. The container 8 of the apparatus for evaluating the removal of microorganisms is a container having a size of 2.0m in length, 2.5m in width, and 2.7m in height. Second, the ambient air temperature inside the container 8 is 25 ° C, and the relative humidity is 42%. In addition, in the third embodiment, as described in the invention below, stirring is performed in the container 8. • 31-(26) 1235671 泮 In comparison with non-stirring, the space in the stirring container 8 is stirred with a mixer 4 with an air volume of 4 m3 / min. As a microorganism, Cladosporium, a fungus, was used. When the black mold is supplied into the container 8, the black mold is supplied from the microorganism injection port 5a in a mist state. Next, the concentration of black mold was dispersed in the container 8 at about 1,000 pieces / m 3. ^ The collector 6 is constructed using a Biotest Hyton RCS gas sampler. When collecting microorganisms with a gas sampler, the collection was performed at 40 L / φ per minute for 4 minutes. Next, with the agitator 4 and without the agitator 4, the above-mentioned gas sampler was used to collect airborne bacteria in the air every 15 minutes, and the number of bacteria was measured. ‘FIG. 6 shows the measurement results of Example 3, and shows the change with time of the residual rate (%) of planktonic fungi in the air that naturally decays with or without stirring. In FIG. 6, the horizontal axis system corresponds to the elapsed time, and the vertical axis system corresponds to the phytoplankton residual rate (%) as in FIG. 3. · When stirring is not performed, after 45 minutes, the residual rate of bacteria whose detection limit is 12%. On the other hand, during the stirring, the residual rate of bacteria was 80% because of natural decay after 1 hour. ^ From the above results, adding agitation means can suppress the natural fall of bacteria, and it is easy to evaluate and remove planktonic microorganisms. In particular, when the mass of bacteria is large, stirring is effective. [Example 4;] -32- (27) 1235671 As Example 4, it was implemented under the following conditions. Regarding the microbial removal delta evaluation, the apparatus 10 for evaluating microbial removal shown in Fig. 1 was used. The container 8 of the apparatus 10 for evaluating the removal of microorganisms is a person using an internal space with a size of 2.0 m in length, 2.5 m in width, and a height of a blade. Secondly, the temperature of the ambient air in the container 8 is 25 ° C, and the relative humidity is 42%. The internal space of the container 8 is stirred by the mixer 4. The stirring system with the mixer 4 was performed with an air volume of 4 m 3 / m i η. Cladosporium is used as a microorganism. When supplying the black mold to the container 8, the microorganism injection port 5a is supplied in a mist form. Secondly, the concentration of black mold was dispersed in the container 8 at about 15 000 pieces / m3. The collector 6 is configured using a Biotest Hyton RCS gas sampler. When collecting microorganisms with a gas sampler, the collection was performed at 40 L / min for 4 minutes. Next, "the ions 7 irradiated to the ion generating device 1 are sent out, and the ions 7 not irradiated to the ion generating device 1 are not sent out, so that they naturally decay." When the ions are sent out, the ion concentration is a distance of 10 cm from the ion sending part, and the positive and negative ions are 50,000 / cm3, respectively. Next, when the ions are sent out and the ions are not sent out, a black mold is taken every 15 minutes with the gas sampler described above, and the number of bacteria taken is measured. Fig. 7 shows the measurement results of Example 4 and shows the change with time of the residual rate (%) of planktonic bacteria. In Fig. 7, the horizontal axis corresponds to the elapsed time, and the vertical axis of 33- (28) 1235671 corresponds to the residual rate of phytoplankton (%) in the same manner as in Fig. 3. ° When the ion is not sent, the natural decay rate after 1 hour has elapsed. The residual rate of bacteria was 75%. On the other hand, the residual bacteria rate after 5 hours passed when the ion was fed out was 10%. Regarding the above measurement, as a general standard for judging whether the effect of removing microorganisms is effective, if the accuracy of measuring microorganisms and the accuracy of measuring the concentration are considered, a difference of 10% from the residual rate of natural decline is considered to be an intentional difference. In addition, if the accuracy of the test is taken into consideration, the natural decay when the ions are not sent out, and the test conditions for a bacteria residual rate of 50% or more after 1 hour are suitable. [Example 5] Example 5 was implemented under the following conditions. As for the evaluation of the removal of microorganisms, the apparatus 20 for evaluating the removal of microorganisms shown in Fig. 2 was used. The container 18 of the apparatus 20 for evaluating the removal of microorganisms was formed by using a quadrangular column with a bottom edge size of 8cxn and a length of 30 cm. Secondly, the temperature of the ambient air system in the container 8 is 25 ° C and the relative humidity is 50%. Poliovirus (P 0 1 i 0 v) · r u S) is used as the treatment microorganism. Secondly, an aqueous solution in which tens of thousands of polioviruses are dispersed per cc is mixed with air to form a mist, and it is supplied to the injection port 1 5 a at a rate of 0 · 1 cc / mi η and a wind speed of 1 · 6 m / sec. Inside the container 18. In addition, regarding the space in which the above-mentioned virus was irradiated with ions 7 and the ions were sent from the ion generating element 12 in a sterilizing treatment] space, the positive -34-(29) 1235671 negative ions were 100,000 / cm3, respectively. In addition, the poliomyelitis virus after the sterilization treatment by irradiating the above-mentioned ions 7 was collected in the collector 6 by a solution foamer to capture the virus. Next, the poliomyelitis virus sterilized by irradiating the ion 7 was collected on the collector 6, and when the number of bacteria was measured, the virus removal rate was 78%. [Example 6] Example 6 was performed under the following conditions. FIG. 8 is a schematic configuration diagram of a device for evaluating the removal of planktonic viruses in this embodiment, and FIG. 11 is a graph showing the frequency of cellular infection of influenza virus based on ion concentration, and FIG. 12 is a diagram of kerax virus based on ion concentration (Coxsakie virus) cell infection frequency chart, Figure 13 shows the ion infection-based polio virus frequency chart. Fig. 14 is a mass spectrum chart showing positive ions and negative ions generated by the ion generating element. Fig. 15 is a flowchart of an evaluation test for comparison when the ion generating element is not operated and when the ion generating element is operated. In this embodiment, as shown in the flowchart of Fig. 15, after preparing a solution containing a microorganism, the test device is used to spray the solution into a space to take in air. In addition, after spraying, the sprayed microbe-containing air is subjected to a step of releasing particles having a bactericidal effect and causing them to act. In addition, tests were performed when the particles were discharged and when the particles were not discharged. The solution used in the above method is, for example, the control method, the red blood cell agglutination reaction, etc., to evaluate the concentration of microorganisms or the activity, etc., to evaluate the effect of sterilization or inactivation, and to compare the effect of particles with and without them This confirms the effect of -35- (30) 1235671 fixed particles. In addition, by changing the concentration of particles or the action time of particles, it is possible to investigate the irradiation time dependence or particle concentration dependence on the degree of sterilization or inactivation. This embodiment uses an apparatus 30 for evaluating the removal of microorganisms as shown in FIG. The ion generating element 12 is a flat surface discharge element having a length of 37 mm and a width of 15 mm. The application of positive and negative high voltages between the electrodes causes surface discharge on the surface of the electrode part. The discharge plasma at atmospheric pressure generates positive and negative ions. The ion generating element is fixed at one end of an acrylic cylindrical container 31 having an inner diameter of 55 mm and a length of 200 mm. A virus sprayer 11 is installed on one side of the container 18 or more, and the other side is provided with The pick-up device 6 is used for virus liquid recovery. Influenza was inoculated into the allantoic membrane cavity of a developing egg, and cultured in an incubator, then the allantoic fluid was taken as the test virus fluid. 10 ml of the test virus solution was put out of a glass sprayer (virus solution sprayer 11) and connected to one end of a container 18. The other end of the container 18 is connected to a glass dust detector (taker 6) containing 10 ml of PBS (-). The discharge pressure of the compressed air from the gas sampler in the sprayer was adjusted to 0.48 hPa by the gauge pressure, and the virus was sprayed into the wind tunnel 31 in the container 18 through the injection port. The spray volume was 3.0 ml (spray flow rate: 0.1 μm1 / minx spray time: 3 Om in). At this time, the ion generating element 12 was controlled to be in a non-operation state, and the ion concentration was 200,000 / cm3, 100,000 / cm3. And 50,000 pieces / cm3. -36- (31) 1235671 The dust tester sucks the air in the test device at a suction flow rate of 10L per minute for 30 minutes. The PBS (-) in the air in the capture test device attracted by the dust tester is the test solution. Influenza viruses are measured using the control method of main darby canine kidney (MDCK) cells. In addition, the Quesha virus and polio virus were measured by a control method against Hela cells. In addition, the so-called control method is to inject a virus-containing liquid into the cell in a way that confirms that the cell is infected with the virus. It can investigate the activity of the virus, that is, the frequency of virus infection or the ability of the virus to multiply in the cell. method. The ion concentration is from one side of the cylindrical wind tunnel 31 provided with the ion generating element 12 as described above, and a fan (not shown) is used to make the wind flow at a wind speed of 4m / sec, and the ion is at a distance from the other side. An air ion counter (product number 83-1001B) manufactured by DAN Scientific was set at 10 cm of the generating element, and the ion concentration in the space was measured. The space ambient temperature is 25t and the relative humidity is 60% RH. The ion generation system was confirmed to have a temperature of 0 ° C and a relative humidity of 10% to a temperature of 40 ° C and a relative humidity of 90%. In addition, the above-mentioned blower is used to confirm the ion concentration. In the actual evaluation of microbial removal, the blower is not used, and the wind generated by the spray of the sprayer 11 is set inside the circular wind tunnel 31. As shown in Figure 11, when the frequency of cellular infection of influenza virus when the ion generating element is not operating is 100%, when 50,000, 100,000, and 200,000 (pieces / cm3) ions occur, the cell infection is greatly reduced. Frequency to 3.8%, 2.6%, and 0.5%. It was confirmed that the increase in ion concentration can improve the performance of removing epidemic -37 · (32) 1235671 influenza virus. In addition, as shown in FIG. 12, when the frequency of Sachs virus cell infection is 100% when the ion generating element is not operated, when 50,000 and 10.2 million (pieces / cm3) ions occur, the frequency of cell infection is greatly reduced to '2.6. % And 1.1%. It was confirmed that the increase in ion concentration can improve the performance of removing parvovirus. In addition, as shown in FIG. 13, when the frequency of cell infection of poliovirus is 100% when the ion generating element is not operated, when 50,000 and 200,000 (pieces / cm3) ions are generated, the frequency of cell infection is greatly reduced by 1.0. %, 0.5% and 0.4%, it was confirmed that the performance of poliovirus can be improved due to the increase in ion concentration. The composition of the generated ions is shown in Figure 14. The positive ions are discharged by isoelectric discharge to ionize water molecules in the air to generate hydrogen ions Η +. The water molecules and hydrogen ions in the air are chstering due to the dissolved energy. It is a plasma discharge that ionizes oxygen molecules in the air to produce oxygen ions. Plant 0, which causes water and oxygen ions in the air to cluster (clustering) due to the solvent and energy. The positive and negative ions sent out of the space surround the virus floating in the air, and the toxic surface ’is caused by the chemical reaction of the positive and negative ions to generate an active source of peroxy Η 2 02 or free radicals · OH, which destroys the protein and kills it. This method effectively sterilizes and removes viruses in the air. As a method for investigating the activity of the virus, erythrocyte coagulation can be used. The erythrocyte agglutination reaction is a method of injecting a solution containing a virus into a blood-containing solution and observing the blood's agglutination. Use gram of virus in the presence of virus and 3.3% of gram of sand to remove ionic media and 100,000. Or water molecules can cause chickens to collect pathogens. -38 · (33) 1235671 The red blood cell agglutinin on the surface of the virus acts on most red blood cells, causing the red blood cells to agglutinate and confirm the existence of the virus. In addition, the method of investigating the virus concentration is to dilute the virus to various concentrations with an aqueous solution to confirm whether a erythrocyte agglutination reaction occurs. In contrast, it is also possible to investigate the active virus concentration, that is, the virus concentration having the infectivity of active erythrocyte agglutinin. [Example 7] Fig. 16 is a schematic diagram of a device for evaluating the removal of planktonic pathogenic bacteria. Figure 17 is a graph showing the change over time of the concentration of Staphylococcus in the air at an ion concentration of 200,000 / cm3. The ion generator was the same as that used in Example 6. Fig. 18 is a graph showing the change over time of the concentration of staphylococcus in the air in the ion generating element and the ultraviolet ozone generating device. The space environment temperature is 25 ° C and the relative humidity is 60% PH. The ion generation system was confirmed to have a temperature of 0 ° C, a relative humidity of 10%, a temperature of 40 ° C, and a relative humidity of 90%. Lu In order to detect the removal effect of staphylococcus aureus existing in a certain space by the ion generating element, this experiment uses the same basic structure as shown in FIG. 1. That is, the container 8 is an acrylic plate made of acrylic resin at the rain end of a 1 m X 1 m X 1 m FRP container using a space of 1 m3. Inside this container, ions are installed on the air blowing outlet above the blower with an air volume of 2m3 / min.

發生元件1。 I 另外,爲使所噴霧菌長期間浮游,於容器8之四角裝 置4座15 cm方形軸流風扇(axi a】-flow fan ) 4,風向朝 (34) 1235671 上。此容器8之丙烯酸製板部份之一端設有菌液噴霧用之 注入管5,以此爲試驗裝置。 試驗菌係接種保存株於胰化酪蛋白大豆瓊脂培養基( BBL’Trypticase soy agar),於 35°C 下,培養 24 小時。 將該菌以滅菌生理食鹽液稀釋調整洗淨後,作爲試驗菌。 將1 0ml之試驗菌液放入玻璃製噴霧器,連接於試驗 裝置之一端。容器18之另一端係連接放入100ml之滅菌 生理食鹽液之玻璃製塵埃測定器。噴霧器中之來自氣體取 樣器之壓縮空氣之吐出壓力,係以表壓調整爲0.48 hP a, 由噴霧口噴霧試驗菌。噴霧量爲1·〇πι1 (噴霧流量0.1ml / min X噴霧時間lOmin )。噴霧菌液的同時,使軸流扇4 運作,直至試驗終了間,進行連續運轉。 噴霧終了時,將容器8內之空氣,以塵埃測定器,每 分鐘10L之吸引流量,吸引捕集1〇分鐘。以此爲〇分値 。運作離子發生元件1時,離子發生元件與送風扇同時地 運作。運作開始後,經過一定時間後,與0分値同樣地吸 引捕集谷器內空氣100L。離子發生濃度爲20萬個/ cm3 〇 另外’不使離子發生元件1運作時(自然衰退値)亦 不使離子發生元件運作,僅送風扇4運作之狀態運轉,每 糸至時時間,吸引捕集容器內空氣。 另外,爲進行與臭氧比較之對照實驗,使用紫外線式 臭氧發生裝置(OZ51N — 1、SEN特殊光源株式會社), Μ與離子發生元件所生成之臭氧量相同之臭氧生成量 -40- (35) 1235671 1.63 7mg/h(22t: ,17% RH )進行試驗。 塵埃測定器所吸引捕集之容器內空氣之滅菌生理食鹽 液爲試驗液,使用滅菌生理食鹽液將其進行階段稀釋,將 原液及各稀釋液塗抹於胰化酪蛋白大豆瓊脂培養基(BB L )’於3 5 °C下,培養4 8小時。培養後,計算培養基上發 育菌落數,表示吸引空氣之菌數。 如圖17所示,發生離子與未使離子發生元件運作時 相比較,經3 0分鐘過後,確認浮游菌濃度約減少至1 0分 之1。進而,經過60分鐘後,未發現有浮游菌之檢出。 如圖1 8所示,離子發生元件與紫外線式臭氧發生裝 置相比較,經60分鐘過後,確認浮游菌濃度約減少至10 分之1。依此,對於院內感染之代表菌之葡萄球菌,依實 施例6所記述之作用,確認其殺菌作用。 [實施例8] 圖19係表示20萬個/ cm3之離子濃度下,空氣中浮 游芽胞桿菌(Bacillus )濃度之經時變化圖。離子發生裝 置係使用與實施例6相同物。圖20係表示於離子發生元 件及紫外線式臭氧發生裝置之空氣中浮游芽胞桿菌濃度之 經時變化圖。 爲檢測離子發生元件對於存在於一定空間中之浮游芽 胞桿囷之除去效果,本試驗中係使用1 m 3之空間之1 m X lm X lm之FRp製容器之兩端加裝丙烯酸製板者。此容器 內,於風量爲8m3/ min之送風扇之上方空氣吹出口部份 -41 - (36) 1235671 ,加裝離子發生元件。 另外,爲使所噴霧菌長期間浮游,於容器之四角裝置 4座15cm方形軸流風扇4,風向朝上。此容器8之丙稀 酸製板部份之一端設有菌液噴霧用之注入管1 5,以此爲 試驗裝置。 試驗菌係接種日抗基孢子形成用培養基(日本抗生物 質醫藥品基準,昭和57年6月30日厚生省告示第117號 ),於3 5 °C下,培養7天。將該菌以滅菌生理食鹽液洗 淨後,以65 °C ’ 30分鐘加熱處理,於顯微鏡下確認形成 芽胞。將其以滅菌生理食鹽液洗淨稀釋後者,作爲芽胞使 用。 將10m]之試驗菌液放入玻璃製噴霧器,連接於試驗 裝置之一端。另一端係連接放入100ml之滅菌生理食鹽液 之玻璃製塵埃測定器。噴霧器中之來自氣體取樣器之壓縮 空氣之吐出壓力,係以表壓調整爲0.48hPa,由噴霧□噴 霧試驗菌。噴霧量爲1·〇π)1(噴霧流量0.1m】/minx噴霧 時間1 0 ιώ i η )。菌液噴霧的同時,使軸流扇4運作,直至 試驗終了間,進行連續運轉。 噴霧終了時’將容器內之空氣,以塵埃測定器,每分 鐘10L之吸引流量,吸引捕集10分鐘。以此爲〇分値。 運作離子發生元件1時,離子發生元件與送風扇同時地運 作。運作開始後,經過一定時間後,與0分値同樣地吸引 捕集容器內空氣100L。離子發生濃度爲20萬個/ cm3。 另外,不使離子發生元件1運作時(自然衰退値)亦 • 42· (37) 1235671 不使離子發生元件運作,僅送風扇4運作之狀態運轉,每 經時時間,吸引捕集容器內空氣。空間環境係溫度爲25 t,相對濕度爲60 % PH。另外,關於離子發生係確認於 溫度爲0 °C、相對濕度爲1 〇 %至溫度爲4 〇 °C、相對濕度 爲90%之範圍。 爲進行與臭氧比較之對照實驗,使用紫外線式臭氧發 生裝置(OZ5 1N - 1、SEN特殊光源株式會社),以與離 子發生元件所生成之臭氧量相同之臭氧生成量1.637mg/ h(22°C,17%RH)進行試驗。 塵埃測定器所吸引捕集之容器內空氣之滅菌生理食鹽 液爲試驗液,將此使用滅菌生理食鹽液進行階段稀釋,將 原液及各稀釋液塗抹於胰化酪蛋白大豆瓊脂培養基(B B L ),於35°C下,培養48小時。培養後,計算培養基上發 育菌落數,表示吸引空氣之菌數。 如圖19所示,發生離子與未使離子發生元件運作時 相比較,經3 0分鐘過後,確認浮游菌濃度約減少至1 0分 之1。進而,經過12 0分鐘後’未發現有浮游菌之檢出。 如圖20所示,離子發生元件與紫外線式臭氧發生裝 置相比較,經60分鐘過後,確認浮游菌濃度約減半。依 此,對於形成具有耐熱性芽胞之芽胞桿菌,依實施例6所 記述之作用,確認其殺菌作用。炭疽菌與芽胞桿菌爲同屬 菌,可期待其效果。 [實施例9] -43 - (38) 1235671 圖2 1係表示配置於離子發生元件吹出口風路之空氣 調節裝置之斷面圖。圖22係表示相對於容積27L之空間 之離子噴出量之60分鐘後之空氣中浮游病毒之細胞感染 頻率圖。圖23係表示於容量30 m3之空間,以 1分鐘分 別供給54〇萬個/ cm3正負離子時,空氣中病毒細胞感染 頻率之經時變化圖。 於圖22所示之試驗中,爲檢測依離子噴出量,對於 存在空間中之浮游流行性感冒病毒之細胞感染頻率之減低 效果,本試驗中所使用 27L之空間係於 30cmx30cmx 30cm之氯化烯製容器之兩端加裝病毒噴霧裝置及回收裝 置者。另外,於此容器內,於送風扇之上方空氣吹出口部 份,加裝離子發生元件。另外,爲達成使所噴霧之病毒長 時間浮游之目的,設置軸流扇之風向朝上。 流行性感冒病毒(Influenza virus A (HI NI) A/PR8 / 34:ATCC VR-95係接種於發育雞蛋之尿囊膜腔,以孵卵 器培養後,採取尿囊液,以此爲試驗病毒液。將ΙΟηαΙ之 試驗病毒液放入玻璃製噴霧器,連接於試驗裝置之一端。 另一端係連接放入1 0 0 m 1之滅菌生理食鹽液之玻璃製塵埃 測定器。噴霧器中之來自氣體取樣器之壓縮空氣之吐出壓 力,係以表壓調整爲0.48hPa,由噴霧口噴霧試驗菌。噴 霧量爲3.0ml (噴霧流量〇.lml/minx噴霧時間30min) 。噴霧病毒液的同時,使軸流扇4運作,直至試驗終了間 ,進行連續運轉。 噴霧終了時,將容器內之空氣,以塵埃測定器,每分 •44 - (39) 1235671 鐘10L之吸引流量,吸引捕集30分鐘。以此爲0分値。 運作開始後1小時,與0分値同樣地吸引捕集容器內空氣 100L。塵埃測定器所吸弓|捕集試驗裝置內空氣之PBS (-)爲試驗液,流行性感冒病毒係使用 MDCK細胞之對照 法進行測定。調製離子發生元件之輸入電壓,而調整離子 噴出量。 正負離子噴出量分別爲0個/cm3·分之細胞感染頻 率爲100%時,確認27萬個/ cm3 ·分以上之離子噴出量 之細胞感染頻率急速地降低,確認正負離子噴出量分別爲 27萬個/ cm3 ·分以上時具有降低病毒感染能力之效果。 進而,爲確認實際上使用於居住環境空間之效果,如 圖23所示之試驗表示,空間容積30 m3內,設置如圖21 所示之空氣調節裝置60,卸下集塵過濾器64b及脫臭過 濾器64a之狀態,使離子發生元件65運轉時,空間內之 浮游病毒之殘存率。 在此,說明圖2 1所示之空氣調節裝置60之構成時, 該空氣調節裝置60係於室內裝置61之前面形成空氣吸入 口 62’裝置61之上方形成空氣吹出口 63。空氣吸入口 62設有脫臭過濾器64a及集塵過濾器6“,另外,空氣吹 出口 63之附近設有離子發生元件65及該高壓電源66所 形成之離子發生裝置67。其次,裝置內部之送風扇68將 空氣吸入口 62所吸入之空氣,由空氣吹出口 63排出於外 部’此時,因離子發生裝置67之驅動,放出離子化空氣 -45- (40) 1235671 如上述構成之空氣調節裝置,於吹出風路上配設離子 發生元件65,由吸入口 62所吸入之空氣,由吹出口 63 排出時,使該空氣中含有離子,可放出離子於空間內。因 此,不僅是所吸入之空氣附加離子,空間內全體均可附加 離子。 病毒濃度測定係與圖22之試驗所進行者同式樣。以 1分鐘分別供給540萬個/ cm3之正負離子。明白1小時 之細胞感染頻率降至10分之1。 如此’關於實際上使用於居住環境之空氣調節裝置之 容積,明白可評估空氣中病毒不活化效果。 送出空間之正負離子包圍浮游於空氣中之病毒,於病 毒表面,因正負離子化學反應而生成活性源之過氧化氫 H202或自由基· OH,破壞蛋白質而殺死。依此方法,可 有效地殺菌除去空氣中之病毒。 另外’本實施例中,離子係表示正負離子雙方者,關 於離子濃度,各離子濃度約爲相等者,記錄其平均値。 另外’於上述全部之實施例中,作爲粒子放出方法, 使用勒納爾效應,亦即使液體產生噴射或振動等作用,使 用物理性分離,使帶有電荷之粒子化而生成之方法,均可 得到本發明之效果。 另外’作爲粒子,使用正離子、負離子及正負離子之 混合氣體或上述以外之α射線及/3射線等之帶電粒子或、 各種等離子化氣體粒子、自由基等之粒子以及藥劑粒子等 ’亦可得到與本發明相同之效果。 -46- (41) 1235671 發明之功效 如以上之說明,依據本發明,於一定的空間中,使微 生物浮游,對於該微生物,照射離子等之殺菌處理微生物 / 用之粒子’之後,採取微生物,進行測定,達成可評估測 - 定上述粒子對於微生物之殺菌處理能力之功效。 &lt; 【圖式簡單說明】 · 圖1係表示有關本發明之評估微生物除去之裝置之第 1實施型態之槪略構成圖。 圖2係表示有關本發明之評估微生物除去之裝置之第 2實施型態之槪略構成圖。 &lt; 圖3爲關於實施例1之測定結果,改變離子濃度殺菌 處理時,所採取微生物之測定結果。 圖4爲關於實施例2之測定結果,進行送出離子與未 進行送出離子時,所採取微生物之測定結果。 0 圖5爲關於實施例2中,攝影所採取之微生物而得之 照片。圖5 ( a )爲進行送出離子時所採取之微生物之照 片,圖5 ( b )爲未進行送出離子時所採取之微生物之照 ’ 片。 圖6爲關於實施例3之測定結果,攪拌容器內與未攪 · 拌時,所採取微生物之測定結果。 . 圖7爲關於實施例4之測定結果,進行送出離子與未 進行送出離子時,所採取微生物之測定結果。 -47 - (42) !235671 圖8係表示評估微生物除去之裝置之第3實施型態及 實施例6之槪略構成圖。 圖9係表示評估浮游微生物除去之裝置之第4實施型 態之槪略構成圖。 圖1 〇係表示評估浮游病毒除去之裝置之第5實施型 態之槪略構成圖。 圖1 1係表示依據實施例6之離子濃度之流行性感冒 病毒之細胞感染頻率圖。 圖1 2係表示依據實施例6之離子濃度之克沙奇病毒 之細胞感染頻率圖。 圖1 3係表示依據實施例6之離子濃度之小兒麻痺病 毒之細胞感染頻率圖。 圖14係表示由實施例6之離子發生元件所生成之正 離子及負離子之質量光譜圖。 圖1 5係表示實施例6之評估試驗流程圖。 匱1 1 6爲實施例7之評估浮游病原性細菌除去之裝置 之槪略圖。 圖17係表示實施例7之20萬個/ cm3之離子濃度下 ,空氣中浮游蔔萄球菌(Staphyl〇coccus )濃度之經時變 化圖。 圖1 8係表示實施例7之離子發生元件及紫外線式臭 氧發生裝置中’空氣中浮游葡萄球菌濃度之經時變化圖。 圖1 9係表示實施例8之2〇萬個/ cm3之離子濃度下 ’空氣中浮游芽胞桿菌(Baci]】us )濃度之經時變化圖。 • 48 - (43) 1235671 圖20係表示實施例8之離子發生元件及紫外線式臭 氧發生裝置中,空氣中浮游芽胞桿菌濃度之經時變化圖。 圖2 1係表示實施例9之配設於離子發生元件吹出口 風路之空氣調節裝置之斷面圖。 / 圖22係表示實施例9之依據離子噴出量之空氣中浮 . 游病毒之細胞感染頻率圖。 圖23係表示實施例9之依據離子噴出量之空氣中病 毒細胞感染頻率之經時變化圖。 Φ 符號說明 1 離 子 發 生 裝 置 2 離 子 發 生 □ 3 微 生 物 採 取 管 3a 微 生 物 採 取 □ 4 攪 拌 機 5 微 生 物 注 入 管 5a 微 生 物 注 入 □ 6 微 生 物 採 取 器 7 ik丄 子 8 容 器 10 評 估 微 生 物 除去之裝置 11 微 生 物 噴 霧 器 12 離 子 發 生 元 件 12a 離 子 發 生 電 極 49 · (44) (44)1235671 13 微生物採取管 13a 微生物採取口 15 微生物注入管 15a 微生物注入口 18 容器 20 評估微生物除去之裝置 3 1 風洞 35 容器Generating element 1. In addition, in order to float the sprayed bacteria for a long period of time, four 15 cm square axial-flow fans (axi a) -flow fans 4 are installed at the four corners of the container 8 with the wind direction (34) 1235671. One end of the acrylic plate portion of the container 8 was provided with an injection tube 5 for spraying bacterial liquid, and this was used as a test device. The test strains were inoculated and preserved in trypticase soy agar medium (BBL ′ Trypticase soy agar) and cultured at 35 ° C for 24 hours. This bacterium was diluted with sterilized physiological saline solution, adjusted and washed, and then used as a test bacterium. 10 ml of the test bacterial solution was put into a glass sprayer and connected to one end of the test device. The other end of the container 18 is connected to a glass dust tester containing 100 ml of a sterilized physiological saline solution. The discharge pressure of the compressed air from the gas sampler in the sprayer was adjusted to 0.48 hPa with the gauge pressure, and the test bacteria were sprayed from the spray port. The spray amount was 1.0 μm (the spray flow rate was 0.1 ml / min X the spray time was 10 min). While spraying the bacterial solution, the axial fan 4 was operated until the end of the test, and continuous operation was performed. When the spraying is finished, the air in the container 8 is sucked and collected for 10 minutes by a suction flow rate of 10 L per minute with a dust measuring device. Take this as 0 minutes. When the ion generating element 1 is operated, the ion generating element and the fan are operated simultaneously. After the start of the operation, after a certain period of time, 100 L of air in the trough trap was sucked in the same way as 0 minutes. The ion generation concentration is 200,000 / cm3. In addition, when the ion generating element 1 is not operated (natural decay), the ion generating element is not operated, and only the fan 4 is operated, and each time it is attracted to capture Collect the air inside the container. In addition, in order to perform a comparison experiment with ozone, a UV-type ozone generator (OZ51N-1, SEN Special Light Source Co., Ltd.) is used, and the ozone generation amount is the same as the ozone generation amount of the ion generating element -40- (35) 1235671 1.63 7mg / h (22t:, 17% RH) for testing. The sterilized physiological salt solution of the air trapped in the container attracted by the dust tester was used as a test solution, and the sterilized physiological salt solution was used to dilute it step by step. 'Incubate at 3 5 ° C for 4 8 hours. After incubation, the number of colonies on the medium was counted, indicating the number of bacteria that attracted air. As shown in Fig. 17, compared with the case where the ion generating element was not operated, it was confirmed that the concentration of phytoplankton had been reduced to about 1 / 10th after 30 minutes. Furthermore, no phytoplankton was detected after 60 minutes. As shown in Fig. 18, after comparing the ion generating element with the ultraviolet type ozone generating device, it was confirmed that the concentration of plankton was reduced to about 1/10 after 60 minutes. Accordingly, the bactericidal effect of Staphylococcus, a representative bacterium of nosocomial infection, was confirmed in accordance with the effect described in Example 6. [Example 8] Fig. 19 is a graph showing the change over time of the concentration of Bacillus in the air at an ion concentration of 200,000 / cm3. The same ion generating apparatus was used as in Example 6. Fig. 20 is a graph showing the change over time of the concentration of planktonic bacillus in the air of an ion generating element and an ultraviolet-type ozone generating device. In order to test the removal effect of the ion-generating element on the planktonic spores existing in a certain space, an acrylic plate was installed at both ends of a 1 m X lm X lm FRp container in a space of 1 m 3. . Inside this container, the air blowing outlet -41-(36) 1235671 above the air blower with an air volume of 8m3 / min is equipped with an ion generating element. In addition, in order to float the sprayed bacteria for a long period of time, four 15 cm square axial fans 4 are installed at the four corners of the container, with the wind direction upward. One end of the acrylic plate portion of the container 8 was provided with an injection tube 15 for spraying bacterial liquid, and this was used as a test device. The test bacterial strains were inoculated with a medium for basal spore formation (Japanese Antibiotics Standard, June 30, 1987, Ministry of Health and Welfare Notice No. 117), and cultured at 35 ° C for 7 days. After the bacteria were washed with a sterilized physiological saline solution, heat treatment was performed at 65 ° C 'for 30 minutes, and spore formation was confirmed under a microscope. The latter was washed with a sterile physiological saline solution and diluted with the latter, and used as spores. The test bacteria solution of 10m] was put into a glass sprayer and connected to one end of the test device. The other end is connected to a glass dust tester containing 100 ml of a sterile physiological saline solution. The discharge pressure of the compressed air from the gas sampler in the sprayer was adjusted to 0.48hPa with the gauge pressure, and the test bacteria were sprayed by spraying. The spray amount is 1.0 π) 1 (spray flow rate of 0.1m) / minx spray time 10m. While spraying the bacterial solution, the axial flow fan 4 was operated until the end of the test, and the continuous operation was performed. At the end of spraying ', the air in the container is sucked and collected for 10 minutes by a suction flow of 10 L per minute with a dust measuring device. This is 0 minutes. When the ion generating element 1 is operated, the ion generating element and the fan are operated simultaneously. After the start of the operation, after a certain period of time, 100 L of air in the trap container was sucked in the same manner as 0 minutes. The ion concentration was 200,000 / cm3. In addition, when the ion generating element 1 is not operated (natural decay) 42 42 · (37) 1235671 The ion generating element is not operated, and only the fan 4 is operated, and the air in the trap container is attracted every time. . The space environment temperature is 25 t and the relative humidity is 60% PH. The ion generation system was confirmed to have a temperature of 0 ° C, a relative humidity of 10%, and a temperature of 40 ° C, and a relative humidity of 90%. In order to perform a comparison experiment with ozone, a UV-type ozone generator (OZ5 1N-1, SEN Special Light Source Co., Ltd.) was used to generate an ozone generation amount of 1.637 mg / h (22 °) equal to the ozone generation amount of the ion generating element. C, 17% RH). The sterilized physiological saline solution in the air trapped in the container attracted by the dust measuring device is a test solution, and the sterilized physiological saline solution is used for stage dilution, and the original solution and each diluted solution are smeared on tryptic casein soybean agar medium (BBL). Incubate at 35 ° C for 48 hours. After incubation, the number of colonies on the medium was counted, indicating the number of bacteria that attracted air. As shown in Fig. 19, it was confirmed that the concentration of phytoplankton was reduced to about 1/10 of that after 30 minutes, as compared with when the ion generating element was not operated. Further, after 120 minutes elapsed ', no phytoplankton was detected. As shown in Fig. 20, when the ion generating element was compared with the ultraviolet type ozone generating device, it was confirmed that the concentration of plankton was reduced by about half after 60 minutes. Accordingly, the bactericidal effect of Bacillus spp. Which formed heat-resistant spores was confirmed by the action described in Example 6. Anthrax and Bacillus are the same genus, and their effects can be expected. [Embodiment 9] -43-(38) 1235671 Fig. 21 is a cross-sectional view showing an air-conditioning apparatus disposed in an air path of an ion generating element blow-out port. Fig. 22 is a graph showing the frequency of cellular infection of plankton virus in the air after 60 minutes with respect to the ion ejection amount in a space of 27L volume. Fig. 23 is a graph showing changes over time in the frequency of virus cell infection in the air when 540,000 positive / negative ions are supplied in a space of 30 m3 in capacity per minute. In the test shown in Figure 22, in order to detect the effect of ion ejection on the frequency of cell infection of plankton influenza virus in the space, the 27L space used in this test is 30cmx30cmx 30cm of chlorinated olefin. A virus spray device and a recovery device are installed at both ends of the container. In this container, an ion generating element is installed in the air blowing port above the blower. In addition, in order to achieve the purpose of floating the sprayed virus for a long time, the axial direction of the axial flow fan is set upward. Influenza virus A (HI NI) A / PR8 / 34: ATCC VR-95 is inoculated into the allantoic membrane cavity of developing eggs, cultured in an incubator, and allantoic fluid is taken as the test virus fluid . Put the test virus solution of ΙΟηαΙ into a glass sprayer and connect it to one end of the test device. The other end is connected to a glass dust tester containing 100 m 1 of sterile physiological salt solution. The sprayer comes from a gas sampler The discharge pressure of the compressed air was adjusted to 0.48hPa with the gauge pressure, and the test bacteria were sprayed from the spray port. The spray volume was 3.0ml (spray flow rate 0.1ml / minx spray time 30min). While spraying the virus solution, the axial flow Fan 4 is operated until the end of the test, and continuous operation is performed. At the end of the spray, the air in the container is dust-measured by a dust detector at a rate of 44-39 (39) 1235671 for 10 minutes per minute to attract and capture for 30 minutes. This is 0 minutes. 1 hour after the start of the operation, 100L of air in the trap container is sucked in the same manner as 0 minutes. The suction bow of the dust tester | The PBS (-) of the air in the capture test device is the test solution, and it is popular Cold virus Measured by the control method of MDCK cells. The input voltage of the ion generating element was adjusted to adjust the ion ejection amount. When the positive and negative ion ejection amounts were 0 / cm3 · min and the cell infection frequency was 100%, it was confirmed that 270,000 / cm3 · The frequency of cell infections with an ion ejection amount of above minus rapidly decreased, and it was confirmed that the positive and negative ion ejection amounts were 270,000 / cm3 or more, respectively, which had the effect of reducing virus infection. Furthermore, in order to confirm the actual use in living environment space The effect is shown in the test shown in FIG. 23. The air conditioning device 60 shown in FIG. 21 is installed in a space volume of 30 m3, and the dust collecting filter 64b and the deodorizing filter 64a are removed, so that the ion generating element 65 Residual rate of plankton virus in the space during operation. Here, when the structure of the air-conditioning apparatus 60 shown in FIG. 21 is described, the air-conditioning apparatus 60 is formed with an air intake port 62 ′ device 61 in front of the indoor device 61. An air outlet 63 is formed above the air inlet 62. A deodorizing filter 64a and a dust collection filter 6 "are provided in the air inlet 62, and an ion generator is provided near the air outlet 63. The ion generating device 67 formed by the element 65 and the high-voltage power source 66. Second, the air fan 68 inside the device exhausts the air sucked in by the air suction port 62 through the air blowing port 63 to the outside. At this time, the ion generating device 67 When driven, it releases ionized air -45- (40) 1235671 The air conditioning device configured as above, is equipped with an ion generating element 65 on the blowing air path, and the air sucked in by the suction port 62 is discharged through the blowout port 63. The air contains ions and can release ions into the space. Therefore, ions can be added not only to the inhaled air but also to the entire space. The virus concentration measurement was performed in the same manner as in the test performed in FIG. 22. 5.4 million ions / cm3 of positive and negative ions were supplied in one minute. Understand that the frequency of cellular infections per hour is reduced to 1/10. In this way, regarding the volume of an air-conditioning apparatus actually used in a living environment, it is understood that the effect of virus inactivation in the air can be evaluated. The positive and negative ions sent out of the space surround the virus floating in the air. On the surface of the virus, the active source of hydrogen peroxide H202 or free radical · OH is generated by the chemical reaction of the positive and negative ions, which destroys the protein and kills it. According to this method, viruses in the air can be effectively sterilized. In addition, in the present embodiment, the ion system indicates both positive and negative ions. Regarding the ion concentration, each ion concentration is approximately equal, and the average radon is recorded. In addition, in all the above-mentioned embodiments, as the particle release method, the Lenar effect is used, and even if the liquid is ejected or vibrated, physical separation is used to generate the particles with electric charges. The effect of the present invention is obtained. In addition, as the particles, positive ions, negative ions, a mixed gas of positive and negative ions, charged particles such as α-rays and / 3-rays other than the above, or particles of various ionized gas particles, radicals, and pharmaceutical particles, etc. The same effects as the present invention are obtained. -46- (41) 1235671 The effect of the invention is as explained above. According to the present invention, a microorganism is allowed to float in a certain space. After the microorganism is irradiated with ions, the germicidal treatment of the microorganism / particles used, then the microorganism is taken. The measurement is carried out to achieve an evaluation test-to determine the effectiveness of the above-mentioned particles on the sterilization treatment ability of microorganisms. &lt; Brief description of the drawings &gt; Fig. 1 is a schematic configuration diagram showing a first embodiment of the apparatus for evaluating microorganism removal according to the present invention. Fig. 2 is a schematic configuration diagram showing a second embodiment of the apparatus for evaluating microorganism removal according to the present invention. &lt; Fig. 3 shows the measurement results of Example 1, and the measurement results of the microorganisms used in the sterilization treatment when the ion concentration was changed. Fig. 4 shows the measurement results of Example 2 regarding the results of measurement of microorganisms taken with and without ions being sent. 0 FIG. 5 is a photograph obtained by photographing the microorganisms taken in Example 2. FIG. Fig. 5 (a) is a photograph of the microorganisms taken when the ion is sent out, and Fig. 5 (b) is a photograph of the microorganisms taken when the ion is not taken out. Fig. 6 shows the measurement results of Example 3, the measurement results of the microorganisms taken in the stirred container and when not stirred. Fig. 7 shows the measurement results of Example 4 regarding the measurement results of the microorganisms taken when the ions were sent and when the ions were not sent. -47-(42)! 235671 Fig. 8 is a schematic diagram showing the third embodiment and the sixth embodiment of the apparatus for evaluating the removal of microorganisms. Fig. 9 is a schematic configuration diagram showing a fourth embodiment of the apparatus for evaluating the removal of planktonic microorganisms. FIG. 10 is a schematic configuration diagram showing a fifth embodiment of the apparatus for evaluating the removal of plankton virus. Fig. 11 is a graph showing the frequency of cellular infection of influenza virus according to the ion concentration of Example 6. FIG. 12 is a graph showing the frequency of cell infection of the Quexach virus according to the ion concentration of Example 6. FIG. Fig. 13 is a graph showing the frequency of cell infection of polio virus according to the ion concentration of Example 6. FIG. 14 is a mass spectrum chart showing positive ions and negative ions generated by the ion generating element of Example 6. FIG. FIG. 15 is a flowchart showing an evaluation test of Example 6. FIG. Fig. 16 is a schematic diagram of a device for evaluating the removal of planktonic pathogenic bacteria in Example 7. Fig. 17 is a graph showing the change over time of the concentration of Staphylococcus in the air at an ion concentration of 200,000 particles / cm3 in Example 7. Fig. 18 is a graph showing the change over time of the concentration of staphylococcus in the air in the ion generating element and the ultraviolet-type ozone generating device of Example 7; Fig. 19 is a graph showing the change over time of the concentration of Bacillus sp. (Baci) us in the air at an ion concentration of 200,000 / cm3 in Example 8. • 48-(43) 1235671 Fig. 20 is a graph showing the change over time of the concentration of planktonic bacillus in the air in the ion generating element and the ultraviolet-type ozone generating device of Example 8. Fig. 21 is a cross-sectional view showing an air-conditioning apparatus provided in an air path of an ion generating element blow-out port in Example 9. / FIG. 22 is a graph showing the frequency of cell infection of floating virus in the air according to the amount of ion ejection in Example 9. Fig. 23 is a graph showing changes over time in the frequency of infection of virus cells in the air according to the amount of ion ejection in Example 9. Φ Symbol description 1 Ion generator 2 Ion generator □ 3 Microbial collection tube 3a Microbial collection □ 4 Mixer 5 Microbial injection tube 5a Microbial injection □ 6 Microbial collector 7 ik 丄 8 Container 10 Evaluation device for microorganism removal 11 Microbial sprayer 12 Ion Generating element 12a Ion generating electrode 49 · (44) (44) 1235671 13 Microbial collection tube 13a Microbial collection port 15 Microbial injection tube 15a Microbial injection port 18 Container 20 Device for evaluating microorganism removal 3 1 Wind tunnel 35 Container

-50·-50 ·

Claims (1)

1235671 ⑴ 拾、申請專利範圍 1 · 一種評估微生物除去之方法,其特徵爲,供給微 生物於容器內部空間,同時照射殺菌處理該微生物用之正 及負離子所形成之粒子,於進行該粒子照射後,採取微生 物’進行所採取之微生物之測定。 2 · —種評估微生物除去之方法,其特徵爲,供給作 爲微生物之病毒於容器內部空間,照射殺菌處理該微生物 用之粒子’於進行該粒子照射後,採取微生物,進行所採 取之微生物之測定。 3 ·如申請專利範圍第1項或第2項之評估微生物除 去之方法,其中進行該粒子照射後,進行該微生物之測定 的同時,進而,以與照射該粒子,殺菌處理微生物時之相 同條件下,供給微生物,不照射該粒子,使微生物自然衰 退之後,採取微生物,進行所採取之微生物之測定。 4 ·如申請專利範圍第1項或第2項之評估微生物除 去之方法,其中該測定係該微生物之濃度測定或活性度之 測定。 5 ·如申請專利範圍第1項或第2項之評估微生物除 去之方法,其中關於測定所採取之微生物,係進而測定依 照射該粒子時間之經時變化。 6 ·如申請專利範圍第1項或第2項之評估微生物除 去之方法,其中關於測定所採取之微生物,係進而測定有 關該粒子之除去性能之濃度依賴性。 7.如申請專利範圍第1項或第2項之評估微生物除 -51 · (2) (2)1235671 去之方法,其中關於供給微生物於該容器之內部空間,係 使分散微生物之溶液成霧狀,進行噴霧。 8 .如申請專利範圍第1項或第2項之評估微生物除 去之方法’其中作爲該微生物之評估方法,係使用微生物 之細胞培養、微生物之紅血球凝集反應或微生物之過敏反 應。 9 ·如申請專利範圍第2項之評估微生物除去之方法 ’其中殺菌處理該微生物用之粒子係由任一種之空氣中放 電、空氣中放射線照射及勒納爾效應(Lenard effect )所 生成之粒子。 1 0 ·如申請專利範圍第2項之評估微生物除去之方法 ,其中殺菌處理該微生物用之粒子係任一種之放射線、X 光、7射線及電磁波。 1 1 ·如申請專利範圍第2項之評估微生物除去之方法 ’其中殺菌處理該微生物用粒子爲藥劑粒子。 1 2 ·如申請專利範圍第1項之評估微生物除去之方法 ’其中該微生物係1種或組合2種以上選自細菌、真菌、 病毒及過敏原物質所成群。 1 3 .如申請專利範圍第1項或第2項之評估微生物除 去之方法,其中關於該容器內部之空間,供給微生物時, 對於該容器內所供給之微生物,由下側進行攪拌容器之內 部空間。 14. 一種評估微生物除去之裝置,其特徵爲,具備有 可供給微生物之內部空間及進行該微生物之殺菌處理用之 ►52- (3) 1235671 容器,及供給微生物於該容 ,及於該容器內部空間,同 及負之離子所形成之粒子之 生物除去手段進行微生物之 生物採取手段,測定以該微 而評估用。 1 5 . —種評估微生物除 可供給作爲微生物之病毒之 菌處理用之容器,及供給微 物供給手段,及於該容器內 用粒子之微生物除去手段, 微生物之殺菌處理後,採取 定以該微生物採取手段所採 1 6 .如申請專利範圍第 除去之裝置,其中該微生物 及該微生物採取手段係於含 側向著下流側,依次排列。 1 7 ·如申請專利範圍第 除去之裝置,其中該微生物 之間,介有形成含有微生物 內側配置著該微生物除去手 18·如申請專利範圍第 除去之裝置5其中該微生物 係配置於該微生物供給手段 器內部空間之微生物供給手段 時供給殺菌處理微生物用之正 微生物除去手段,以及以該微 殺菌處理後,採取微生物之微 生物採取手段所採取之微生物 去之裝置,其特徵爲,具備有 內部空間及進行該微生物之殺 生物於該容器內部空間之微生 部空間,供給殺菌處理微生物 以及以該微生物除去手段進行 微生物之微生物採取手段,測 取之微生物而評估用。 1 4項或第1 5項之評估微生物 供給手段、該微生物除去手段 有微生物之空氣通路,由上流 14項或第15項之評估微生物 供給手段及該微生物採取手段 之空氣通路之風洞,該風洞之 段。 1 4項或第1 5項之評估微生物 除去手段及該微生物採取手段 之垂直下方以外之區域。 •53- (4) 1235671 1 9 .如申請專利範圍第1 4項惑 除去之裝置,其中於該容器之外側 之其他容器。 2 〇 ·如申請專利範圍第1 4項惑 除去之裝置5其中於該容器之內部 空間用之攪拌手段。 21 ·如申請專利範圍第1 4項或 除去之裝置,其中以該微生物供給 分散微生物之溶液成霧狀,噴霧於 成。 22. 如申請專利範圍第14項或 除去之裝置,其中殺菌處理該微生 之空氣中放電、空氣中放射線照射 effect)所生成之氣體所放出而構成 23. 如申請專利範圍第15項 置,其中殺菌處理該微生物用粒子 光、r射線及電磁波所放出而構成 24. 如申請專利範圍第15項 置,其中該微生物除去手段係照射 用粒子之藥劑粒子所構成。 5第15項之評估微生物 ,配置著可遮覆該容器 5第15項之評估微生物 空間,設有攪拌該內部 〖第15項之評估微生物 手段之微生物供給係使 該容器之內部空間所構 :第15項之評估微生物 物用之粒子係由任一種 及勒納爾效應(Lenard 〇 之評估微生物除去之裝 係任一種之放射線、X 〇 之評估微生物除去之裝 作爲殺囷處理該微生物 -54-1235671 ⑴ Pick up, apply for patent scope 1 · A method for evaluating the removal of microorganisms, which is characterized by supplying microorganisms to the internal space of the container and simultaneously irradiating particles formed by positive and negative ions used for sterilizing the microorganisms. After the particles are irradiated, Take microorganisms' for the determination of the taken microorganisms. 2-A method for evaluating the removal of microorganisms, characterized in that a virus as a microorganism is supplied to the inner space of the container, and particles used for sterilizing the microorganism are irradiated. After the particles are irradiated, the microorganisms are taken and the measured microorganisms are measured. . 3. The method of evaluating microorganism removal as described in item 1 or 2 of the scope of patent application, wherein after the particle is irradiated, the measurement of the microorganism is performed, and further, the same conditions as when irradiating the particle to sterilize the microorganism Next, the microorganisms are supplied, and the particles are not irradiated. After the microorganisms naturally decay, the microorganisms are collected and the measured microorganisms are measured. 4 · If the method for assessing the removal of microorganisms is set out in item 1 or 2 of the scope of the patent application, wherein the determination is a determination of the concentration of the microorganism or a determination of the activity. 5 · If the method for evaluating microorganism removal in the first or second scope of the patent application is applied, the measurement of the microorganisms used is to further measure the change over time according to the time of irradiation of the particle. 6 · If the method for assessing the removal of microorganisms is set out in item 1 or 2 of the scope of the patent application, wherein the determination of the microorganisms used is to further determine the concentration dependence of the removal performance of the particles. 7. The method for removing microorganisms in accordance with item 1 or item 2 of the scope of the patent application -51 · (2) (2) 1235671, wherein the supply of microorganisms to the internal space of the container is to make the solution of dispersed microorganisms fog And spray. 8. The method for removing microorganisms as described in item 1 or 2 of the scope of the patent application, wherein the method for evaluating the microorganisms is the use of cell culture of microorganisms, erythrocyte agglutination reaction of microorganisms, or allergic reaction of microorganisms. 9 · The method for evaluating the removal of microorganisms according to item 2 of the scope of the patent application, wherein the particles used to sterilize the microorganisms are particles generated by any of air discharge, radiation in the air, and Lenard effect. . 10 · The method for evaluating the removal of microorganisms according to item 2 of the scope of the patent application, wherein the particles used for sterilizing the microorganisms are any of radiation, X-rays, 7 rays and electromagnetic waves. 1 1 · The method for evaluating the removal of microorganisms according to item 2 of the scope of the patent application ′ wherein the particles for sterilizing the microorganisms are pharmaceutical particles. 1 2 · The method for evaluating the removal of microorganisms according to item 1 of the scope of the patent application, wherein the microorganism is one or a combination of two or more selected from the group consisting of bacteria, fungi, viruses, and allergens. 1 3. If the method for evaluating microorganism removal is described in item 1 or 2 of the scope of the patent application, regarding the space inside the container, when supplying microorganisms, for the microorganisms supplied in the container, the inside of the container is stirred from the lower side. space. 14. An apparatus for evaluating the removal of microorganisms, comprising an internal space capable of supplying microorganisms and a sterilizing treatment for the microorganisms ►52- (3) 1235671 container, and supplying microorganisms to the container, and the container In the internal space, the biological removal means of the particles formed by the negative ions is used for the biological taking measures of the microorganisms, and the measurement is used for the evaluation. 15. A kind of container for evaluating the microorganisms that can be used to supply the bacteria as viruses, and a means for supplying micro-organisms, and a method for removing microorganisms using particles in the container. After the microorganisms are sterilized, take the The microorganisms are taken by means of 16. The device for removing the scope of the patent application, wherein the microorganisms and the means of taking the microorganisms are arranged side by side to the downstream side. 1 7 · The device for removing the scope of the patent application, wherein the microorganisms are interposed between the microorganisms, and the microorganism removing hand is arranged on the inside. 18 · The device for removing the scope of the patent application 5, wherein the microorganisms are arranged in the microorganism supply. The microorganism supply means for the internal space of the device is provided with a means for removing positive microorganisms for sterilizing microorganisms, and a device for removing microorganisms by means of the microorganisms after the micro-sterilization treatment. The device is characterized by having an internal space. And the micro-organism kills the microorganism in the space of the micro-biological part of the container internal space, and supplies the germicidal treatment microorganism and the microorganism-removing microorganism-removing microorganism-receiving method to measure the microorganisms for evaluation. The assessment means for supplying microorganisms in item 14 or item 15 and the means for removing microorganisms have air passages for microorganisms. The wind tunnel in the air passages for assessing supply means for microorganisms in item 14 or 15 above and the means for taking the microorganisms, the wind tunnel. Paragraph. The evaluation microorganisms of item 14 or item 15 and the area other than the vertical direction below the microorganisms' removal method. • 53- (4) 1235671 1 9. The device to be removed as described in item 14 of the scope of patent application, in which other containers are located outside the container. 2 〇 As described in item 14 of the scope of patent application, the device 5 is a stirring means used in the internal space of the container. 21 · The device as claimed in item 14 of the patent application scope or removed, wherein the microorganism-dispersed solution of the microorganisms is supplied in a mist form and sprayed on. 22. If the patent application scope item 14 or removed device, which sterilizes the micro-born air discharge, radiation in the air, the gas generated by the effect) is released and constitutes 23. If the patent application scope item 15 is set, Among them, the microorganisms are sterilized by light, r-rays, and electromagnetic waves. 24. For example, the scope of application for patent No. 15 is set, wherein the microorganisms removal means is composed of pharmaceutical particles of irradiation particles. 5 The evaluation microorganism of item 15 is provided with an evaluation microorganism space which can cover the container according to item 15 of the container, and the microorganism supply means for stirring the inside of the evaluation microorganism of item 15 is to make the internal space of the container constitute: The particle used for the evaluation of microorganisms in item 15 is composed of either one and the Lenar effect (the evaluation of removal of microorganisms by Lenard 〇, the radiation of any one, the evaluation of removal of microorganisms by X 〇 is used to kill the microorganism-54. -
TW92107911A 2002-04-05 2003-04-07 Method of estimating elimination of microorganisms and apparatus for estimating elimination of microorganisms TWI235671B (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
JP2002104306 2002-04-05
JP2002326078A JP2004159508A (en) 2002-11-08 2002-11-08 Method and apparatus for evaluating removal of microorganism

Publications (2)

Publication Number Publication Date
TW200403081A TW200403081A (en) 2004-03-01
TWI235671B true TWI235671B (en) 2005-07-11

Family

ID=36648830

Family Applications (1)

Application Number Title Priority Date Filing Date
TW92107911A TWI235671B (en) 2002-04-05 2003-04-07 Method of estimating elimination of microorganisms and apparatus for estimating elimination of microorganisms

Country Status (1)

Country Link
TW (1) TWI235671B (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN111902526A (en) * 2018-03-26 2020-11-06 夏普株式会社 Clean space maintaining device, building structure, cell culture method, and cell production method

Also Published As

Publication number Publication date
TW200403081A (en) 2004-03-01

Similar Documents

Publication Publication Date Title
KR100738174B1 (en) Method of Estimating Elimination of Microorganisms and Apparatus for Estimating Elimination of Microorganisms
EP2051741B1 (en) Method for air disinfection and sterilization
US9365884B2 (en) Environmental evaluation installation and environmental evaluation method
Xia et al. Inactivation of airborne porcine reproductive and respiratory syndrome virus (PRRSv) by a packed bed dielectric barrier discharge non-thermal plasma
JP4142974B2 (en) Microorganism removal evaluation method and microorganism removal evaluation apparatus
CN112028169A (en) Medical wastewater electron beam irradiation treatment device and treatment method
JP2008022765A (en) Device for evaluating environment and method for evaluating environment
CN101296741A (en) Internal suction type air filtering disinfection method and system
Ignatov et al. Studying the antimicrobial and antiviral effects of electrochemically activated NaCl solutions of anolyte and catholyte on a strain of e. coli dh5 and classical swine fever (csf) virus
JP2004159508A (en) Method and apparatus for evaluating removal of microorganism
JP2004159636A (en) Method and apparatus for evaluating removal of microorganism
TWI235671B (en) Method of estimating elimination of microorganisms and apparatus for estimating elimination of microorganisms
KR101694895B1 (en) Method for simultaneous sampling and quantification of bacteria and host-based virus
JP2008022764A (en) Environment evaluation method
Guo et al. Inactivation of airborne pathogenic microorganisms by plasma-activated nebulized mist
Obrová et al. Decontamination of high-efficiency mask filters from respiratory pathogens including SARS-CoV-2 by non-thermal plasma
JPH07303688A (en) Sterilization of microorganism, etc., in transferring gas and sterilizing device
JP2003325198A (en) Method and apparatus for evaluating removal of microorganism
CN1472331A (en) Method for testing virus removing effect with air purifier
JP5656517B2 (en) Suspension virus inactivation evaluation method and apparatus
Nur et al. A successful elimination of Indonesian SARS-CoV-2 variants and airborne transmission prevention by cold plasma in fighting COVID-19 pandemic: A preliminary study
JPH07170888A (en) Aseptic culture and apparatus therefor
Benn et al. Disinfection of mechanical ventilators: an investigation using formaldehyde in a Cape ventilator
JP2011139682A (en) Device and method for measuring inactivation effect of floating-infective influenza virus
JP2004065307A (en) Sterilization and deodorization device for gas

Legal Events

Date Code Title Description
MM4A Annulment or lapse of patent due to non-payment of fees