JPH07251027A - Management method of biological deodorizer - Google Patents
Management method of biological deodorizerInfo
- Publication number
- JPH07251027A JPH07251027A JP6066547A JP6654794A JPH07251027A JP H07251027 A JPH07251027 A JP H07251027A JP 6066547 A JP6066547 A JP 6066547A JP 6654794 A JP6654794 A JP 6654794A JP H07251027 A JPH07251027 A JP H07251027A
- Authority
- JP
- Japan
- Prior art keywords
- deodorizing
- packed bed
- organisms
- biological
- gas
- 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
Links
Classifications
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Landscapes
- Disinfection, Sterilisation Or Deodorisation Of Air (AREA)
- Treating Waste Gases (AREA)
Abstract
(57)【要約】
【目的】 停止状態からの再始動時に短期間に良好に装
置の脱臭能力を再生できる生物脱臭装置の管理方法を提
供する。
【構成】 悪臭成分を含むガス1を、悪臭成分を分解し
脱臭する微生物(以下「脱臭生物」という)を付着させ
た充填層3に接触させて脱臭する生物脱臭装置の管理方
法において、該装置の停止時には、充填層3に保持され
た脱臭生物を乾燥させて、該乾燥状態を停止中維持し、
使用時には、水分を補給9して脱臭能力を賦活させるこ
ととしたものであり、前記脱臭生物の乾燥は乾燥用ガス
を充填層に通すことにより行い、或は装置内を陰圧状態
にしてもよく、その含水率は30%以下とする。
(57) [Abstract] [Purpose] To provide a method for controlling a biological deodorizing device, which can satisfactorily regenerate the deodorizing ability of the device in a short period when restarting from a stopped state. In a method of controlling a biological deodorizing device, a gas 1 containing a malodorous component is brought into contact with a packed bed 3 to which microorganisms that decompose the malodorous component and deodorize (hereinafter referred to as “deodorizing organisms”) are attached to deodorize the device. When stopping, the deodorized organisms retained in the packed bed 3 are dried to maintain the dry state during suspension,
At the time of use, the deodorizing ability is activated by replenishing water 9, and the deodorizing organisms are dried by passing a drying gas through a packed bed, or even when the inside of the apparatus is in a negative pressure state. Often, the water content is 30% or less.
Description
【0001】[0001]
【産業上の利用分野】本発明は、生物脱臭装置の管理方
法に係り、特に、し尿処理場、下水処理場や化学工場等
で発生する脂肪酸、アンモニア、硫化水素、メチルメル
カプタン等の悪臭成分を含む悪臭ガスを脱臭する生物脱
臭装置の管理方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for controlling a biological deodorizing device, and more particularly, to a malodorous component such as fatty acid, ammonia, hydrogen sulfide and methyl mercaptan generated in human waste treatment plants, sewage treatment plants and chemical plants. The present invention relates to a method for managing a biological deodorizing device that deodorizes a malodorous gas including.
【0002】[0002]
【従来の技術】生物脱臭装置は、し尿処理場、下水処理
場及び化学工場等で発生する悪臭ガスに対する低コスト
の脱臭装置として広く利用されている。生物脱臭装置の
原理は以下の通りである。即ち、担体を充填した充填層
に悪臭ガスを通し、担体に付着した生物によって悪臭成
分を分解する。また、充填層に散水することによって生
物に水分を補給し、同時に充填層から老廃物を除去す
る。この際、悪臭成分は脱臭生物にとってはエネルギー
源あるいは炭素源である。そして、脱臭生物は悪臭成分
を分解することによって増殖する。増殖した脱臭生物は
自己分解や捕食されることによって死滅し、充填層内の
脱臭生物体量は悪臭成分供給量に応じて、ある量で動的
平衡状態となる。2. Description of the Related Art Biological deodorizers are widely used as low-cost deodorizers for malodorous gases generated in human waste treatment plants, sewage treatment plants, chemical plants and the like. The principle of the biological deodorizer is as follows. That is, the malodorous gas is passed through the packed bed filled with the carrier, and the malodorous components are decomposed by the organisms attached to the carrier. It also replenishes the organisms with water by watering the packed bed and at the same time removes waste products from the packed bed. At this time, the malodorous component is an energy source or a carbon source for the deodorizing organism. Then, the deodorizing organism proliferates by decomposing the malodorous component. The deodorized organisms that have proliferated die by autolysis and predation, and the amount of deodorized organisms in the packed bed is in a dynamic equilibrium state depending on the amount of malodorous component supplied.
【0003】ところで悪臭ガスの臭気濃度は、気候変化
及び工場の運転状況等によって変動し、それにともなっ
て生物脱臭装置の処理能力も変動する。従って、臭気が
発生しないときには、脱臭生物は増殖せず、死滅のみが
進行する。この状態が長期間に及ぶと充填層内の脱臭生
物は減少し、場合によってはほとんど残らず死滅してし
まう。このような状態では悪臭が再発生したとき、脱臭
能力は失われており、再起動させる際には下水や排水の
活性汚泥処理施設の余剰汚泥を接種するなどの処置を行
なっても回復のために数週間から1カ月以上の期間を要
する。By the way, the odor concentration of the malodorous gas varies depending on the climate change and the operating condition of the factory, and the treatment capacity of the biological deodorizer also varies accordingly. Therefore, when the odor is not generated, the deodorizing organism does not grow and only kills. If this state continues for a long period of time, the deodorizing organisms in the packed bed will decrease, and in some cases almost all will die. In such a condition, when the bad odor re-occurs, the deodorizing ability is lost, and when restarting, recovery is possible even if measures such as inoculating surplus sludge from the activated sludge treatment facility for sewage and wastewater are taken. It takes a few weeks to a month or more.
【0004】一方、上記のようないわゆる固定化微生物
を製造する方法として、特開昭64−2569号公報に
低温乾燥により自己粒子化する方法が開示され、脱臭に
供される生物については低温での乾燥に対して耐性を有
することが一般に知られている。また、上記技術の脱臭
への適用としては特開平5−123527号公報に、余
剰汚泥の乾燥物を固定化微生物(脱臭剤)として用いる
方法が記載されている。この方法では余剰汚泥の乾燥物
は生物担体と種汚泥の両方の機能を備えており、運転開
始時に余剰汚泥(懸濁液状のもの)を添加しなくても脱
臭できる。On the other hand, as a method for producing the so-called immobilized microorganism as described above, Japanese Patent Application Laid-Open No. 64-2569 discloses a method of self-particle formation by low-temperature drying. It is generally known to have resistance to dryness. Further, as an application of the above technique to deodorization, JP-A-5-123527 describes a method of using a dried product of excess sludge as an immobilized microorganism (deodorant). In this method, the dried product of the surplus sludge has both the functions of the biological carrier and the seed sludge, and can be deodorized without adding the surplus sludge (in the form of suspension) at the start of the operation.
【0005】上記技術は、一旦製造された脱臭微生物粒
子を曝気槽又は脱臭塔において使用するものであるた
め、脱臭固定化微生物の作用環境は従来の脱臭装置と大
差なく脱臭装置の水中に臭気が長期に渡って供給されな
いときには脱臭能力を失うであろうことは容易に推察さ
れる。さらに、この方法の実施例では空間速度(SV)
は約4hr-1程度であったが、近年、下水処理場などで
利用されている脱臭装置はSV=70〜750hr-1程
度であり、この方法は実用的ではなかった。Since the above-described technique uses the deodorized microbial particles once produced in an aeration tank or a deodorization tower, the working environment of the deodorant-immobilized microorganisms is not much different from that of the conventional deodorizing device, and the odor in the water of the deodorizing device does not change. It is easily inferred that the deodorizing ability will be lost when it is not supplied for a long period of time. Further, in this embodiment of the method, space velocity (SV)
Although a which was about 4hr -1, recently, deodorizing apparatus which is used in sewage treatment plants is about SV = 70~750hr -1, this method has not been practical.
【0006】[0006]
【発明が解決しようとする課題】本発明は、悪臭成分の
供給が停止した状態においても脱臭生物を維持し、再始
動時に種菌の添加等の手順を必要とせず、短時間に良好
に装置の脱臭能力を再生させることのできる生物脱臭装
置の管理方法を提供することを課題とする。DISCLOSURE OF THE INVENTION The present invention maintains a deodorant organism even when the supply of malodorous components is stopped, does not require a procedure such as addition of inoculum at the time of restarting, and can satisfactorily improve the device in a short time. An object of the present invention is to provide a management method of a biological deodorizing device capable of reproducing the deodorizing ability.
【0007】[0007]
【課題を解決するための手段】上記課題を解決するため
に、本発明では、悪臭成分を含むガスを、悪臭成分を分
解し脱臭する微生物(脱臭生物)を付着させた充填層に
接触させて脱臭する生物脱臭装置の管理方法において、
該装置の停止時には、充填層に保持された脱臭生物を乾
燥させて、該乾燥状態を停止中維持し、使用時には、水
分を補給して脱臭能力を賦活させることとしたものであ
る。In order to solve the above problems, in the present invention, a gas containing a malodorous component is brought into contact with a packed bed on which microorganisms (deodorant organisms) that decompose and deodorize malodorous components are attached. In the management method of the biological deodorizing device for deodorizing,
When the apparatus is stopped, the deodorizing organisms retained in the packed bed are dried to maintain the dry state during the stop, and when used, water is replenished to activate the deodorizing ability.
【0008】前記管理方法において、充填層に保持され
た脱臭生物の乾燥は、大気などの乾燥用ガス中の温度が
高いときには、乾燥用ガスを予めヒーターで加熱するか
又は除湿器で除湿して湿度を低減させてから充填層と接
触させればよく、この際装置内を陰圧状態にするのがよ
い。また、上記方法を実施するための脱臭装置として
は、悪臭成分を分解する微生物を付着した充填層と、充
填層の上部に循環水を散水するノズルと、下部に循環水
を受ける水槽と、処理ガスを充填層に送るための送風機
を具備した装置が使用でき、該装置には乾燥用ガスの湿
度を低減させるためのヒーター又は除湿器を設けてもよ
く、また、装置内を陰圧状態にするための真空ポンプを
具備してもよい。In the above management method, the deodorizing organisms retained in the packed bed are dried by heating the drying gas with a heater or dehumidifying with a dehumidifier when the temperature of the drying gas such as the atmosphere is high. It is only necessary to reduce the humidity and then to contact with the packed bed, and at this time, it is preferable that the inside of the apparatus is in a negative pressure state. Further, as a deodorizing device for carrying out the above method, a packed bed to which microorganisms decomposing malodorous components are attached, a nozzle for sprinkling circulating water on the upper part of the packed layer, a water tank for receiving circulating water on the lower part, and a treatment A device equipped with a blower for sending gas to the packed bed can be used, and the device may be provided with a heater or a dehumidifier for reducing the humidity of the drying gas, and the device is kept in a negative pressure state. You may provide the vacuum pump for this.
【0009】[0009]
【作用】本発明は、微生物菌株の保存方法として知られ
た低温乾燥保存という概念を、「PPM」1992年3
月号p22〜28や前記公報等に開示されている活性汚
泥生物だけでなく、開放型の大規模な脱臭装置におい
て、特化した脱臭生物群の保存再生に適用し、脱臭生物
の保存、能力再生に格別の効果を得た。即ち、本発明は
生物脱臭装置を停止する際に、脱臭微生物の充填層に供
給する水を停止して、装置内の水を排出した後、低湿度
の空気を該充填層に通気するか、あるいは装置全体を陰
圧にして充填層に保持された脱臭生物を乾燥させること
を特徴とする分解能力維持方法である。The present invention is based on the concept of low temperature dry preservation known as a method for preserving microbial strains, as described in "PPM" March 1992.
In addition to the activated sludge organisms disclosed in the monthly issues p22-28 and the above publications, etc., it is applied to the preservation and regeneration of specialized deodorant organism groups in an open-type large-scale deodorizing device, and the ability to preserve the deodorant organisms I got a special effect on the reproduction. That is, the present invention, when stopping the biological deodorizing device, stop the water supplied to the packed bed of deodorizing microorganisms, after draining the water in the device, or aeration of low humidity air to the packed bed, Alternatively, it is a method for maintaining the decomposing ability, which is characterized in that the deodorizing organism retained in the packed bed is dried by making the whole device into negative pressure.
【0010】以下、本発明の一例を示す図面を参照しな
がら本発明を詳細に説明する。図1は運転時の生物脱臭
装置の概略説明図、図2及び図3は乾燥時の生物脱臭装
置の概略説明図である。図1に示すように運転時には、
悪臭ガス1を送風機2を用いて充填層3に通し処理ガス
4を排気口5から排出する。また、循環水6を充填層3
上部のノズル7から散水し、充填層1下方に備え付けた
水槽8で捕集する。The present invention will be described in detail below with reference to the drawings showing an example of the present invention. FIG. 1 is a schematic explanatory diagram of the biological deodorizing device during operation, and FIGS. 2 and 3 are schematic explanatory diagrams of the biological deodorizing device during drying. As shown in Figure 1, during operation,
The malodorous gas 1 is passed through the packed bed 3 using the blower 2 and the processing gas 4 is discharged from the exhaust port 5. In addition, the circulating water 6 is filled with the packed bed 3
Water is sprayed from the upper nozzle 7 and collected in a water tank 8 provided below the packed bed 1.
【0011】低湿度の空気を充填層に通して脱臭生物を
乾燥させる方法については図2を用いて説明する。該装
置を停止する際には、まず通気及び散水を停止すると共
に排水口10より該装置内の水を排出する。続いて、空
気12をヒーター11で加熱した後充填層3に通し排ガ
ス13は、装置上部の排気口5より排出する。これによ
って充填層内の脱臭生物は乾燥される。乾燥は出来るか
ぎり低温で、しかも短時間で行なわれるのが好ましい。
低温の空気は飽和水蒸気濃度が小さいため、脱臭生物の
乾燥に使用すると、極めて長い時間を必要とする。A method of passing low-humidity air through the packed bed to dry the deodorized organism will be described with reference to FIG. When stopping the apparatus, first, ventilation and water sprinkling are stopped, and water in the apparatus is discharged from the drain port 10. Subsequently, the air 12 is heated by the heater 11 and then passed through the packed bed 3, and the exhaust gas 13 is discharged from the exhaust port 5 in the upper part of the apparatus. As a result, the deodorized products in the packed bed are dried. Drying is preferably carried out at the lowest temperature possible and in a short time.
Cold air requires a very long time when used to dry deodorant organisms because of its low saturated water vapor concentration.
【0012】しかし、低温の空気はわずかに加熱するこ
とで飽和水蒸気濃度を高めることが可能である。例え
ば、温度10℃の空気は飽和水蒸気濃度が0.008m
g−水蒸気/m3 −乾き空気であるが、温度30℃の空
気では0.027mg−水蒸気/m3 −乾き空気であ
る。すなわち、仮に温度10℃、相対湿度100%の空
気であっても30℃に加熱することによって、新たに
0.02mg−水蒸気/m3−乾き空気の水蒸気を保持
することが可能となる。ただし、温度を上げ過ぎると生
物の有する脱臭酵素が変性し、機能を失う危険性があ
る。However, it is possible to raise the saturated steam concentration by slightly heating low-temperature air. For example, air with a temperature of 10 ° C has a saturated steam concentration of 0.008 m.
g- steam / m 3 - is a dry air, at a temperature 30 ° C. The air 0.027mg- steam / m 3 - a dry air. That is, even if air having a temperature of 10 ° C. and a relative humidity of 100% is heated to 30 ° C., 0.02 mg-steam / m 3 -steam of dry air can be newly retained. However, if the temperature is raised too high, there is a risk that the deodorizing enzyme possessed by the organism will be denatured and its function will be lost.
【0013】従って、乾燥温度は対象とする微生物の温
度耐性に応じて決定される。例えば、耐熱性に優れたメ
タン酸化細菌では高い処理温度でも活性の維持が可能で
あるが、この場合においても約70℃以下であることが
望ましい。また活性汚泥などの好気性微生物を処理する
場合には約50℃以下であることが望ましい。実用上は
微生物を同定し得ないことが多いため、通常脱臭運転時
に許容される温度程度まで昇温することが好ましい。従
って、短時間の自然乾燥温度についで、ブロアの発熱に
よる温度上昇や高温高濃度臭気ガスであれば、冷却用熱
交換装置吐出温度を目安にできる。Therefore, the drying temperature is determined according to the temperature tolerance of the target microorganism. For example, the activity of methane-oxidizing bacteria having excellent heat resistance can be maintained even at a high treatment temperature, but in this case as well, it is desirable that the temperature is about 70 ° C or lower. When treating aerobic microorganisms such as activated sludge, the temperature is preferably about 50 ° C or lower. In many cases, it is practically impossible to identify microorganisms, and therefore it is preferable to elevate the temperature to a temperature that is usually allowed during deodorization operation. Therefore, if the temperature rises due to the heat generated by the blower or if the odorous gas has a high concentration and high temperature, the discharge temperature of the heat exchanger for cooling can be used as a guide after the natural drying temperature for a short time.
【0014】また、装置内を陰圧状態にすることによっ
て脱臭生物を乾燥する方法については図3を用いて説明
する。上記同様、まず該装置の通気及び散水を停止する
と共に該装置内の水を排出する。続いて、排気口5に真
空ポンプ14を連結し、他の開口部をすべて密閉し、真
空ポンプを運転して装置内部を陰圧にして装置内部の水
を揮発させて除去する。いずれの方法においても乾燥が
完了したら脱臭装置特に充填層を密閉しておく。その
際、乾燥状態を維持するために脱臭装置内に乾燥剤を投
入しておくことが好ましい。乾燥の目標としては、含水
率30%以下、好ましくは25%以下とするのがよい。
これ以上の含水率であると微生物の自己分解により、従
来と同様急速に脱臭能力が低下し、再生できなくなる。A method of drying the deodorized organisms by setting the inside of the apparatus to a negative pressure will be described with reference to FIG. Similar to the above, first, the ventilation and water sprinkling of the apparatus are stopped and the water in the apparatus is discharged. Then, a vacuum pump 14 is connected to the exhaust port 5, all other openings are sealed, the vacuum pump is operated to make the inside of the device a negative pressure, and the water inside the device is volatilized and removed. In any of the methods, after the drying is completed, the deodorizing device, especially the packing layer, is closed. At that time, in order to maintain the dry state, it is preferable to put a desiccant in the deodorizing device. The target of drying is to set the water content to 30% or less, preferably 25% or less.
When the water content is higher than this, self-decomposition of microorganisms causes a rapid decrease in deodorizing ability as in the conventional case, making regeneration impossible.
【0015】[0015]
【実施例】以下、本発明を実施例により具体的に説明す
るが、本発明はこれらの実施例に限定されない。 実施例1 以下の条件で3か月間、生物脱臭装置を運転した結果、
表1に示すように各種の悪臭成分は良く除去されてい
た。この生物脱臭装置の充填材を取りだし、充填材に付
着した硫黄酸化細菌を計数した。EXAMPLES The present invention will now be described in detail with reference to examples, but the present invention is not limited to these examples. Example 1 As a result of operating the biological deodorizer for 3 months under the following conditions,
As shown in Table 1, various malodorous components were well removed. The filler of this biological deodorizer was taken out, and the sulfur-oxidizing bacteria adhering to the filler were counted.
【0016】(処理条件) 空塔速度 : 0.7m/sec 散水量(単位処理時間当たり): 3 リットル/m3 ガス温度 : 20〜25℃ 充填材 : 特殊スポンジ 充填層断面積 : 0.2 m2 充填層高さ : 1 m 初期MLSS : 2000ppm 循環液のpH : 6〜8(NaOHで
調整)(Treatment conditions) Superficial velocity: 0.7 m / sec Water spray rate (per unit treatment time): 3 liters / m 3 Gas temperature: 20-25 ° C. Filler: Special sponge Cross section of packed bed: 0.2 m 2 Packed bed height: 1 m Initial MLSS: 2000 ppm pH of circulating fluid: 6 to 8 (adjusted with NaOH)
【0017】[0017]
【表1】 [Table 1]
【0018】また、同じ生物脱臭装置の充填材を乾燥器
に入れ、温度を40℃に保って充填材を乾燥させた。乾
燥時間を段階的に変えて、約10から70%の含水率の
充填材を得た。これらの充填物を密閉容器に入れて28
℃で放置した。2か月間経過後、前記の方法に従って硫
黄酸化菌数を測定し、充填材の含水率と長期保存後の硫
黄酸化細菌数の関係を明らかにした。以上の結果を図4
に示す。含水率25%以下では硫黄酸化細菌数は保存前
の約15分の1から5分の1の範囲にあり、良く保存さ
れていた。しかし、含水率が30%を越えると、細菌数
は急激に減少した。以上の結果から脱臭生物の付着した
充填材の含水率を約30%以下にすることによって硫黄
酸化細菌を長期間保存可能であることが明らかになっ
た。Further, the filler of the same biological deodorizing device was put in a drier and the temperature was kept at 40 ° C. to dry the filler. The drying time was changed stepwise to obtain a filler having a water content of about 10 to 70%. Put these fillings in a closed container 28
It was left at ℃. After 2 months, the number of sulfur-oxidizing bacteria was measured according to the method described above, and the relationship between the water content of the filler and the number of sulfur-oxidizing bacteria after long-term storage was clarified. The above results are shown in FIG.
Shown in. When the water content was 25% or less, the number of sulfur-oxidizing bacteria was in the range of about 1/15 to 1/5 of that before storage and was well preserved. However, when the water content exceeded 30%, the number of bacteria decreased sharply. From the above results, it was clarified that the sulfur-oxidizing bacteria can be stored for a long period of time by setting the water content of the filler to which the deodorizing organism is attached to about 30% or less.
【0019】実施例2 3台の生物脱臭装置、装置1、装置2及び装置3を以下
に示す処理条件で3か月間運転した。悪臭ガスは人為的
に調整した。その結果、表2に示すように流入悪臭物質
はいずれの装置においても高効率で分解されていた。 (処理条件) 空塔速度 : 0.7m/sec 散水量(単位処理時間当たり): 3 リットル/m3 ガス温度 : 20〜25℃ 充填材 : 特殊スポンジ 充填層断面積 : 0.2 m2 充填層高さ : 1 m 初期MLSS : 2000ppm 循環液のpH : 6〜8(NaOHで
調整)Example 2 Three biological deodorizers, device 1, device 2 and device 3 were operated for 3 months under the treatment conditions shown below. The malodorous gas was artificially adjusted. As a result, as shown in Table 2, the inflowing malodorous substances were decomposed with high efficiency in any of the devices. (Treatment conditions) Superficial velocity: 0.7 m / sec Sprinkling amount (per unit treatment time): 3 liter / m 3 Gas temperature: 20 to 25 ° C. Filler: Special sponge Filled layer cross-sectional area: 0.2 m 2 Filling Layer height: 1 m Initial MLSS: 2000 ppm pH of circulating fluid: 6-8 (adjusted with NaOH)
【0020】[0020]
【表2】 [Table 2]
【0021】続いて、各装置の通気及び散水を停止し
た。そして、装置1及び装置2は循環水を排出した後、
以下の条件で脱臭生物を乾燥した。装置1は湿度を低減
させた大気を充填層に通して乾燥させた。装置2は装置
内部を陰圧状態にして乾燥させた。その後、装置1及び
装置2は密閉して放置した。また、装置3は通気及び散
水を停止して、そのまま放置した。Subsequently, ventilation and water sprinkling of each device were stopped. And after the circulating water is discharged from the device 1 and the device 2,
The deodorized product was dried under the following conditions. The device 1 was dried by passing a reduced-humidity atmosphere through a packed bed. The device 2 was dried by setting the inside of the device to a negative pressure state. After that, the device 1 and the device 2 were sealed and left to stand. In addition, the device 3 stopped the ventilation and water sprinkling and was left as it was.
【0022】(装置1の乾燥条件) 空塔速度 : 0.7m/sec 流入ガス温度 : 40 ℃ 流入ガス相対湿度 : 10〜40% 乾燥時間 : 4 日間 (装置2の乾燥条件) 真空度 : 約70Torr以下 乾燥温度 : 8〜17℃ 乾燥時間 : 4 日間 放置する前に各装置の脱臭生物の含水率を測定した。そ
の結果は表3の通りであった。(Drying conditions of apparatus 1) Superficial velocity: 0.7 m / sec Inflowing gas temperature: 40 ° C. Inflowing gas relative humidity: 10-40% Drying time: 4 days (Drying conditions of apparatus 2) Degree of vacuum: Approximately 70 Torr or less Drying temperature: 8 to 17 ° C. Drying time: 4 days Before standing, the water content of the deodorizing organisms in each device was measured. The results are shown in Table 3.
【0023】[0023]
【表3】 [Table 3]
【0024】2か月経過後、装置1及び2に循環水を注
入し、散水を再開し、続いて以上3台の装置を初期の運
転条件で運転した。表4は運転5日後の処理成績であ
る。装置1及び2は乾燥前の処理成績に近い処理成績が
得られた。一方、装置3は3種類の悪臭物質共にかなり
高い割合で処理ガスに残留していた。これは装置1及び
2では乾燥によって脱臭生物の多くが保存された結果、
脱臭能力が維持され、装置3では大半の脱臭生物が死滅
した結果、脱臭能力が失われたことを示している。After the lapse of 2 months, circulating water was injected into the devices 1 and 2, watering was restarted, and then the above three devices were operated under the initial operating conditions. Table 4 shows the treatment results after 5 days of operation. The processing results of the devices 1 and 2 were similar to the processing results before drying. On the other hand, in the device 3, all the three types of malodorous substances remained in the treated gas at a considerably high rate. This is because most of the deodorant organisms were preserved by drying in the devices 1 and 2,
The deodorizing ability is maintained, and the device 3 shows that the deodorizing ability is lost as a result of the death of most of the deodorizing organisms.
【0025】[0025]
【表4】 [Table 4]
【0026】[0026]
【発明の効果】本発明によれば、脱臭装置を長期間停止
した後でも、極めて短期間で脱臭能力を回復させること
ができる。According to the present invention, the deodorizing ability can be restored in an extremely short period of time even after the deodorizing device has been stopped for a long period of time.
【図1】運転時の生物脱臭装置の概略説明図。FIG. 1 is a schematic explanatory diagram of a biological deodorizing device during operation.
【図2】低湿度の空気を充填層に通して脱臭生物を乾燥
させる際の生物脱臭装置の概略説明図。FIG. 2 is a schematic explanatory view of a biological deodorizing apparatus when drying a deodorizing organism by passing low humidity air through a packed bed.
【図3】装置内を陰圧状態にすることによって脱臭成分
を乾燥させる際の生物脱臭装置の概略説明図。FIG. 3 is a schematic explanatory view of a biological deodorizing device when drying a deodorizing component by setting a negative pressure inside the device.
【図4】充填材の乾燥状態と硫黄酸化菌の長期保存状態
の関係を示すグラフ。FIG. 4 is a graph showing the relationship between the dry state of the filler and the long-term storage state of sulfur-oxidizing bacteria.
1:悪臭ガス、2:送風機、3:充填層、4:処理ガ
ス、5:排気口、6:循環水、7:ノズル、8:水槽、
9:供給水、10:排水口、11:ヒーター、12:空
気、13:排ガス、14:真空ポンプ1: Malodorous gas, 2: Blower, 3: Packed bed, 4: Process gas, 5: Exhaust port, 6: Circulating water, 7: Nozzle, 8: Water tank,
9: Supply water, 10: Drainage port, 11: Heater, 12: Air, 13: Exhaust gas, 14: Vacuum pump
───────────────────────────────────────────────────── フロントページの続き (51)Int.Cl.6 識別記号 庁内整理番号 FI 技術表示箇所 A61L 9/01 P B01D 53/34 ZAB (72)発明者 北川 政美 神奈川県藤沢市本藤沢4丁目2番1号 株 式会社荏原総合研究所内─────────────────────────────────────────────────── ─── Continuation of the front page (51) Int.Cl. 6 Identification code Internal reference number FI Technical display location A61L 9/01 P B01D 53/34 ZAB (72) Inventor Masami Kitagawa 4-chome, Fujisawa, Fujisawa-shi, Kanagawa No. 2 No. 1 EBARA Research Institute
Claims (1)
し脱臭する微生物(以下「脱臭生物」という)を付着さ
せた充填層に接触させて脱臭する生物脱臭装置の管理方
法において、該装置の停止時には、充填層に保持された
脱臭生物を乾燥させて、該乾燥状態を停止中維持し、使
用時には、水分を補給して脱臭能力を賦活させることを
特徴とする生物脱臭装置の管理方法。1. A method for controlling a biological deodorizing device, which comprises deodorizing a gas containing a malodorous component by contacting it with a packed bed on which a microorganism that decomposes the malodorous component and deodorizes it (hereinafter referred to as "deodorizing organism") is used. When stopping, the deodorizing organisms retained in the packed bed are dried, the dry state is maintained during suspension, and at the time of use, the deodorizing ability is activated by replenishing water to control the biological deodorizing device. .
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6066547A JPH07251027A (en) | 1994-03-11 | 1994-03-11 | Management method of biological deodorizer |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP6066547A JPH07251027A (en) | 1994-03-11 | 1994-03-11 | Management method of biological deodorizer |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| JPH07251027A true JPH07251027A (en) | 1995-10-03 |
Family
ID=13319048
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP6066547A Pending JPH07251027A (en) | 1994-03-11 | 1994-03-11 | Management method of biological deodorizer |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH07251027A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN119386664A (en) * | 2024-12-31 | 2025-02-07 | 上海展冀环境有限公司 | A biological deodorizing device for waste gas deodorizer |
-
1994
- 1994-03-11 JP JP6066547A patent/JPH07251027A/en active Pending
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN119386664A (en) * | 2024-12-31 | 2025-02-07 | 上海展冀环境有限公司 | A biological deodorizing device for waste gas deodorizer |
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