JPH11137953A - Microorganism deodorization apparatus and method for operating the apparatus - Google Patents

Microorganism deodorization apparatus and method for operating the apparatus

Info

Publication number
JPH11137953A
JPH11137953A JP9322349A JP32234997A JPH11137953A JP H11137953 A JPH11137953 A JP H11137953A JP 9322349 A JP9322349 A JP 9322349A JP 32234997 A JP32234997 A JP 32234997A JP H11137953 A JPH11137953 A JP H11137953A
Authority
JP
Japan
Prior art keywords
water
carrier
storage tank
nitrifying bacteria
bacteria
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.)
Granted
Application number
JP9322349A
Other languages
Japanese (ja)
Other versions
JP3447537B2 (en
Inventor
Akio Ono
秋夫 大野
Tatsuo Nagai
達夫 永井
Sukenori Kunoki
右典 九軒
Kenji Fukushima
健次 福島
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.)
Japan Steel Works Ltd
Original Assignee
Japan Steel Works Ltd
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 Japan Steel Works Ltd filed Critical Japan Steel Works Ltd
Priority to JP32234997A priority Critical patent/JP3447537B2/en
Publication of JPH11137953A publication Critical patent/JPH11137953A/en
Application granted granted Critical
Publication of JP3447537B2 publication Critical patent/JP3447537B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A50/00TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
    • Y02A50/20Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/10Biological treatment of water, waste water, or sewage

Abstract

PROBLEM TO BE SOLVED: To enable the exhibition of good ammonia deodorization performance from the initial period of operation by providing the apparatus with water spraying equipment for spraying water to carriers deposited with microorganisms and a water storage tank for recovering the sprayed water and adding liquid media and nitrifying bacteria to the water in the water storage tank before the operation of the apparatus. SOLUTION: An the time of operation of the deodorization device, the nitrifying bacteria 15 previously cultured in the liquid media are added together with the media into the water 6 in the water storage tank 6. Odors are supplied through an odor pipe 2 into a deodorization vessel 1 and the water added with the nitrifying bacteria in the storage tank 6 is sprayed toward the carriers 3 from a water spraying section 10 through a water lifting pipe 8 and a water spraying pipe 9 by a pump 7. The sprayed water partly passes among the carriers 3 and moves from a shelf section 1a to a water receiving section 1b and is circulated by refluxing the same to the storage tank 6 through a return pipe 5. When the odor amt. to the odor pipe 2 is thereafter put into a stationary state, the ammonia component in the odor is surely cracked and the waste gases substantially not containing the ammonia are discharged from a discharge pipe 4.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、有機性廃棄物のコ
ンポスト化プラント、下水処理場、畜舎等で発生する臭
気に含まれているアンモニアガスを脱臭処理する微生物
脱臭装置およびその運転方法に関するものである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a microorganism deodorizing apparatus for deodorizing ammonia gas contained in an odor generated in an organic waste composting plant, a sewage treatment plant, a livestock barn, and the like, and a method of operating the same. It is.

【0002】[0002]

【従来の技術】従来の微生物脱臭方法では、微生物脱臭
装置の立ち上げ時に、下水処理場の活性汚泥液を散布し
て臭気ガスを流し、その臭気ガスを処理することができ
る菌を増やしていた。これは、微生物を担持する担体に
は、ゼオライト、木炭、スラグ、セラミックス、活性
炭、PVAゲルなどの無機質材料、または有機質材料を
使用するが、これらの担体には、脱臭を行う菌はほとん
ど付着しておらず、したがって、活性汚泥等を用いて、
菌を添加し、ゆっくりと臭気負荷をあげながら菌を増や
す馴養と呼ばれる期間が必要であるためである。さらに
上記脱臭装置では、微生物の活動環境を整えるために水
分の管理が必要であり、散水装置を付設して必要に応じ
て担体に散水している。また、この散水では担体に固定
されている微生物が多少なりとも流されるので、散水さ
れて担体中を移動した水を回収して貯水タンクに収容
し、これを再度、散水に使用している。そして、上記担
体中で微生物が順調に活動すると、担体中を通過する臭
気成分が微生物によって分解され、脱臭作用が得られ
る。
2. Description of the Related Art In a conventional microorganism deodorizing method, when starting up a microorganism deodorizing apparatus, an activated sludge solution in a sewage treatment plant is sprayed to flow odor gas, thereby increasing the number of bacteria capable of treating the odor gas. . This is because, for the carrier that carries the microorganisms, inorganic materials such as zeolite, charcoal, slag, ceramics, activated carbon, and PVA gel, or organic materials are used, but bacteria that deodorize adhere to these carriers. Therefore, using activated sludge, etc.,
This is because a period called acclimation, in which the bacteria are added and the bacteria are increased while slowly increasing the odor load, is required. Further, in the above deodorizing device, it is necessary to control the water content in order to prepare an environment for the activity of microorganisms, and a watering device is attached to water the carrier as required. In addition, in this sprinkling, the microorganisms fixed on the carrier are flowed to some extent, so that the water that has been sprinkled and moved in the carrier is collected, stored in a water storage tank, and used again for sprinkling. Then, when the microorganisms work smoothly in the carrier, the odor components passing through the carrier are decomposed by the microorganisms, and a deodorizing effect is obtained.

【0003】[0003]

【発明が解決しようとする課題】ところで、臭気には各
種の臭気成分が含まれており、臭気発生源によっては、
臭気中にアンモニア成分が多く含まれている。しかし、
アンモニアを酸化処理する硝化細菌(主としてアンモニ
ア酸化細菌、亜硝酸酸化細菌)の増殖速度は、他の従属
栄養細菌と比較した場合、1/30〜1/6であるた
め、アンモニアを処理するのに十分な菌密度になる前
に、臭気中の他の臭気成分を栄養源として他種の細菌の
増殖が早期に進行する。そして、上記したように脱臭で
は担体に散水を行うことが不可欠であるので、微生物を
固定しておくためには担体表面に付着していることが必
要である。しかし、担体の表面積には限りがあるため、
上記のように他種の細菌の増殖が優位に進行して担体表
面に固定されてしまうと、その後、硝化細菌が増殖して
も付着可能な担体表面が得られず、よって担体に固定さ
れることなく散水で流されてしまうので十分なアンモニ
ア分解性能が得られない。さらに、このような状態が長
く続くと臭気ガスのアンモニアにより担体のpHが上が
って硝化細菌の生育範囲以外の環境になるので、硝化細
菌の活性が失われるという問題が発生する。上記の理由
により、従来の脱臭装置では、高濃度のアンモニアを含
む臭気ガスを微生物脱臭で行うのは困難とされている。
本発明は、上記事情を背景としてなされたものであり、
運転立ち上げ時に硝化細菌の優位性を確保して上記問題
を解決し、運転初期から良好なアンモニア脱臭性能を発
揮することができる微生物脱臭装置およびその運転方法
を提供することを目的とする。
By the way, the odor contains various odor components, and depending on the source of the odor,
The odor contains a large amount of ammonia. But,
Since the growth rate of nitrifying bacteria (mainly ammonia-oxidizing bacteria and nitrite-oxidizing bacteria) that oxidize ammonia is 1/30 to 1/6 as compared with other heterotrophic bacteria, it is difficult to treat ammonia. Before reaching a sufficient bacterial density, the growth of other types of bacteria proceeds early using other odor components in the odor as nutrient sources. As described above, it is essential to spray water on the carrier for deodorization. Therefore, in order to fix microorganisms, it is necessary to adhere to the surface of the carrier. However, since the surface area of the carrier is limited,
As described above, if the growth of other types of bacteria progresses predominantly and is fixed to the carrier surface, then even if nitrifying bacteria grow, a carrier surface to which the bacteria can adhere cannot be obtained, and thus the bacteria are fixed to the carrier. As a result, sufficient ammonia decomposition performance cannot be obtained. Furthermore, if such a state continues for a long time, ammonia in the odorous gas raises the pH of the carrier and becomes an environment outside the growth range of the nitrifying bacteria, thus causing a problem that the activity of the nitrifying bacteria is lost. For the above reasons, it is difficult for conventional deodorizers to remove odorous gas containing high-concentration ammonia by microorganism deodorization.
The present invention has been made in view of the above circumstances,
It is an object of the present invention to provide a microorganism deodorizing apparatus capable of solving the above problem by securing the superiority of nitrifying bacteria at the start of operation and exhibiting good ammonia deodorizing performance from the beginning of operation, and an operation method thereof.

【0004】[0004]

【課題を解決するための手段】上記課題を解決するため
本発明の微生物脱臭装置は、微生物を担持する担体と、
該担体に散水する散水設備と、散水した水を回収する貯
水タンクとを備えており、装置運転前に該貯水タンク内
水に液体培地と、他の細菌の増殖を抑えて優先的に培養
した硝化細菌とが添加されていることを特徴とする。
Means for Solving the Problems To solve the above problems, a microorganism deodorizing apparatus of the present invention comprises: a carrier for supporting microorganisms;
A sprinkler for sprinkling the carrier and a water storage tank for collecting the sprinkled water are provided, and prior to the operation of the device, the liquid medium in the water in the water storage tank, and preferentially cultured while suppressing the growth of other bacteria. It is characterized by adding nitrifying bacteria.

【0005】また、第2の発明の微生物脱臭装置の運転
方法は、微生物を担持する担体と、該担体に散水する散
水設備と、散水した水を回収する貯水タンクとを備え、
前記微生物によってアンモニアガスを含む臭気を脱臭す
る微生物脱臭装置の運転方法において、少なくとも運転
立ち上げ時迄に、予め培養しておいた硝化細菌を担体ま
たは散水中に添加することを特徴とする。さらに、第3
の発明の微生物脱臭装置の運転方法は、第2の発明にお
いて、前記硝化細菌が、他の細菌の増殖を抑えて優先的
に増殖させたものであることを特徴とする。
[0005] A method of operating a microorganism deodorizing apparatus according to a second aspect of the present invention includes a carrier for supporting microorganisms, a watering facility for sprinkling water on the carrier, and a water storage tank for collecting sprinkled water.
In the method for operating a microorganism deodorizing apparatus for deodorizing an odor containing ammonia gas by the microorganism, a nitrifying bacterium that has been cultured in advance is added to a carrier or water spray at least at the time of starting operation. In addition, the third
The method for operating a microorganism deodorizing device according to the invention is characterized in that, in the second invention, the nitrifying bacteria are grown preferentially while suppressing the growth of other bacteria.

【0006】本発明は、アンモニアを臭気成分として含
む臭気を対象とするものであり、その発生源としては、
前述したようにコンポスト化プラント、下水処理場、畜
舎が例示される。ただし、本発明としては、これらに限
定されるものではなく、アンモニアを含む臭気を発生す
るものであれば、その発生源を問わない。また、処理す
べきアンモニアの濃度も特に限定されるものではない
が、本発明では、500ppmを越える濃度のアンモニ
アを含む臭気においても確実にアンモニアの分解を行う
ことができる。なお、予め培養して添加される硝化細菌
は、主としてアンモニア酸化細菌と亜硝酸酸化細菌から
なる。本発明としては、上記の中で特定に細菌に限定さ
れるものではないが、アンモニア酸化細菌と亜硝酸酸化
細菌とがバランスよく混在するものが望ましい。
[0006] The present invention is directed to an odor containing ammonia as an odor component.
As described above, a composting plant, a sewage treatment plant, and a barn are exemplified. However, the present invention is not limited to these, and any source may be used as long as it generates an odor including ammonia. Further, the concentration of ammonia to be treated is not particularly limited, but in the present invention, ammonia can be reliably decomposed even with an odor containing ammonia having a concentration exceeding 500 ppm. The nitrifying bacteria added after being cultured in advance mainly consist of ammonia oxidizing bacteria and nitrite oxidizing bacteria. The present invention is not particularly limited to bacteria among the above, but it is preferable that ammonia-oxidizing bacteria and nitrite-oxidizing bacteria are mixed in a well-balanced manner.

【0007】上記微生物を担持する担体には、前述した
ように、ゼオライト、木炭、スラグ、セラミックス、活
性炭、PVAゲルなどの無機質材料、または有機質材料
を使用することができるが、アンモニアガスの吸着性に
優れたゼオライトが最適である。従来は、この担体に活
性汚泥を混合し、その中から硝化細菌を馴養していた
が、本発明では、硝化細菌の優位性を確保するため、活
性汚泥は使用せず、予め培養した硝化細菌のみで運転を
開始するのが望ましい。上記担体は、大規模の装置で
は、大地に穴を掘り、この穴に収容することができ、ま
た適当な容器に収容するようにしてもよい。担体の収容
部では、底部で散水した水を回収するように回収部を設
ける。例えば大地の穴に担体を収容している場合には、
地面中に水が浸透しないようにシートなどの水遮断層を
設け、この遮断層から水を採って貯水タンクに収容する
ことができる。貯水タンクに収容された水は、ポンプ等
によって散水設備に供給し、この散水設備から担体に水
を散水する。なお、散水設備の構成や、散水方法は本発
明としては特に限定されるものではない。
As described above, inorganic or organic materials such as zeolite, charcoal, slag, ceramics, activated carbon, and PVA gel can be used as the carrier for supporting the microorganisms. The best zeolite is the best. Conventionally, activated sludge was mixed with this carrier, and nitrifying bacteria were acclimated from the mixture.In the present invention, however, in order to secure the superiority of nitrifying bacteria, activated sludge was not used, and nitrifying bacteria previously cultured were used. It is desirable to start operation only with. In a large-scale device, the carrier may be dug in the ground and accommodated in this hole, or may be accommodated in a suitable container. In the carrier accommodating section, a collecting section is provided so as to collect water sprinkled at the bottom. For example, if you have a carrier in the hole in the earth,
A water blocking layer such as a sheet is provided so that water does not penetrate into the ground, and water can be taken from this blocking layer and stored in a water storage tank. The water stored in the water storage tank is supplied to a watering facility by a pump or the like, and water is sprayed from the watering facility to the carrier. The structure of the watering equipment and the watering method are not particularly limited as the present invention.

【0008】上記硝化細菌は、脱臭装置の運転に先立っ
て、予め適当な培地や環境等を定めて培養しておく。こ
の培養では他の細菌の増殖を抑えて硝化細菌を優先的に
増殖させるのが望ましい。この結果、硝化細菌の個数
が、他の細菌を含めた総個数に対し、90%以上となる
のが望ましい。また、硝化細菌の濃度は、運転前に培地
とともにタンクの貯水中に添加した状態で、貯水中に1
6個/ml以上存在するのが望ましい。
[0008] Prior to the operation of the deodorizing device, the nitrifying bacteria are cultured with an appropriate medium, environment, and the like defined in advance. In this culture, it is desirable to suppress the growth of other bacteria and preferentially grow nitrifying bacteria. As a result, it is desirable that the number of nitrifying bacteria is 90% or more of the total number including other bacteria. In addition, the concentration of nitrifying bacteria should be 1
0 to present 6 cells / ml or more.

【0009】上記硝化細菌は、少なくとも運転立ち上げ
時までに担体または散水する水に添加するが、担体に均
一に添加できるように、散水の水に添加して散水ととも
に担体に添加するのが望ましい。硝化細菌の添加は、上
記のように運転立ち上げ迄に行うのが必須であるが、運
転後、硝化細菌の補給を目的に任意の時期に添加するこ
とも可能である。ただし、運転立ち上げ迄に行う添加と
は上記のように明らかに目的が異なっている。すなわ
ち、運転立ち上げ迄に行う添加では、硝化細菌を他の細
菌よりも優先的に担体に固定して、担体の表面を硝化細
菌で優先的に占有させることを目的としており、単なる
硝化細菌の補給とは異なる。その後、運転の続行におい
ても、担体への固定状態で硝化細菌が優位な状態が維持
され、臭気のアンモニア成分が確実かつ効率的に分解さ
れることになる。
The nitrifying bacteria are added to the carrier or water to be sprinkled at least at the start of the operation. However, it is desirable that the nitrifying bacteria be added to the water to be sprinkled and added to the carrier together with the sprinkle so that the bacteria can be uniformly added. . It is essential to add nitrifying bacteria before the start of operation as described above, but it is also possible to add nitrifying bacteria at any time after the operation for the purpose of replenishing nitrifying bacteria. However, the purpose is clearly different from the addition performed before the start of operation as described above. That is, the addition performed before the start-up of the operation is intended to fix the nitrifying bacteria on the carrier preferentially over other bacteria and to occupy the surface of the carrier preferentially with the nitrifying bacteria. Different from replenishment. Thereafter, even when the operation is continued, the state in which the nitrifying bacteria are dominant in the state of being fixed to the carrier is maintained, and the ammonia component of the odor is reliably and efficiently decomposed.

【0010】なお、運転の初期には、担体のpH上昇を
抑制しつつ臭気ガスを担体に流すとともに、前記貯水タ
ンク内水を担体に散水しつつ散水した水を回収するよう
に循環させて硝化細菌を優先的に増殖させながら担体に
固定するのが望ましい。この方法により、優先的に増殖
した硝化細菌が循環しつつ次第に担体に固定されるの
で、担体の表面において早期かつ確実に硝化細菌を優位
に固定することができ、運転早期から優れたアンモニア
分解性能が得られる。したがって、この運転方法は、従
来の馴養のように単に硝化細菌の増殖を意図するもので
はなく、担体の表面を硝化細菌が優位に占めることが重
要である。また、pHの上昇抑制は、pHが硝化細菌の
活動範囲外に迄上がらない程度や所定のpH上限値を定
めて行うことができるが、硝化細菌の活性度を確保する
ためには、余裕を見てpHの上限値を定めるのが望まし
く、例えば、このpH上限値として9.0を例示するこ
とができる。上記条件の維持は、負荷する臭気の送風量
やアンモニア濃度を制御することにより行うことができ
る。
In the early stage of the operation, the odor gas is allowed to flow through the carrier while suppressing the pH rise of the carrier, and the water in the water storage tank is circulated so as to collect the sprinkled water while spraying the water onto the carrier. It is desirable to immobilize the bacteria on the carrier while preferentially growing the bacteria. By this method, the nitrifying bacteria that have been preferentially grown are gradually fixed to the carrier while circulating, so that the nitrifying bacteria can be fixed dominantly and reliably on the surface of the carrier early, and the excellent ammonia decomposition performance can be achieved from the early operation. Is obtained. Therefore, this operation method is not intended to simply increase the nitrifying bacteria as in the conventional practice, but it is important that the nitrifying bacteria dominate the surface of the carrier. In addition, the suppression of the increase in pH can be performed by setting the pH to such an extent that the pH does not rise outside the activity range of the nitrifying bacteria or a predetermined upper limit of the pH. However, in order to secure the activity of the nitrifying bacteria, there is a margin. It is desirable to determine the upper limit of the pH, and for example, 9.0 can be exemplified as the upper limit of the pH. The above conditions can be maintained by controlling the amount of odor blown and the ammonia concentration to be loaded.

【0011】すなわち、本発明によれば、運転初期に十
分に増殖された硝化細菌が得られる。そして硝化細菌
中、アンモニア酸化細菌は、アンモニアを酸化して亜硝
酸に変え、この亜硝酸は、亜硝酸酸化細菌によって酸化
されて硝酸イオンとなる。この硝酸イオンは、脱窒細菌
により還元され窒素になって大気中に放出されたり、散
水の水に溶け込んで持ち去られることにより、高濃度の
アンモニアにおいても生化学的に良好に分解される。
That is, according to the present invention, a nitrifying bacterium that has been sufficiently grown in the early stage of operation can be obtained. Among the nitrifying bacteria, the ammonia oxidizing bacteria oxidize ammonia to nitrite, and the nitrite is oxidized by the nitrite oxidizing bacteria into nitrate ions. This nitrate ion is reduced by denitrifying bacteria to become nitrogen and released into the atmosphere, or dissolved in water of sprinkling and carried away, so that even high-concentration ammonia is satisfactorily biochemically decomposed.

【0012】[0012]

【発明の実施の形態】以下、本発明の一実施形態を添付
図面に基づいて説明する。脱臭槽1は、箱形形状からな
り、その底部に通水性の棚部1aを有するとともに、天
井部に近接して臭気管2が連結されており、該臭気管2
は、図示しない臭気源および送風装置に接続されてい
る。また、該脱臭槽1内には、前記棚部1aで支持する
ようにしてゼオライト粒からなる担体3が収容されてい
る。さらに、脱臭槽1の棚部1a下には、排気管4が連
結されているとともに、水受け部1bが確保されてお
り、該水受け部1bに戻り管5の一端が連結されてい
る。該戻り管5の他端は貯水タンク6に連結されてい
る。また貯水タンク6内には、ポンプ7の吸引側に接続
した揚水管8が配置されており、ポンプ7の吐出側に
は、散水管9を介して散水部10が接続されている。該
散水部10は、脱臭槽1内において上記担体3の上方に
位置されており、上記ポンプ7、揚水管8、散水管9、
散水部10によって散水設備が構成されている。
DESCRIPTION OF THE PREFERRED EMBODIMENTS One embodiment of the present invention will be described below with reference to the accompanying drawings. The deodorizing tank 1 has a box shape, has a water-permeable shelf 1a at the bottom thereof, and is connected to an odor pipe 2 near the ceiling.
Are connected to an odor source and a blower (not shown). Further, in the deodorizing tank 1, a carrier 3 made of zeolite particles is accommodated so as to be supported by the shelf 1a. Further, below the shelf 1a of the deodorization tank 1, an exhaust pipe 4 is connected, and a water receiver 1b is secured. One end of a return pipe 5 is connected to the water receiver 1b. The other end of the return pipe 5 is connected to a water storage tank 6. A water pump 8 connected to the suction side of the pump 7 is disposed in the water storage tank 6, and a water sprinkling section 10 is connected to the discharge side of the pump 7 via a water sprinkling pipe 9. The water sprinkling section 10 is located above the carrier 3 in the deodorizing tank 1, and includes the pump 7, the water pipe 8, the water sprinkling pipe 9,
The water spraying unit 10 constitutes a water spray facility.

【0013】上記で説明した脱臭装置の動作について説
明すると、予め硝化細菌を液体培地で優先的に培養して
おき、この硝化細菌15(図中には模式的に記載)を貯
水タンク6内の水6a中に、培地とともに添加する。そ
して、臭気管2を通して定常時よりも少ない量の臭気を
脱臭槽1内に供給するとともに、ポンプ7を稼働させて
貯水タンク6内の水を揚水管8によって硝化細菌15と
ともに揚水して散水管9を等して散水部10から担体3
に向けて散水する。この散水は、一部が担体3間を通過
して棚部1aから水受け部1bに移動し、さらに戻り管
5を通して貯水タンク6に環流することにより循環す
る。この循環に際しては、硝化細菌15が増殖しながら
徐々に担体3に付着して固定化され、固体された硝化細
菌15も次第に増殖する。担体3の表面において硝化細
菌が優先的に固定されたことが確認された後、臭気管2
への臭気量を定常状態にすると、臭気中のアンモニア成
分が確実に分解され、アンモニアを殆ど含まない排気ガ
スが排気管4から脱臭槽1外部に排出される。
The operation of the deodorizing apparatus described above will be described. Nitrifying bacteria are preferentially cultured in a liquid medium in advance, and the nitrifying bacteria 15 (shown schematically in the figure) are stored in the water storage tank 6. It is added to the water 6a together with the medium. Then, a smaller amount of odor than in the normal state is supplied into the deodorizing tank 1 through the odor pipe 2, and the pump 7 is operated to pump water from the water storage tank 6 together with the nitrifying bacteria 15 by the pumping pipe 8 to spray the water. 9 to the carrier 3
Sprinkle water for Part of the sprinkling passes between the carriers 3, moves from the shelf 1 a to the water receiving portion 1 b, and circulates by returning to the water storage tank 6 through the return pipe 5. During this circulation, the nitrifying bacteria 15 are gradually attached to and fixed to the carrier 3 while growing, and the solidifying nitrifying bacteria 15 also gradually grow. After it was confirmed that nitrifying bacteria were preferentially fixed on the surface of the carrier 3, the odor tube 2
When the amount of odor to the odor is in a steady state, the ammonia component in the odor is surely decomposed, and the exhaust gas containing almost no ammonia is discharged from the exhaust pipe 4 to the outside of the deodorization tank 1.

【0014】[0014]

【実施例】上記実施形態の脱臭装置を用いて、本発明の
実施例として予め硝化細菌を液体培地において優先的に
培養したものと、比較例として活性汚泥を用いたものと
を比較試験した。なお、予め硝化細菌を優先的に培養し
たものでは、細菌総個数に対し、硝化細菌の個数が約9
0%であり、その濃度は108個/mlであった。この
硝化細菌を液体培地100l(リットル)とともに、1
0m3の水を収容した貯水タンクに投入した。また、活
性汚泥うわずみ液では、硝化細菌の濃度が約106個/
mlであり、この活性汚泥うわずみ液100lを担体に
混合した。各試験では、運転初期にアンモニア濃度が3
00ppmの臭気を100m3/分の風量で脱臭槽に送
気し、それぞれ散水を行った。上記初期運転を2週間行
った後、臭気の風量を200m3/分に増加して定常状
態とし、その排気中のアンモニア濃度を測定したとこ
ろ、本発明の実施例では未検出であり、比較例では10
ppmであった。上記結果から、本発明の装置および方
法によれば、比較例に比べてアンモニアの分解性能が顕
著に優れていることが明らかとなった。
EXAMPLE Using the deodorizing apparatus of the above embodiment, a comparative test was conducted between an example in which nitrifying bacteria were preferentially cultured in a liquid medium in advance and an example using activated sludge as a comparative example. In the case where nitrifying bacteria were preferentially cultured in advance, the number of nitrifying bacteria was about 9% of the total number of bacteria.
0% and the concentration was 10 8 cells / ml. This nitrifying bacterium is mixed with 100 l (liter) of liquid medium for 1 hour.
It was charged into a water storage tank containing 0 m 3 of water. In addition, the concentration of nitrifying bacteria was about 10 6 /
ml of the activated sludge was mixed with the carrier. In each test, the ammonia concentration was 3 at the beginning of operation.
An odor of 00 ppm was sent to the deodorizing tank at an air flow rate of 100 m 3 / min, and water was sprayed. After the initial operation was performed for two weeks, the air volume of the odor was increased to 200 m 3 / min to a steady state, and the ammonia concentration in the exhaust was measured. Then 10
ppm. From the above results, it has been clarified that the apparatus and method of the present invention have remarkably excellent ammonia decomposition performance as compared with the comparative example.

【0015】[0015]

【発明の効果】以上説明したように、本発明の微生物脱
臭装置によれば、微生物を担持する担体と、該担体に散
水する散水設備と、散水した水を回収する貯水タンクと
を備えており、装置運転前に該貯水タンク内水に液体培
地と他の細菌の増殖を抑えて優先的に培養した硝化細菌
とが添加されているので、運転初期に硝化細菌を効率よ
くかつ均一に担体に接触させて、担体に優位に固定する
ことができ、運転初期から優れたアンモニアの分解性能
を発揮する。
As described above, according to the microorganism deodorizing apparatus of the present invention, a carrier for supporting microorganisms, a watering facility for sprinkling water on the carrier, and a water storage tank for collecting sprinkled water are provided. Before the operation of the apparatus, the liquid medium and the nitrifying bacteria cultured preferentially while suppressing the growth of other bacteria are added to the water in the water storage tank. It can be fixed to the carrier by contact, and exhibits excellent ammonia decomposition performance from the beginning of operation.

【0016】また、本発明の微生物脱臭装置の運転方法
によれば、運転立ち上げ時迄に、予め培養しておいた硝
化細菌を担体または散水中に添加するので、立ち上げ迄
に担体のpHが上がったり、他の細菌が優位になるのを
抑制して、硝化細菌を担体に優位に固定することがで
き、その結果、優れたアンモニア分解性能を引き出すこ
とができる。また、上記運転方法において、前記硝化細
菌を、他の細菌の増殖を抑えて優先的に増殖させたもの
とすれば、運転初期時に硝化細菌の優位性を一層確実な
ものとし、他の細菌に比べて増殖速度の遅い硝化細菌に
おいても担体への固定において優位性が得られる。
According to the method for operating a microorganism deodorizing apparatus of the present invention, nitrifying bacteria which have been cultured in advance are added to a carrier or watering by the time of starting operation, so that the pH of the carrier is increased by the time of starting. Thus, the nitrifying bacteria can be fixed to the carrier in a dominant manner by suppressing the increase in the number of bacteria and other bacteria, and as a result, excellent ammonia decomposition performance can be obtained. Further, in the above-mentioned operation method, if the nitrifying bacteria are preferentially grown while suppressing the growth of other bacteria, the superiority of the nitrifying bacteria is further ensured at the initial stage of the operation, and the nitrifying bacteria can be used for other bacteria. Even in nitrifying bacteria having a slower growth rate, superiority can be obtained in fixing to a carrier.

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

【図1】 本発明の一実施形態の脱臭装置を示す概略図
である。
FIG. 1 is a schematic view showing a deodorizing device according to an embodiment of the present invention.

【符号の説明】[Explanation of symbols]

1 脱臭槽 2 臭気管 3 担体 5 戻り管 6 貯水タンク 7 ポンプ 8 揚水管 9 散水管 10 散水部 15 硝化細菌 DESCRIPTION OF SYMBOLS 1 Deodorizing tank 2 Odor pipe 3 Carrier 5 Return pipe 6 Water storage tank 7 Pump 8 Pumping pipe 9 Sprinkling pipe 10 Sprinkling part 15 Nitrifying bacteria

フロントページの続き (51)Int.Cl.6 識別記号 FI C02F 3/34 101 (72)発明者 福島 健次 広島県広島市安芸区船越南1丁目6番1号 株式会社日本製鋼所内Continued on the front page (51) Int.Cl. 6 Identification code FI C02F 3/34 101 (72) Inventor Kenji Fukushima 1-6-1, Funakoshiminami, Aki-ku, Hiroshima-shi, Hiroshima Japan Steel Works Co., Ltd.

Claims (3)

【特許請求の範囲】[Claims] 【請求項1】 微生物を担持する担体と、該担体に散水
する散水設備と、散水した水を回収する貯水タンクとを
備えており、装置運転前に該貯水タンク内水に液体培地
と他の細菌の増殖を抑えて優先的に培養した硝化細菌と
が添加されていることを特徴とする微生物脱臭装置
Claims: 1. A carrier for supporting microorganisms, a water spraying device for sprinkling water on the carrier, and a water storage tank for collecting the water sprinkled, and a liquid medium and other water are added to the water in the water storage tank before operation of the device. A microbial deodorizing device characterized by adding nitrifying bacteria, which are preferentially cultured while suppressing bacterial growth.
【請求項2】 微生物を担持する担体と、該担体に散水
する散水設備と、散水した水を回収する貯水タンクとを
備え、前記微生物によってアンモニアガスを含む臭気を
脱臭する微生物脱臭装置の運転方法において、少なくと
も運転立ち上げ時迄に、予め培養しておいた硝化細菌を
担体または散水中に添加することを特徴とする微生物脱
臭装置の運転方法
2. A method for operating a microorganism deodorizing apparatus, comprising: a carrier carrying microorganisms; a water spraying facility for sprinkling water on the carrier; and a water storage tank for collecting water sprinkled, wherein the microorganisms deodorize odors containing ammonia gas. The method for operating a microbial deodorizer, characterized in that nitrifying bacteria previously cultured are added to a carrier or water spray at least at the start of operation.
【請求項3】 前記硝化細菌は、他の細菌の増殖を抑え
て優先的に増殖させたものであることを特徴とする請求
項2記載の微生物脱臭装置の運転方法
3. The method for operating a microorganism deodorizing apparatus according to claim 2, wherein the nitrifying bacteria are grown preferentially while suppressing the growth of other bacteria.
JP32234997A 1997-11-07 1997-11-07 Microorganism deodorizing device and method of operating the device Expired - Fee Related JP3447537B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP32234997A JP3447537B2 (en) 1997-11-07 1997-11-07 Microorganism deodorizing device and method of operating the device

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP32234997A JP3447537B2 (en) 1997-11-07 1997-11-07 Microorganism deodorizing device and method of operating the device

Publications (2)

Publication Number Publication Date
JPH11137953A true JPH11137953A (en) 1999-05-25
JP3447537B2 JP3447537B2 (en) 2003-09-16

Family

ID=18142658

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP3447537B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002143636A (en) * 2000-11-13 2002-05-21 Takashi Hirai Deodorizing equipment
CN110841392A (en) * 2019-10-28 2020-02-28 江苏科技大学 Oil fume treatment device and method combining water curtain and bubbling

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2002143636A (en) * 2000-11-13 2002-05-21 Takashi Hirai Deodorizing equipment
CN110841392A (en) * 2019-10-28 2020-02-28 江苏科技大学 Oil fume treatment device and method combining water curtain and bubbling
CN110841392B (en) * 2019-10-28 2021-08-13 江苏科技大学 Oil fume treatment device and method combining water curtain and bubbling

Also Published As

Publication number Publication date
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