JPH0373154A - Collecting method for ethylene oxide gas - Google Patents

Collecting method for ethylene oxide gas

Info

Publication number
JPH0373154A
JPH0373154A JP2115108A JP11510890A JPH0373154A JP H0373154 A JPH0373154 A JP H0373154A JP 2115108 A JP2115108 A JP 2115108A JP 11510890 A JP11510890 A JP 11510890A JP H0373154 A JPH0373154 A JP H0373154A
Authority
JP
Japan
Prior art keywords
eog
valve
sterilization chamber
compressor
pressure
Prior art date
Legal status (The legal status 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 status listed.)
Pending
Application number
JP2115108A
Other languages
Japanese (ja)
Inventor
Yoichi Shimoi
洋一 下井
Hiroshige Makino
牧野 広成
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Nippon Steel Eco Tech Corp
Original Assignee
Nittetsu Kakoki 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
Application filed by Nittetsu Kakoki KK filed Critical Nittetsu Kakoki KK
Publication of JPH0373154A publication Critical patent/JPH0373154A/en
Pending legal-status Critical Current

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  • Apparatus For Disinfection Or Sterilisation (AREA)
  • Gas Separation By Absorption (AREA)

Abstract

PURPOSE:To collect EOG used for sterilization as much as possible in a clean state and to reutilize it by accumulating and collecting treated EOG to an accumulating tank by a compressor and offering it for reuse, and also, exhausting rarefied EOG generated at the time of taking in and out to the outside of a system. CONSTITUTION:After the treatment is ended, EOG, etc., pass through valves A, H by the own pressure at first and fed to a cushion tank 2, and subsequently, pass through a valve C and accumulated in an accumulating tank 3 brought to pressure rise by driving of a compressor B-2. Next, at the time point when pressure of a sterilizing chamber 1 becomes 1.2atm, the valve H is closed and the valve B is opened, a vacuum pump B-1 operates, and the EOG passes though the valves A, B, the cushion tank 2, the valve C, and the compressor B-2 and accumulated in the accumulating tank 3. at the time when pressure of the sterilizing chamber 1 becomes 50Torr, the valves A, B and C, the vacuum pump B-1 and the compressor B-2 are stopped, the valve E is opened air flows into the sterilizing chamber 1, and the becomes 1atm. Thereafter, the valve E is closed, the vacuum pump B-1 operates, the valve A, G are opened, diluted EOG, etc., are led to the outside of a closed circuit, and at the time of the next sterilization treatment, the accumulated BOG is allowed to flow in.

Description

【発明の詳細な説明】 〔産業上の利用分野〕 本発明はEOGの回収方法に関し、特に医療機材、化粧
品、脱脂綿、包装材料など衛生管理の分野にシける滅菌
装置から排出されるEOGの回収方法に関する。
[Detailed Description of the Invention] [Industrial Application Field] The present invention relates to a method for collecting EOG, and in particular, the collection of EOG discharged from sterilizers used in the field of hygiene management such as medical equipment, cosmetics, absorbent cotton, and packaging materials. Regarding the method.

〔従来の技術〕[Conventional technology]

EOGはエチレングリコールの中間原料等として広く利
用されているが、酸化性を有し、この滅菌作用のため燻
蒸消毒あるいは殺菌剤として医療器材、包装材料、書籍
1文化財等の滅菌分野に利用されている。
EOG is widely used as an intermediate raw material for ethylene glycol, etc., but it has oxidizing properties, and because of this sterilization effect, it is used as a fumigation disinfectant or a disinfectant in the field of sterilizing medical equipment, packaging materials, books, cultural properties, etc. ing.

とのEOGは精神障害、発癌性など人体に対して毒性を
有し、またEOGと空気との混合物は広い爆発範囲(3
〜100 qb )をもち、かつ可燃性の危険物質であ
る。このためEOGは高圧ガス取締法及び労働安全衛生
法による規制を受けるが、大気汚染防止上は特に規制は
なく、在れ咳で未処理のit大気に放出される例が多か
った。
EOG is toxic to the human body, including mental disorders and carcinogenicity, and a mixture of EOG and air has a wide explosive range (3
~100 qb) and is a flammable hazardous substance. For this reason, EOG is subject to regulations under the High Pressure Gas Control Law and the Industrial Safety and Health Law, but there are no particular regulations regarding air pollution prevention, and there are many cases where EOG is released into the untreated atmosphere.

しかし近年公害問題に対する関心の高まりと共に焼却方
式、湿式方式による処理が多く行われるようになってき
た。
However, in recent years, with increasing interest in pollution problems, incineration and wet treatment methods have become more common.

湿式吸収法としては単なる水吸収が最も手軽な方法であ
るが、水に対する溶解度は塩素ガス基であり(溶解度の
指標であるヘンリ一定数mは25℃で13である)、水
吸収は確実な方法とは言えない。
Simple water absorption is the simplest wet absorption method, but the solubility in water is chlorine gas (Henry's constant m, which is an index of solubility, is 13 at 25°C), and water absorption is reliable. I can't say it's a method.

EOGは硫酸を触媒に用いると容易に加水分解して下記
の反応式のようにエチレングリコールを生成する。
When sulfuric acid is used as a catalyst, EOG is easily hydrolyzed to produce ethylene glycol as shown in the reaction formula below.

II、80゜ CJ4aO+ )I*OC*H4(OH)を仁の反応は
本来エチレングリコールの製造に応用されているが、E
OGの除去にも優れた効果を発揮する。すなわち水に物
理溶解したEOGは逐次エチレングリコールに加水分解
するため、水のみの吸収に比較して極めて大きな吸収速
度を示す。
II, 80°CJ4aO+) I*OC*H4(OH) reaction was originally applied to the production of ethylene glycol, but E
It also exhibits excellent effects in removing OG. That is, since EOG physically dissolved in water is sequentially hydrolyzed into ethylene glycol, it exhibits an extremely high absorption rate compared to absorption of water alone.

この反応を用−た吸収方式は、特開昭59−22215
7に発表されている。また本発明者らは特願陥63−1
7’7199としてEOGの改良吸収方法を田願した。
The absorption method using this reaction was published in Japanese Patent Application Laid-Open No. 59-22215.
It was announced on 7th. In addition, the present inventors have patent application defect 63-1
7'7199, an improved EOG absorption method was proposed.

しかしこの吸収方式は貴重なEOGを最終的に廃棄する
ことになり、また硫酸及びその中和に特性ソーダを必要
とし、加水分解の結果供したエチレングリコールを周期
的に抜きεす、廃棄しなくではならず、と、れは高BO
Dの排水として排水処理に出費が伴なう。
However, this absorption method ultimately disposes of valuable EOG, requires sulfuric acid and special soda for its neutralization, and eliminates the need to periodically extract and dispose of the ethylene glycol provided as a result of hydrolysis. It's not, it's a high BO
As wastewater from D is discharged, there is an expense involved in wastewater treatment.

一方焼却方式は湿式方式に比較(−で100 %分解と
除去率の大きな利点を有するが、燃料費や設備費がかか
り、さらに何よりも責重なE OGを消失させるという
資源の損失とい、う点で大きい不利益がある。
On the other hand, the incineration method has the great advantage of 100% decomposition and removal rate compared to the wet method (-), but it requires high fuel and equipment costs, and above all, it causes a loss of resources due to the disappearance of the responsible EOG. There is a big disadvantage in this respect.

こ、のよりに従来除害処理する己とはあっでも回収きれ
る己とはなかった。
In this case, there was no way that I would be able to recover the waste even if I used to carry out detoxification treatment.

〔発明が解決しようとする課題〕[Problem to be solved by the invention]

本発明は上記の事情に鑑み、これらを改良し5たもので
、滅菌に使用したEOGを清浄な状態で極力回収し再利
用する方法の提供を目的とする。
In view of the above-mentioned circumstances, the present invention is an improvement on these methods and aims to provide a method for recovering and reusing EOG used for sterilization in as clean a state as possible.

〔課題を解決するための手段〕[Means to solve the problem]

己の目的を達成するための本発明は次の3の請求項から
なる。即ち、己の第1の発明は滅菌室、真空ポンプ、ク
ツシランタンク、圧縮機及び蓄圧タンクを順次配管によ
り接続して蓄圧タンクより滅菌室に戻る閉回路を形成し
、処理済のE O(3を圧縮機により蓄圧タンクに蓄圧
回収して再使用に供すると共に、滅菌室における被処理
物の出し入れ時に発生する稀薄EOGを系外に排出し、
且つ、この損失に見合う不足分を補給するものである。
The present invention to achieve its object consists of the following three claims. That is, my first invention connects a sterilization room, a vacuum pump, a kutsushiran tank, a compressor, and a pressure storage tank in sequence with piping to form a closed circuit that returns from the pressure storage tank to the sterilization room, and then processes the processed E.O. 3 is stored and recovered in a pressure storage tank using a compressor for reuse, and at the same time, diluted EOG that is generated when the objects to be processed are taken out and taken out of the sterilization room is discharged from the system.
Moreover, it is intended to replenish the shortage commensurate with this loss.

また、請求項(2)に記載した譲2の発明は、上記EO
G回収の閉回路において、滅菌室に水蒸気吹込手段を設
ける表共に、クッシーンタンクと圧縮機εの間に除湿器
を設け、滅菌工程中で発生するバクテリヤの死骸、菌類
の胞子及びダスト等を凝縮水と共に系外に排出すること
からなる。また、請求項(3)に記載した築3の発明は
滅菌室における被処理物の出し入れ時に発生する回収可
能な限度以下の稀薄gOG−4真空ポンプにより吸収装
置に導いて除害した後、大気に排出することからなって
いる。
Furthermore, the invention of Assignment No. 2 stated in claim (2) is based on the above-mentioned EO
In the closed circuit for G recovery, a steam blowing means is installed in the sterilization room, and a dehumidifier is installed between the Cushion tank and the compressor ε to remove dead bacteria, fungal spores, dust, etc. generated during the sterilization process. This consists of discharging it out of the system together with condensed water. In addition, the third aspect of the invention described in claim (3) is that the dilute gOG-4 generated when taking in and out of the processed material in the sterilization room is guided to the absorption device by the vacuum pump to remove the gas, which is less than the recoverable limit, and then the air is removed. It consists of discharging the water.

以下に本発明を図により具体的に説明する。The present invention will be specifically explained below with reference to the drawings.

第1図は第1及び第3発明を組み合わせた実施例の図で
あυ、第2図は第2発明の実施例を示す図である。第1
図に示すように、第1発明は滅菌室l、真空ポンプB−
1%クッシワンタンク2.圧縮嵩・ロー2、蓄圧タンク
3の各機を配管15〜18で接続し、さらに蓄圧タンク
3よシ配管19〜20を経て滅菌室1に戻る閉園路を形
成する。また該閉回路に配管22.24を介してそれぞ
れB OG供給源(ボンベ)7及び後記の排出口に接続
し、さらに配管14を介して滅菌室1のパージ用空気供
給に接続しでいる。乙のパージ用空気は、熱或は紫外線
等で予め殺菌された空気である仁とが望ましい。
FIG. 1 is a diagram showing an embodiment combining the first and third inventions, and FIG. 2 is a diagram showing an embodiment of the second invention. 1st
As shown in the figure, the first invention includes a sterilization chamber l, a vacuum pump B-
1% Cushion Tank 2. The compressor/row 2 and the pressure accumulator tank 3 are connected by pipes 15 to 18, and a closed path returning to the sterilization room 1 via the pressure accumulator tank 3 and pipes 19 to 20 is formed. Further, the closed circuit is connected to a BOG supply source (cylinder) 7 and a discharge port described later through pipes 22 and 24, respectively, and further connected to a purge air supply for the sterilization chamber 1 via a pipe 14. It is preferable that the purge air is air that has been previously sterilized by heat or ultraviolet light.

滅菌室lで使用する滅菌処理用のEOGは爆発防止のた
め、予めE OG 10〜30 vol qb、 C0
190〜70vo1%の組成としく以下この混合ガスを
単にEOG等と称する)、運転当初は2ataの圧力を
有している。処理終了後EOG等は初め自圧によυ弁A
及びHを通シクッシッンタンクに送られ、引続き弁Cを
通り圧縮機B−2の駆動により昇圧され蓄圧タンク3に
蓄積される。
The EOG for sterilization used in the sterilization room 1 is prepared in advance with 10 to 30 vol qb of EOG, C0 to prevent explosion.
The mixed gas has a composition of 190 to 70 vol% (hereinafter simply referred to as EOG, etc.), and has a pressure of 2 ata at the beginning of operation. After processing is completed, EOG, etc. is initially operated by υ valve A due to its own pressure.
and H are sent to the compression tank, and then passed through valve C to be pressurized by driving the compressor B-2 and stored in the pressure storage tank 3.

次いで滅菌室lの圧力が1,2 ataになった時点で
、弁Hを閉じて弁Bを開き、真空ポンプB−1が作動し
、弁A、B、クッシ目ンタンク2、弁C1圧縮機B−2
を通り蓄圧タンク3に蓄積される。蓄圧タンクは温水等
により適宜加温されて蓄圧タンク内でE、OGの凝縮を
防ぎ、EOG等のガス組成の変化がなく、爆発の危険を
回避して安全に操業される。弁の切替は圧力指示調節計
(図示せず)と連動して自動的に行うこともできる。ま
たEOG等は蓄圧タンク3の前および/または後に設置
されたフィルター12によりゴミ、銹等がr過される。
Next, when the pressure in the sterilization chamber 1 reaches 1.2 ata, valve H is closed and valve B is opened, vacuum pump B-1 is activated, and valves A, B, gas tank 2, and valve C1 are compressed. B-2
is accumulated in the pressure accumulation tank 3. The pressure accumulator tank is appropriately heated with hot water or the like to prevent condensation of E and OG within the pressure accumulator tank, and there is no change in the composition of gases such as EOG, thereby avoiding the risk of explosion and operating safely. Valve switching can also be performed automatically in conjunction with a pressure indicating controller (not shown). Further, in EOG and the like, dust, rust, etc. are filtered through a filter 12 installed before and/or after the pressure accumulating tank 3.

このフィルターは一例として0.1μ以上の異物を99
1以上捕集するクリーンルーム用のフィルターを用いる
とよい。
For example, this filter can filter out 99% of foreign matter larger than 0.1μ.
It is recommended to use a clean room filter that collects one or more particles.

滅菌室1の圧力が5 Q Torrになりた時点で・弁
A、B、Cを閉じ(他の弁D−Hは全べて前工程におい
て閉じられている)、真空ポンプB−1、圧縮機B−2
は停止し、弁Eが開いて空気が滅菌室1に流入し、1 
ataになる。この時EOG等は大量の空気で希釈され
た状態になり、ここで弁Eを閉じ、真空ポンプB−1が
作動し、弁A及びqが開き、希釈されたEOG等は配管
24を通って閉回路外に導かれ、装置の規模、環境等を
考慮して、別途に除害処理が行なわれる。
When the pressure in sterilization chamber 1 reaches 5 Q Torr, close valves A, B, and C (all other valves D-H were closed in the previous process), and turn on vacuum pump B-1 and compressor. Machine B-2
stops, valve E opens and air flows into sterilization chamber 1.
Become ata. At this time, EOG, etc. are diluted with a large amount of air, and valve E is closed, vacuum pump B-1 is activated, valves A and q are opened, and the diluted EOG, etc. is passed through piping 24. It is led out of the closed circuit and is subjected to separate detoxification treatment, taking into account the scale of the equipment, environment, etc.

第1図には、第3の発明としてこの様な稀薄EOGの吸
収装置の一例が示されている。このEOG吸収装置では
特願昭63−177199に示すようにEOG等はスク
ラバー4で硫酸溶液によジエチレングリコールとして吸
収され、排ガスは排出口30より大気中に排出される。
FIG. 1 shows an example of such a dilute EOG absorption device as the third invention. In this EOG absorption device, as shown in Japanese Patent Application No. 63-177199, EOG and the like are absorbed as diethylene glycol by a sulfuric acid solution in a scrubber 4, and exhaust gas is discharged into the atmosphere from an outlet 30.

この吸収工程は滅菌室の圧力が50 Torrになった
時点で終了して真空ポンプB−1を停止する。次いで弁
A、Cxを閉じ、弁Eを開いて滅菌室lに空気を導入し
て滅菌室を常圧に戻した後、滅菌済みの物品が取出され
る。
This absorption process ends when the pressure in the sterilization chamber reaches 50 Torr, and the vacuum pump B-1 is stopped. Then, valves A and Cx are closed and valve E is opened to introduce air into the sterilization chamber 1 to return the sterilization chamber to normal pressure, after which the sterilized articles are taken out.

次回の滅菌処理をする場合には、滅菌室内を減圧し、必
要に応じてCO,置換を行った後、弁りのみを開き蓄圧
タンク3に蓄積され九EOG等を滅菌室1に流入させる
。次いで物品取出し時に排出され、減量したEOGはボ
ンベ7よう補給される。
When performing the next sterilization process, the pressure in the sterilization chamber is reduced, CO is replaced as necessary, and then only the valve is opened to allow the EOG, etc. stored in the pressure accumulation tank 3 to flow into the sterilization chamber 1. Next, the EOG that is discharged and reduced in volume when the article is taken out is replenished into the cylinder 7.

なお滅菌室における温度条件として凝縮をさけるために
、EOGが30℃で2.12ata以上の圧で凝縮する
ので15〜50℃の範囲で操作する必要がある。
In addition, in order to avoid condensation as a temperature condition in the sterilization room, it is necessary to operate within the range of 15 to 50°C since EOG condenses at a pressure of 2.12 ata or more at 30°C.

次に第2図に基づいて第2の発明について説明する。第
2図による工程は前記した第1図の工程に、次の2つの
工程を加えたものである。
Next, the second invention will be explained based on FIG. The process shown in FIG. 2 is obtained by adding the following two steps to the process shown in FIG. 1 described above.

即ち、l)滅菌室にスチームを導入して滅菌室の容積−
当り約49 ccの水を添加することにより、殺菌効果
を高める。2)圧縮真・のサクション側に凝縮式の除湿
器34を設けて、ダストやバクテリヤの死骸、カビの胞
子のまわうに水分を凝縮させてこれらを除去し、リサイ
クルするEOGの清浄化を図るものである。ここで用い
られる除湿器はチラー水による凝縮式のものであれば公
知のものが使用できる。この除湿器具は内部にフィン付
管を設け、チラー35からチラー水が除湿器34内を循
環して凝縮水をトラップ36から排出する。この際、水
分がバクテリヤの死骸、カビの胞子等の表面に凝縮して
、これらの不純物が効率よく除去され、EOGの循環使
用にかける清浄化のイメージを上げることができる。尚
、この除湿器34の設置に伴ない、蓄圧タンク3からク
ッシ言ンタンク2にガスを導管40を介して戻すと共に
、蓄圧タンク3の温度調整を行う。
That is, l) introducing steam into the sterilization chamber to reduce the volume of the sterilization chamber -
The sterilizing effect is enhanced by adding approximately 49 cc of water per bottle. 2) A condensing type dehumidifier 34 is installed on the suction side of the compression stem to condense moisture around dust, dead bacteria, and mold spores and remove them, thereby purifying the EOG to be recycled. It is. Any known dehumidifier can be used as long as it is a condensing type dehumidifier using chiller water. This dehumidification device is provided with a finned tube inside, and chiller water from the chiller 35 circulates within the dehumidifier 34 and condensed water is discharged from the trap 36. At this time, water condenses on the surfaces of dead bacteria, mold spores, etc., and these impurities are efficiently removed, which improves the image of cleaning that can be achieved by recycling EOG. Incidentally, with the installation of the dehumidifier 34, gas is returned from the pressure storage tank 3 to the gas tank 2 via the conduit 40, and the temperature of the pressure storage tank 3 is adjusted.

〔実施例〕〔Example〕

次の条件で実験した。 The experiment was conducted under the following conditions.

滅菌室容量   5Wt 使用EOG等組成  80G20俤、Co、8O俤滅菌
室圧力   2 ata 〜50 Tory真空ポンプ
排出ffk   2,0?F/Aクノシヨンタンク容電
  0.Sr& 圧   縮   機   2.2成偽 蓄圧タンク圧力  8 ata 蓄圧タンク容置  1..5tt/ 弁A−Hを閉じ、滅菌工程を終了した時点で、弁A11
1及びCを開りてクッシ3ンタンク2がl ataにな
るようPSA(圧力調整器)にて制御して圧縮機を作動
させ5分で滅菌室の圧力が2at、aから1..2at
aになった。
Sterilization chamber capacity 5Wt EOG composition used 80G20t, Co, 8Ot Sterilization room pressure 2 ata ~50 Tory vacuum pump discharge ffk 2,0? F/A injection tank capacitance 0. Sr & Compressor 2.2 Synthetic pressure accumulator tank pressure 8 ata Pressure accumulator tank storage 1. .. 5tt/ When valves A-H are closed and the sterilization process is completed, valve A11 is closed.
1 and C are opened and the pressure in the sterilization chamber is controlled by the PSA (pressure regulator) so that the pressure in the sterilization chamber reaches 2 at, and from a to 1. .. 2at
It became a.

次いで真空ポンプB−1が作動し、弁■を開き、弁11
を閉じて7分で滅菌室が1.2 alaから5QTor
rになり、仁のときの蓄圧タンク3のLE力は7,5 
ataに昇圧した。
Next, the vacuum pump B-1 operates, opens the valve ■, and opens the valve 11.
The sterilization chamber went from 1.2 ala to 5Q Tor in 7 minutes after closing.
r, and the LE power of the pressure accumulator tank 3 when it is 7.5
The pressure was increased to ata.

次に弁A、 B、 Cを閉じ、弁Bが開いて空気が滅菌
室に流入し、1分で5 Q Torvから1.ataに
なった。このたき滅菌室のEOG濃度は13000p・
plTl、であった。
Valves A, B, and C are then closed, and valve B is opened to allow air to flow into the sterilization chamber, from 5 Q Torv to 1. It became ata. The EOG concentration in the Konotaki sterilization room is 13,000 p.
It was plTl.

七の抜弁Eが閉にて弁A及びGが開き、真空ポンプが作
動し、6分で滅菌室は1 ataから50Torrにな
った。
The seventh vent valve E was closed, valves A and G were opened, the vacuum pump was activated, and the sterilization chamber was heated from 1 ata to 50 Torr in 6 minutes.

再び弁A、(3を閉じ非Bを開き空気を滅菌室に流入き
せ、滅菌室の圧力iJ: 50 Torrから1 al
aになった。この時の所要時間は1分でEOG濃度はs
oo ppmであった。次に再び弁Eを閉じて弁A及び
Gを開き、真空ポンプが作動1,2.6分で1.ata
から5 Q Torrになった。次いで、止jfij:
ε囲様にしで空気を導入するとEOGの濃度は50pp
mになった。己の3(ロ)の空気の混じ、:)たJくO
G等はE OG吸収装置のスクラバー5れエチレングリ
コールとして吸収された。
Close valves A and (3) and open valve B again to allow air to flow into the sterilization chamber, and the pressure in the sterilization chamber iJ: from 50 Torr to 1 al
It became a. The time required for this is 1 minute and the EOG concentration is s
It was oo ppm. Next, valve E is closed again and valves A and G are opened, and the vacuum pump is activated for 1.2.6 minutes. ata
It became 5 Q Torr. Then stop:
When air is introduced in an ε-like manner, the concentration of EOG is 50pp.
It became m. A mixture of my own 3 (b) air, :) TaJkuO
G and the like were absorbed as ethylene glycol by the scrubber 5 of the EOG absorption device.

ニニでE OG等で滅菌された被処理物をとりIE し
た後、弁Eを閉じ、弁A、Gを開いて真空ポンプB−1
により滅菌室を5QTorriで排気した。次いで弁A
、(3を閉じ、真空ポンプを停止した後、弁りを開は蓄
圧タンク3からE OG等を滅菌室に流入させ次回の滅
菌処理に備えた。
After taking the workpiece that has been sterilized with EOG, etc., and performing IE, close valve E, open valves A and G, and turn on vacuum pump B-1.
The sterilization chamber was evacuated with 5Q Torri. Then valve A
(After closing 3 and stopping the vacuum pump, the valve was opened to allow EOG, etc. to flow from the pressure accumulation tank 3 into the sterilization chamber in preparation for the next sterilization process.

なお蓄圧タンクの圧は7.5 ataから1.85at
aになり滅菌室の圧力は1.85ataとなったので弁
りを閉じて弁Fを開きEOGボンベよりEOG等を滅菌
室に補給し圧力2 ataになるようにした。これに要
した時間は2分であυ、lサイクル合計の所要時間は4
5分であった。
The pressure of the pressure storage tank is 7.5 ata to 1.85 ata.
A and the pressure in the sterilization chamber became 1.85 ata, so the valve was closed and valve F was opened to replenish EOG and the like from the EOG cylinder to the sterilization chamber to bring the pressure to 2 ata. The time required for this was 2 minutes υ, and the total time required for 1 cycle was 4
It was 5 minutes.

なおこの場合エチレングリコールとしてEOG吸収装置
で吸収された量は0,13Kfであり、にれは使用した
EOGの4俤に相当する。
In this case, the amount of ethylene glycol absorbed by the EOG absorption device was 0.13 Kf, and the amount was equivalent to 4 tons of EOG used.

〔発明の効果〕〔Effect of the invention〕

従来の運転ではEOGボンベ(EOG20%、cot 
80%の混合ガス)を600 KzA消費していたが本
発明の方法によりEOG等εして96憾、5、7 (l
i ′I4回収でき、4憾のEOGFiユチレングリコ
ールとして吸収され、大気汚染は殆とな(なった。
In conventional operation, EOG cylinder (EOG 20%, cot
80% mixed gas) was consuming 600 KzA, but by the method of the present invention, EOG etc.
i'I4 could be recovered and absorbed as 4 EOGFi ethylene glycol, resulting in almost no air pollution.

【図面の簡単な説明】[Brief explanation of drawings]

諮1図は本発明の一実施例を示すフローシー・トである
。譲2図は本発明の別の実施例を示すフローシートであ
る。
Figure 1 is a flow sheet showing one embodiment of the present invention. FIG. 2 is a flow sheet showing another embodiment of the present invention.

Claims (3)

【特許請求の範囲】[Claims] (1)滅菌室、真空ポンプ、クッションタンク、圧縮機
及び蓄圧タンクを順次配管により接続して蓄圧タンクよ
り滅菌室に戻る閉回路を形成し、該滅菌室内における滅
菌処理後のエチレンオキサイドガス(以下EOGと称す
る)を圧縮機により蓄圧タンクに蓄圧回収して再使用に
供し、該滅菌室における被処理物の出し入れ時に発生す
る回収不能の稀薄EOGを系外に排出すると共に不足す
るEOGを補給することを特徴とするEOGの回収方法
(1) A sterilization chamber, a vacuum pump, a cushion tank, a compressor, and a pressure storage tank are sequentially connected by piping to form a closed circuit that returns from the pressure storage tank to the sterilization chamber, and the ethylene oxide gas (hereinafter referred to as ethylene oxide gas) after sterilization in the sterilization chamber is The EOG (hereinafter referred to as EOG) is stored and recovered in a pressure storage tank using a compressor for reuse, and the unrecoverable diluted EOG generated when the objects to be processed are taken out and taken out of the sterilization chamber is discharged from the system, and the insufficient EOG is replenished. A method for collecting EOG characterized by the following.
(2)請求項(1)記載の閉回路において、該滅菌室に
水蒸気吹込手段を設けると共にクッションタンクと圧縮
機との間に除湿器を設け、滅菌工程中で発生するバクテ
リヤの死骸、菌類の胞子、ダスト及びEOG反応生成物
等を凝縮水と共に系外に排出することを特徴とするEO
Gの回収方法。
(2) In the closed circuit according to claim (1), a steam blowing means is provided in the sterilization chamber, and a dehumidifier is provided between the cushion tank and the compressor to remove dead bacteria and fungi generated during the sterilization process. EO characterized by discharging spores, dust, EOG reaction products, etc. out of the system together with condensed water
How to collect G.
(3)該滅菌室における被処理物の出し入れ時に発生す
る回収可能な限度以下の稀薄な残留EOGを真空ポンプ
により吸収装置に導いて除害した後、大気に排出するこ
とを特徴とする請求項(1)及び(2)記載のEOGの
回収方法。
(3) A claim characterized in that the dilute residual EOG, which is less than the recoverable limit, generated when the material to be processed is taken out and taken out of the sterilization chamber is guided to an absorption device by a vacuum pump, detoxified, and then discharged into the atmosphere. The EOG recovery method described in (1) and (2).
JP2115108A 1989-05-09 1990-05-02 Collecting method for ethylene oxide gas Pending JPH0373154A (en)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
JP11426589 1989-05-09
JP1-114265 1989-05-09

Publications (1)

Publication Number Publication Date
JPH0373154A true JPH0373154A (en) 1991-03-28

Family

ID=14633472

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2115108A Pending JPH0373154A (en) 1989-05-09 1990-05-02 Collecting method for ethylene oxide gas

Country Status (1)

Country Link
JP (1) JPH0373154A (en)

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