JPH11169649A - Microbial deodorization apparatus - Google Patents

Microbial deodorization apparatus

Info

Publication number
JPH11169649A
JPH11169649A JP9354204A JP35420497A JPH11169649A JP H11169649 A JPH11169649 A JP H11169649A JP 9354204 A JP9354204 A JP 9354204A JP 35420497 A JP35420497 A JP 35420497A JP H11169649 A JPH11169649 A JP H11169649A
Authority
JP
Japan
Prior art keywords
tank
deodorizing
water
deodorization
odor
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
JP9354204A
Other languages
Japanese (ja)
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 JP9354204A priority Critical patent/JPH11169649A/en
Publication of JPH11169649A publication Critical patent/JPH11169649A/en
Pending 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

Landscapes

  • Treating Waste Gases (AREA)
  • Biological Treatment Of Waste Water (AREA)
  • Purification Treatments By Anaerobic Or Anaerobic And Aerobic Bacteria Or Animals (AREA)

Abstract

PROBLEM TO BE SOLVED: To efficiently treat the complex odors contg. plural odor components in addition to ammonia by microbial deodorization. SOLUTION: This apparatus is provided with a plurality of deodorization tanks 1 and 11 housing carriers 3 and 13 carrying microorganisms and an odor introducing pipe 12 of the deodorization tank 11 of the rear stage is connected to a discharge pipe 4 of the deodorizatibn tank 1 of the fore stage. The gaseous ammonia is deodorized by the deodorization tank 1 of the first state and the other odors are deodorized by the deodorization tank 11 of the rear stage. As a result, the ammonia in the odors is efficiently treated by the deodorization tank of the first stage and the other odor components are treated by the deodorization tanks of the second and subsequent stages, by which the composite odors are efficiently deodorized.

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、
アンモニアガスを含む複合臭気を効率的に処理できる微
生物脱臭装置に関するものである。
The present invention relates to an organic waste composting plant, sewage treatment plant, livestock barn, etc.
The present invention relates to a microorganism deodorizing device capable of efficiently treating a complex odor containing ammonia gas.

【0002】[0002]

【従来の技術】従来、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を脱臭する方
法として微生物を用いた方法が知られている。この方法
では、微生物を担体に担持させ、この担体を脱臭槽に収
納して脱臭槽内に臭気を送り込み、前記微生物の活動に
よって臭気成分を分解して脱臭するものである。この脱
臭装置の一例を示すと、臭気導入管25aおよび排気管
25bを設けた脱臭槽25内に、微生物20を担持する
担体26が収納されており、該担体26の下方の脱臭槽
25底部には担体26に散水されて担体26中を一部透
過した水を受ける水受け部27が設けられている。この
水受け部27は、脱臭槽25の外部に設置した貯水タン
ク28に連結されており、貯水タンク28内の水は散水
装置29によって担体26に散水される。この散水は、
上記したように一部が担体26中を通過して水受け部2
7に移動し、さらに貯水タンク28へと環流することに
より循環する。
2. Description of the Related Art Conventionally, a method using microorganisms has been known as a method for deodorizing odors generated in composting plants for organic waste, sewage treatment plants, livestock pens, and the like. In this method, microorganisms are carried on a carrier, the carrier is housed in a deodorizing tank, odor is sent into the deodorizing tank, and odor components are decomposed and deodorized by the activity of the microorganisms. As an example of this deodorizing device, a carrier 26 carrying microorganisms 20 is accommodated in a deodorizing tank 25 provided with an odor introducing pipe 25a and an exhaust pipe 25b. Is provided with a water receiving portion 27 which receives water which is sprayed on the carrier 26 and partially permeates the carrier 26. The water receiving portion 27 is connected to a water storage tank 28 installed outside the deodorization tank 25, and water in the water storage tank 28 is sprinkled on the carrier 26 by a water sprinkling device 29. This watering,
As described above, a part passes through the carrier 26 and
7 and then circulates by flowing back to the water storage tank 28.

【0003】なお、上記装置の運転に際しては活性汚泥
等(図示しない)を担体26に混合しておき、この脱臭
槽25に臭気導入管25aから臭気を導入するととも
に、必要に応じて散水装置29から担体26および活性
汚泥等に向けて散水する。すると、活性汚泥に含まれる
微生物は、適度な水分と基質とが与えられることにより
徐々に増殖し、次第に担体に固定され、臭気を分解す
る。また、散水によって、一部の微生物は水とともに移
動し、また臭気成分や微生物の活動によって生成された
分解物の一部がこの水に溶解して持ち去られる。この水
は、一旦、貯水タンク28に収容されるため、貯水タン
ク28内においてこれら成分を基質とする微生物の分解
反応が起こり、脱臭性能を高める。
In operation of the above apparatus, activated sludge or the like (not shown) is mixed in a carrier 26, and odor is introduced into the deodorization tank 25 from an odor introduction pipe 25a. , And water is sprayed toward the carrier 26 and the activated sludge. Then, the microorganisms contained in the activated sludge gradually grow by being provided with appropriate moisture and a substrate, are gradually fixed to the carrier, and decompose the odor. Also, due to the water spray, some microorganisms move together with water, and a part of odor components and decomposition products generated by the activity of microorganisms are dissolved in the water and carried away. Since this water is once stored in the water storage tank 28, a decomposition reaction of microorganisms using these components as a substrate occurs in the water storage tank 28, and the deodorizing performance is enhanced.

【0004】[0004]

【発明が解決しようとする課題】ところで、上記のよう
な設備で発生する臭気には、アンモニアガスを初めとす
る複数の臭気成分が含まれており、このような複合臭気
では、各臭気成分に対応した複数種の微生物の存在およ
び活動が必要になる。しかし、複数の微生物では、それ
ぞれ最適な活動環境が異なるため、上記のような複合臭
気では、微生物によって効果的な脱臭を行うのは困難で
あるのが現状である。本発明者は、上記のような複合臭
気の脱臭性能の改善につき研究を進めたところ、複合臭
気中に上記のようにアンモニアガスが含まれていると、
アンモニアの溶解によって担体および散水の回収水のp
Hが高くなっていることが判明した。このようにpHが
上がると、アンモニア以外の臭気を処理する微生物にと
っては、活動しにくい環境になるため、その働きが悪く
なって全体の脱臭性能が低下することが分かった。本発
明は、上記事情を背景としてなされたものであり、最初
に第1段目の脱臭槽でアンモニアを除去し、後段の脱臭
槽でその他の臭気を処理することによって複合臭気を効
果的に脱臭することができる微生物脱臭装置を提供する
ことを目的とする。
By the way, the odor generated by the above-mentioned equipment contains a plurality of odor components such as ammonia gas. Corresponding presence and activity of multiple types of microorganisms are required. However, since a plurality of microorganisms have different optimum activity environments, it is difficult at present to effectively deodorize the microorganisms with the complex odor as described above. The present inventor has conducted research on improving the deodorizing performance of the above-described complex odor, and when the composite odor contains ammonia gas as described above,
The carrier and sprinkled recovery water p
H was found to be high. It has been found that when the pH is increased in this manner, the environment becomes difficult for microorganisms that treat odors other than ammonia to act, so that the function is deteriorated and the overall deodorizing performance is reduced. The present invention has been made in view of the above circumstances. First, ammonia is removed in a first-stage deodorizing tank, and other odors are treated in a second-stage deodorizing tank, thereby effectively deodorizing a complex odor. It is an object of the present invention to provide a microorganism deodorizing device that can perform the method.

【0005】[0005]

【課題を解決するための手段】上記課題を解決するた
め、本発明のうち、第1の発明の微生物脱臭装置は、微
生物と該微生物を担持する担体とを収納して、アンモニ
アガスを含む臭気を内部に取り入れて前記微生物により
脱臭した後、外部に排気する脱臭槽を備えた微生物脱臭
装置において、前記脱臭槽を複数有しているとともに、
脱臭槽同士は、前段の脱臭槽の排気を後段の脱臭槽に取
り入れるように直列に接続されており、さらに、第1段
目の脱臭槽は、アンモニアガスの脱臭に割り当てられ、
後段の脱臭槽は、その他の臭気の脱臭に割り当てられて
いることを特徴とする。
Means for Solving the Problems In order to solve the above-mentioned problems, among the present invention, a microorganism deodorizing apparatus according to a first aspect of the present invention accommodates microorganisms and a carrier carrying the microorganisms, and comprises an odor containing ammonia gas. After deodorizing the microorganisms by taking it into the inside, in a microorganism deodorizing device provided with a deodorizing tank to exhaust to the outside, while having a plurality of the deodorizing tank,
The deodorizing tanks are connected in series so that the exhaust gas of the preceding deodorizing tank is taken into the latter deodorizing tank, and the first deodorizing tank is assigned to deodorize ammonia gas.
The deodorization tank in the latter stage is characterized by being assigned to deodorization of other odors.

【0006】第2の発明の微生物脱臭装置は、第1の発
明において、前記担体に散水する散水設備と、散水した
水を脱臭槽から回収して再度散水に供するように貯水す
る貯水タンクとをそれぞれ複数備えており、少なくとも
最前段の脱臭槽には専用の散水設備と貯水タンクとが割
り当てられており、該専用の貯水タンクおよび散水設備
では、第1段目の脱臭槽との間でのみ散水された水の回
収と散水とが行われることを特徴とする。
In a second aspect of the present invention, in the first aspect of the present invention, the microorganism deodorizing apparatus comprises: a water spraying device for sprinkling water on the carrier; and a water storage tank for collecting the water sprinkled from the deodorizing tank and storing it again for water sprinkling. At least the first stage deodorizing tank is provided with a dedicated sprinkler and a water storage tank, and the dedicated water storage tank and sprinkler is provided only between the first deodorizing tank and the first deodorizing tank. It is characterized in that the sprinkled water is collected and sprinkled.

【0007】第3の発明の微生物脱臭装置は、第1また
は第2の発明において、第1段目の脱臭槽に硝化細菌が
付着され、後段の脱臭槽にはその他の臭気を処理する細
菌が付着されていることを特徴とする。
A third aspect of the present invention is the microorganism deodorizing apparatus according to the first or second aspect, wherein nitrifying bacteria are attached to the first-stage deodorizing tank, and bacteria for treating other odors are provided in the second-stage deodorizing tank. It is characterized by being attached.

【0008】本発明は、アンモニアを臭気成分として含
む複合臭気の脱臭を目的とするものであり、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、畜舎等が例示される。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、5ppm以上のアンモ
ニアガスを含む複合臭気の脱臭において、特に効果があ
る。これは5ppm以上のアンモニアガスを臭気中に含
む際に、担体や散水の回収水のpHが顕著に上昇するた
めである。
[0008] The present invention aims at deodorizing a complex odor containing ammonia as an odor component. Examples of the generation source include a composting plant, a sewage treatment plant, and a livestock barn as described above. However, the present invention is not limited to these, and any source may be used as long as it generates an odor including ammonia. The concentration of ammonia to be treated is not particularly limited, but the present invention is particularly effective in deodorizing a complex odor containing ammonia gas of 5 ppm or more. This is because when the odor contains ammonia gas of 5 ppm or more, the pH of the carrier or the water collected by sprinkling significantly increases.

【0009】また、上記した複合臭気を脱臭するため
に、本発明では、アンモニアガスの分解のために硝化細
菌が用いられる。なお、第1段の脱臭槽には、その機能
としてアンモニアガスの脱臭が割り当てられているの
で、アンモニアガスを分解する硝化細菌を第1段目の脱
臭槽に付着させるのが望ましい。なお、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
が、本発明としては、上記の中で特定に細菌に限定され
るものではなく、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されているものが望ましい。ま
た、その後段の脱臭槽では、脱臭目的の臭気成分に適合
するように、その他の微生物を単独でまたは複数種が混
在した状態で活着させるのが望ましい。
Further, in order to deodorize the above-mentioned complex odor, nitrifying bacteria are used in the present invention for decomposing ammonia gas. Since the function of the first-stage deodorizing tank is to deodorize ammonia gas, it is desirable to attach nitrifying bacteria that decompose ammonia gas to the first-stage deodorizing tank. The nitrifying bacteria are mainly composed of ammonia-oxidizing bacteria and nitrite-oxidizing bacteria, but the present invention is not limited to the above-described bacteria, and the ammonium-oxidizing bacteria and nitrite-oxidizing bacteria are balanced. Those that are well mixed are desirable. In the subsequent deodorization tank, it is desirable to activate other microorganisms alone or in a mixture of plural types so as to be compatible with the odor component intended for deodorization.

【0010】なお、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。上記担体に前記した微生
物を固定する際、従来は、担体に活性汚泥を混合するこ
とによって行っており、本発明においてもこの方法を採
用することができるが、特にこの方法に限定されるもの
ではなく、例えば、予め培養した細菌を添加するもので
あってもよい。特に、第1段目の脱臭槽において硝化細
菌を付着させる際には、他の細菌の増殖を抑えて優先的
に培養した硝化細菌を用いるのが有効である。優先的な
培養は、適当な培地や環境等を定めて培養することによ
り行うことができる。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、99%と以上となるのが
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106
個/l以上存在するのが望ましい。なお、上記硝化細菌
は、液体培地とともに貯水タンクに投入して散水するこ
とにより担体に散布することができる。このように散水
とともに散布すれば、担体に均一に添加することができ
る。
[0010] 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. In fixing the microorganisms described above to the carrier, conventionally, the method is carried out by mixing activated sludge with the carrier, and this method can be employed in the present invention, but is not particularly limited to this method. Instead, for example, bacteria that have been cultured in advance may be added. In particular, when attaching nitrifying bacteria in the first-stage deodorizing tank, it is effective to use nitrifying bacteria which are preferentially cultured while suppressing the growth of other bacteria. The preferential culture can be performed by defining an appropriate medium, environment and the like and culturing. As a result, the number of nitrifying bacteria is desirably 99% or more of the total number including other bacteria. The concentration of nitrifying bacteria, while added to the water storage tank with medium before driving into the water 106
It is desirable that there be at least 1 / l. In addition, the said nitrifying bacteria can be sprayed on a carrier by throwing into a water storage tank together with a liquid medium and spraying water. By spraying together with watering in this manner, it can be uniformly added to the carrier.

【0011】上記担体を収納する脱臭槽としては、大規
模の装置では、大地に穴を掘り、この穴を脱臭槽として
利用することができ、また適当な容器を脱臭槽として使
用することもできる。脱臭槽には、臭気を取り入れる取
り入れ部と、脱臭したガスを排気する排気部とを設け
る。この脱臭槽は、前段の脱臭槽の排気を後段の脱臭槽
の取り入れ部に送るようにして2段以上を直列に接続す
る。ただし、第1段目の脱臭槽では、当然に臭気取り入
れ部は、臭気の発生源に連結されており、最終段の脱臭
槽では、排気部は、そのまま大気に開放されたり、適当
な排気設備等に連結される。この脱臭槽は2段以上であ
れば、その数は限定されない。
As a deodorizing tank for accommodating the carrier, in a large-scale apparatus, a hole can be dug in the ground and this hole can be used as a deodorizing tank, and an appropriate container can be used as a deodorizing tank. . The deodorization tank is provided with an intake section for taking in odors and an exhaust section for exhausting deodorized gas. In this deodorization tank, two or more stages are connected in series such that exhaust gas from the preceding deodorization tank is sent to the intake of the subsequent deodorization tank. However, in the first-stage deodorizing tank, the odor intake section is naturally connected to the source of the odor, and in the final-stage deodorizing tank, the exhaust section is directly opened to the atmosphere or an appropriate exhaust equipment is provided. And so on. The number of the deodorizing tanks is not limited as long as the number is two or more.

【0012】なお各脱臭槽では、さらに、散水した水を
回収するように水回収部を設ける。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。ただし、第1段目の脱臭槽では、専用
の貯水タンクおよび散水装置を設置して、この脱臭槽を
介してのみ水が循環するように構成するのが望ましい。
これは、貯水タンクや散水装置を他の脱臭槽と共用する
と、回収した水にアンモニアが溶解して水のpHを上
げ、これを他の脱臭槽に散水することにより、アンモニ
ア以外の臭気を処理する微生物の働きを阻害するためで
ある。なお、第2段目以降の脱臭槽では、上記とは別の
貯水タンクと散水装置を設置して複数の脱臭槽で共用す
ることも可能であるが、特定の脱臭槽で回収した水が他
の脱臭槽に悪影響を与えるようであれば、その特定の脱
臭槽について上記と同様に専用の貯水タンク、散水装置
を設けることも可能である。
Each of the deodorizing tanks is further provided with a water collecting section for collecting sprinkled water. For example, when a carrier is accommodated in a hole in the ground, a water barrier layer such as a sheet may be provided to prevent water from penetrating into the ground, and water may be taken from the barrier 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. However, in the first-stage deodorizing tank, it is desirable to provide a dedicated water storage tank and a sprinkler so that water circulates only through the deodorizing tank.
This is because if the water storage tank and water sprinkler are shared with other deodorizing tanks, the dissolved water will dissolve ammonia, raise the pH of the water, and sprinkle it into other deodorizing tanks to treat odors other than ammonia. This is to inhibit the action of the microorganisms. In the deodorization tanks of the second and subsequent stages, it is possible to install a separate water storage tank and water sprinkler and share them with multiple deodorization tanks. If it has an adverse effect on the deodorizing tank, it is also possible to provide a dedicated water storage tank and a sprinkler for the specific deodorizing tank as described above.

【0013】[0013]

【発明の実施の形態】次に、本発明の一実施形態を添付
図面に基づき説明する。この脱臭装置は、2段の脱臭槽
を有しており、一段目の脱臭槽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取り入れ部として臭気導入管2が連
結されており、該臭気導入管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、側方に抜けて次段の臭気導入管12と連
結される排気管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
(貯水槽)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7aが配置され
ており、ポンプ7の吐出側には、散水管8aを介して散
水部8が接続されており、該散水部8は、脱臭槽1内に
おいて上記担体3の上方に位置している。なお、上記ポ
ンプ7、揚水管7a、散水管8a、散水部8によって散
水装置が構成されている。また、第2段目の脱臭槽11
も上記とほぼ同様の構成を有しており、前記した臭気導
入管12と図示しない排気設備に接続された排気管14
と棚部11aおよび水受け部11bとが設けられてお
り、棚部11a上にはゼオライト粒からなる担体13が
収納されている。また、水受け部11bには連結管15
が接続されており、該連結管15は上記と同様に貯水タ
ンク16に接続されている。そしてこの貯水タンク16
から揚水して担体13に散水する散水装置が、ポンプ1
7、揚水管17a、散水管18a、散水部18によって
構成されている。以上に示すように、2つの脱臭槽1、
11は、それぞれ専用の貯水タンクと散水装置とを有し
ている。
Next, an embodiment of the present invention will be described with reference to the accompanying drawings. This deodorizing apparatus has a two-stage deodorizing tank. The first-stage deodorizing tank 1 has a box shape, has a water-permeable shelf 1a at the bottom thereof, and has an odor near the ceiling. An odor introduction pipe 2 is connected as an intake section, and the odor introduction pipe 2 is 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 which is connected to the next-stage odor introduction pipe 12 through the side is connected, and a water receiving section 1b is secured. One end of the return pipe 5 is connected to the water receiving portion 1b. The other end of the return pipe 5 is connected to a water storage tank (water storage tank) 6. In the water storage tank 6, a water pump 7a connected to the suction side of the pump 7 is arranged, and to the discharge side of the pump 7, a water sprinkling section 8 is connected via a water sprinkling pipe 8a. The part 8 is located above the carrier 3 in the deodorization tank 1. The pump 7, the water pump 7a, the water sprinkler 8a, and the water sprinkler 8 constitute a water sprinkler. In addition, the second-stage deodorization tank 11
Has substantially the same configuration as the above, and has the above-described odor introduction pipe 12 and an exhaust pipe 14 connected to exhaust equipment (not shown).
And a shelf 11a and a water receiving portion 11b. A carrier 13 made of zeolite grains is stored on the shelf 11a. In addition, a connecting pipe 15 is provided in the water receiving portion 11b.
The connecting pipe 15 is connected to a water storage tank 16 in the same manner as described above. And this water storage tank 16
A sprinkler for pumping water from the pump and spraying water on the carrier 13 is a pump 1
7. It is constituted by a water pump 17a, a water sprinkler 18a, and a water sprinkler 18. As shown above, two deodorization tanks 1
Numeral 11 has a dedicated water storage tank and a sprinkler.

【0014】次に、上記脱臭装置の動作について説明す
る。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20a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、臭気導入管2を通してアン
モニアを含む臭気を脱臭槽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7aに
よって硝化細菌20aとともに揚水して散水管8aを等
して散水部8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1
b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20aが増殖しながら徐々に担体3に付着し、付着
した硝化細菌20aも次第に増殖する。この硝化細菌2
0aによって臭気中のアンモニア成分が確実に分解さ
れ、一部は貯水タンク6内においても同様に分解を受け
る。このようにしてアンモニアは分解されて、アンモニ
アを殆ど含まない臭気ガスが排気管4から次段の脱臭槽
11に臭気導入管12を通して送られる。
Next, the operation of the deodorizing device will be described. Nitrifying bacteria are preferentially cultured in a liquid medium in advance,
The nitrifying bacteria 20a are added to the water 6a in the water storage tank 6 together with the medium. Then, the odor containing ammonia is supplied into the deodorization tank 1 through the odor introduction pipe 2, and the pump 7 is operated to pump water from the water storage tank 6 together with the nitrifying bacteria 20 a by the pumping pipe 7 a so that the water sprinkling pipe 8 a is discharged. Then, water is sprayed from the water spraying section 8 toward the carrier 3. A part of the water is passed between the carriers 3 and the water is transferred from the shelf 1a to the water receiver 1
b, and further circulates by returning to the water storage tank 6 through the return pipe 5. During this circulation, the nitrifying bacteria 20a gradually attach to the carrier 3 while growing, and the attached nitrifying bacteria 20a also gradually grow. This nitrifying bacterium 2
The ammonia component in the odor is surely decomposed by Oa, and a part thereof is similarly decomposed in the water storage tank 6. In this way, the ammonia is decomposed, and the odor gas containing almost no ammonia is sent from the exhaust pipe 4 to the next-stage deodorizing tank 11 through the odor introduction pipe 12.

【0015】なお、脱臭槽11では、運転に先立って脱
臭槽11内に活性汚泥上澄液(図示しない)を添加して
担体13と十分に混合しておく。この活性汚泥上澄液に
は、通常、硝化細菌も含まれているが、硝化細菌は他の
細菌と比べて増殖が遅いため、アンモニアを処理した臭
気をこの脱臭槽に送り込めば、その他の細菌20bが優
先的に増殖して、実質的には硝化細菌以外の細菌20b
が付着した状態になる。この脱臭槽11における動作も
上記脱臭槽1における動作と同じであり、アンモニア以
外の臭気成分、例えば硫化水素がイオウ酸化細菌によっ
て分解される。この際に、上記と同様に担体13に散水
がなされ、水受け部11bに移動した水が貯水タンク1
6に回収されて再度、散水に使用される。第1段目の脱
臭槽1でアンモニアが除かれ、この脱臭槽11によって
臭気成分硫化水素が除かれたガスは、十分な脱臭がなさ
れており、排気管14から図示しない排気設備へと送ら
れる。なお、この実施形態では、脱臭槽を2段設けたも
のを説明したが、必要に応じて3段以上の脱臭槽を設け
ることも可能である。
In the deodorizing tank 11, an activated sludge supernatant (not shown) is added to the deodorizing tank 11 and sufficiently mixed with the carrier 13 before the operation. This activated sludge supernatant usually contains nitrifying bacteria, but nitrifying bacteria grow slower than other bacteria, so if ammonia-treated odor is sent to this deodorization tank, other Bacteria 20b grow preferentially, and bacteria 20b substantially other than nitrifying bacteria
Is attached. The operation in the deodorization tank 11 is the same as the operation in the deodorization tank 1, and odor components other than ammonia, for example, hydrogen sulfide are decomposed by sulfur-oxidizing bacteria. At this time, water is applied to the carrier 13 in the same manner as described above, and the water that has moved to the water receiving portion 11b is stored in the water storage tank 1
6 and used again for watering. The gas from which ammonia has been removed in the first-stage deodorization tank 1 and the odor component hydrogen sulfide has been removed by the deodorization tank 11 has been sufficiently deodorized, and is sent from the exhaust pipe 14 to exhaust equipment (not shown). . In this embodiment, the deodorizing tank is provided in two stages, but three or more deodorizing tanks can be provided as necessary.

【0016】[0016]

【実施例】上記実施形態の脱臭装置の性能を評価するた
め、上記第1段目と第2段目の脱臭槽容量の総量とほぼ
同じ容量の脱臭槽をただ一つ有する一段型の脱臭装置を
従来例として用意し、臭気成分としてアンモニアを30
0ppm、硫化水素を10ppm、メチルメルカプタン
を7ppm含む臭気を上記各装置で脱臭処理を行った。
その結果、実施形態の装置では、第2段目の脱臭槽で排
気されたガスの成分を分析したところ、アンモニア濃度
は<0.1ppm、硫化水素濃度は<0.01ppm、
メチルメルカプタン濃度は<0.01ppmとなった。
一方、従来装置では、排気ガスのアンモニア濃度は1p
pm、硫化水素濃度は0.1ppm、メチルメルカプタ
ン濃度は0.1ppmであった。この結果から、アンモ
ニアを第1段目の脱臭槽で処理することにより、アンモ
ニアおよびその他の臭気が効率的に処理されることが明
らかとなった。
EXAMPLE In order to evaluate the performance of the deodorizing apparatus of the above embodiment, a single-stage deodorizing apparatus having only one deodorizing tank having substantially the same capacity as the total capacity of the first and second deodorizing tanks. Is prepared as a conventional example, and 30
An odor containing 0 ppm, 10 ppm of hydrogen sulfide, and 7 ppm of methyl mercaptan was deodorized by each of the above apparatuses.
As a result, in the apparatus of the embodiment, when the components of the gas exhausted in the second-stage deodorization tank were analyzed, the ammonia concentration was <0.1 ppm, the hydrogen sulfide concentration was <0.01 ppm,
The methyl mercaptan concentration was <0.01 ppm.
On the other hand, in the conventional device, the ammonia concentration of the exhaust gas is 1 p.
pm, the concentration of hydrogen sulfide was 0.1 ppm, and the concentration of methyl mercaptan was 0.1 ppm. From this result, it became clear that ammonia and other odors were efficiently treated by treating ammonia in the first-stage deodorizing tank.

【0017】[0017]

【発明の効果】以上説明したように本発明の脱臭装置に
よれば、脱臭槽を複数設けるとともに、前段の脱臭槽の
排気を後段の脱臭槽に取り入れるように脱臭槽同士を直
列に接続し、さらに、第1段目の脱臭槽を、アンモニア
ガスの脱臭に割り当て、後段の脱臭槽を、その他の臭気
の脱臭に割り当てたので、第1段目の脱臭槽でアンモニ
アの処理が効率的になされ、第2段目以降でその他の臭
気成分の処理が効率的になされるので、複合臭気におい
ても効率的な脱臭処理が可能になる。
As described above, according to the deodorizing apparatus of the present invention, a plurality of deodorizing tanks are provided, and the deodorizing tanks are connected in series so that the exhaust gas of the former deodorizing tank is taken into the latter. Further, the first-stage deodorization tank is assigned to deodorize ammonia gas, and the second-stage deodorization tank is assigned to deodorization of other odors. Thus, ammonia is efficiently treated in the first-stage deodorization tank. Since the other odor components are efficiently treated in the second and subsequent stages, efficient deodorization can be performed even for complex odors.

【0018】また、前記担体に散水する散水装置と、散
水した水を脱臭槽から回収して再度散水に供するように
貯水する貯水タンクとをそれぞれ複数設け、少なくとも
最前段の脱臭槽には専用の散水装置と貯水タンクとを割
り当てれば、回収した水を他の脱臭槽に散水することに
よって悪影響が生じることを避けられ、脱臭を一層効率
的に行うことができる。さらに、第1段目の脱臭槽に硝
化細菌を付着させ、後段の脱臭槽にはその他の臭気を処
理する細菌を付着させれば、各脱臭槽の機能を最大限に
機能させて目的となる臭気をより効率的に処理すること
が可能になる。
A plurality of sprinklers for sprinkling water on the carrier and a plurality of water tanks for collecting sprinkled water from the deodorizing tank and storing the sprinkled water again for watering are provided. By allocating the water sprinkler and the water storage tank, it is possible to avoid the adverse effect caused by spraying the collected water to another deodorization tank, and it is possible to perform deodorization more efficiently. Furthermore, if nitrifying bacteria are attached to the first-stage deodorizing tank, and bacteria for treating other odors are attached to the second-stage deodorizing tank, the function of each deodorizing tank can be maximized to achieve the purpose. The odor can be more efficiently treated.

【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.

【図2】 同じく、従来の脱臭装置を示す概略図であ
る。
FIG. 2 is a schematic view showing a conventional deodorizing apparatus.

【符号の説明】[Explanation of symbols]

1 脱臭槽 2 臭気導入管 3 担体 5 戻り管 6 貯水タンク 7 ポンプ 7a 揚水管 8a 散水管 8 散水部 11 脱臭槽 12 臭気導入管 13 担体 15 戻り管 16 貯水タンク 17 ポンプ 17a 揚水管 18a 散水管 18 散水部 20 微生物 20a 硝化細菌 20b その他の細菌 DESCRIPTION OF SYMBOLS 1 Deodorizing tank 2 Odor introduction pipe 3 Carrier 5 Return pipe 6 Water storage tank 7 Pump 7a Pumping pipe 8a Sprinkling pipe 8 Sprinkling part 11 Deodorizing tank 12 Odor introduction pipe 13 Carrier 15 Return pipe 16 Water storage tank 17 Pump 17a Pumping pipe 18a Sprinkling pipe Watering part 20 Microorganism 20a Nitrifying bacteria 20b Other bacteria

フロントページの続き (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Continuation of front page (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】 微生物と該微生物を担持する担体とを収
納して、アンモニアガスを含む臭気を内部に取り入れて
前記微生物により脱臭した後、外部に排気する脱臭槽を
備えた微生物脱臭装置において、前記脱臭槽を複数有し
ているとともに、脱臭槽同士は、前段の脱臭槽の排気を
後段の脱臭槽に取り入れるように直列に接続されてお
り、さらに、第1段目の脱臭槽は、アンモニアガスの脱
臭に割り当てられており、後段の脱臭槽は、その他の臭
気の脱臭に割り当てられていることを特徴とする微生物
脱臭装置
1. A microorganism deodorizing apparatus comprising a deodorizing tank containing a microorganism and a carrier carrying the microorganism, taking in an odor including ammonia gas therein, deodorizing the microorganism, and exhausting the odor to the outside. In addition to having a plurality of the deodorizing tanks, the deodorizing tanks are connected in series so that the exhaust gas from the preceding deodorizing tank is taken into the subsequent deodorizing tank. A microbial deodorizer characterized by being assigned to gas deodorization, and a subsequent deodorization tank being assigned to deodorization of other odors.
【請求項2】 前記担体に散水する散水設備と、散水し
た水を脱臭槽から回収して再度散水に供するように貯水
する貯水タンクとをそれぞれ複数備えており、少なくと
も最前段の脱臭槽には専用の散水設備と貯水タンクとが
割り当てられており、該専用の貯水タンクおよび散水設
備では、第1段目の脱臭槽との間でのみ散水された水の
回収と散水とが行われることを特徴とする請求項1記載
の微生物脱臭装置
2. A water spraying facility for sprinkling water on the carrier, and a plurality of water storage tanks for collecting the sprinkled water from the deodorization tank and storing the water for re-sprinkling, are provided in at least the first stage deodorization tank. A dedicated sprinkling facility and a water storage tank are allocated, and the dedicated water storage tank and the sprinkling facility ensure that the water collected and sprinkled only with the first-stage deodorizing tank is collected and sprinkled. The microorganism deodorizing device according to claim 1, characterized in that:
【請求項3】 第1段目の脱臭槽に硝化細菌が付着さ
れ、後段の脱臭槽にはその他の臭気を処理する細菌が付
着されていることを特徴とする請求項1または2に記載
の微生物脱臭装置
3. The method according to claim 1, wherein nitrifying bacteria are attached to the first-stage deodorizing tank, and bacteria for treating other odors are attached to the second-stage deodorizing tank. Microbial deodorizer
JP9354204A 1997-12-08 1997-12-08 Microbial deodorization apparatus Pending JPH11169649A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP9354204A JPH11169649A (en) 1997-12-08 1997-12-08 Microbial deodorization apparatus

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP9354204A JPH11169649A (en) 1997-12-08 1997-12-08 Microbial deodorization apparatus

Publications (1)

Publication Number Publication Date
JPH11169649A true JPH11169649A (en) 1999-06-29

Family

ID=18435989

Family Applications (1)

Application Number Title Priority Date Filing Date
JP9354204A Pending JPH11169649A (en) 1997-12-08 1997-12-08 Microbial deodorization apparatus

Country Status (1)

Country Link
JP (1) JPH11169649A (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20010067159A (en) * 1999-09-06 2001-07-12 마에다 시게루 Process and apparatus for treating exhaust gases containing nitrides
JP2011520610A (en) * 2008-05-20 2011-07-21 玉川大学 農学部 Purification and deodorization methods for malodorous and odorous gas substances originating in structures related to biological production

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20010067159A (en) * 1999-09-06 2001-07-12 마에다 시게루 Process and apparatus for treating exhaust gases containing nitrides
JP2011520610A (en) * 2008-05-20 2011-07-21 玉川大学 農学部 Purification and deodorization methods for malodorous and odorous gas substances originating in structures related to biological production

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