JPS60209227A - Deodorization of discarded gas - Google Patents

Deodorization of discarded gas

Info

Publication number
JPS60209227A
JPS60209227A JP59063809A JP6380984A JPS60209227A JP S60209227 A JPS60209227 A JP S60209227A JP 59063809 A JP59063809 A JP 59063809A JP 6380984 A JP6380984 A JP 6380984A JP S60209227 A JPS60209227 A JP S60209227A
Authority
JP
Japan
Prior art keywords
soil
water
waste gas
deodorizing
deodorization
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
JP59063809A
Other languages
Japanese (ja)
Inventor
Shigeo Murakami
村上 茂雄
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.)
Toyota Motor Corp
Original Assignee
Toyota Motor Corp
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 Toyota Motor Corp filed Critical Toyota Motor Corp
Priority to JP59063809A priority Critical patent/JPS60209227A/en
Publication of JPS60209227A publication Critical patent/JPS60209227A/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

Landscapes

  • Treating Waste Gases (AREA)

Abstract

PURPOSE:To arrange a soil deodorization method to be utilizable to discarded gases from several kinds of production process and to reduce deodorization cost by providing a discarded gas introducing chamber to the bottom side of a deodorization tank filled with soil and providing a sprinkling pipe to the discarded gas introducing chamber and the top of the soil layer. CONSTITUTION:Discarded gas generated in several production processes such as casting process is introduced into a discarded gas introducing chamber 5, led further to a main body 1 of a deodorization tank through holes 2a provided to a plate 2, deodorizing in the soil 4 and then dispersed to the outside from the top of the deodorization tank main body 1. Rain water flows through the soil 4 and stored in a water storage chamber 7. The water content of the soil is sensed by a water content sensor 14, and a pump 10 is driven by a controller 16 to spray the water in the water storage chamber 7 into the discarded gas introducing chamber 5 from the sprinkling pipe 8. The water level in the water storage chamber 7 is monitored with a water level meter 15. When the amt. of the water in the water storage chamber is defficient and the water content in the soil is sensed to be insufficient by the water content meter 14, a solenoid valve 13 is opened by the controller 16, and industrial water is sprayed on the soil 4 through the sprinkling pipe 11.

Description

【発明の詳細な説明】 技術分野 この発明は鋳造工程その他の各種生産工程で生じた廃棄
対象となるガスの脱臭を行なうための廃棄ガス脱臭装置
に関するものである。
DETAILED DESCRIPTION OF THE INVENTION Technical Field The present invention relates to a waste gas deodorizing apparatus for deodorizing gas to be disposed of, which is generated in a casting process and other various production processes.

従来技術 各種生産設備例えば鋳造工程では、フェノール、アンモ
ニア、ホルムアルデヒド等を成分とし、悪臭を有するガ
スが不可避的に生成される。そのようなガスを廃棄する
べくそのまま大気中に放散すると、臭気による悪影響が
著しく、そこで廃棄にあたっては事前に脱臭処理を施す
必要がある。
BACKGROUND OF THE INVENTION In various production facilities such as casting processes, gas containing phenol, ammonia, formaldehyde, etc. and having a bad odor is inevitably produced. If such a gas is released into the atmosphere as it is for disposal, the bad odor will be significant, so it is necessary to perform deodorization treatment before disposal.

従来、生産工程で生じる廃棄ガスの脱臭処理には薬液洗
浄法が適用されていた。先ず、薬液洗浄法による脱臭処
理ではガスからの脱臭効率を向上するにはガスと脱臭液
との気液接触界面を広くする必要があり、その場合廃棄
ガス送給圧の圧力損失が増大してそれに伴い送風機の負
萄が増大し、結果としてランニングコストが増加すると
いう不都合がある。また、薬液洗浄法を行なう場合、脱
臭薬液調整用の薬品の保管・管理や脱臭液の濃度調整を
行なう作業が煩雑であるという欠点もあった。さらに大
きな問題として、薬液洗浄を行なう説臭装■からの排水
には多曇のNが窒素化合物等の形で含有され、その排水
を河川に放流した場合、河川の富栄養化という問題が生
じる。
Conventionally, chemical cleaning methods have been applied to deodorize waste gas generated during production processes. First, in deodorizing treatment using the chemical cleaning method, in order to improve the efficiency of deodorizing the gas, it is necessary to widen the gas-liquid contact interface between the gas and the deodorizing liquid, and in this case, the pressure loss of the waste gas supply pressure increases. As a result, the load on the blower increases, resulting in an increase in running costs. Furthermore, when using the chemical cleaning method, there is also the drawback that the work of storing and managing the chemicals for preparing the deodorizing chemical and adjusting the concentration of the deodorizing liquid is complicated. An even bigger problem is that the wastewater from the chemical cleaning system ■ contains a cloudy amount of N in the form of nitrogen compounds, and if this wastewater is discharged into rivers, it will cause the problem of eutrophication of the rivers. .

一方、薬液洗浄法以外の脱臭法には土壌脱臭法があり、
従来し尿処理場等の一部業種の雰囲気ガスの脱臭用に採
用されていた。そこで、その土壌脱臭法を鋳造工程その
他の各種生産工程゛における廃棄ガス脱臭に適用するこ
とが考えられる。しかし、一般に生産工程で生じる廃棄
ガスは乾燥している場合が多く、そのように乾燥(たガ
スの脱臭に土壌脱臭法を適用する場合、脱臭を行なう土
壌が乾燥して脱臭性能が低下するため、その点から生産
工程の廃棄ガス脱臭用に土壌脱臭法を適用することは困
難であった。
On the other hand, there is a soil deodorization method as a deodorization method other than the chemical cleaning method.
It has been used to deodorize atmospheric gas in some industries such as human waste treatment plants. Therefore, it is conceivable to apply the soil deodorization method to waste gas deodorization in casting processes and other various production processes. However, the waste gas generated in the production process is often dry, and when applying the soil deodorization method to deodorize such dry gas, the soil being deodorized becomes dry and the deodorizing performance decreases. From this point of view, it has been difficult to apply soil deodorization methods to deodorize waste gas in production processes.

発明の目的 この発明は以上の従来の事情に鑑みてなされたものであ
って、鋳造工程等の各積生産工程で生じる廃棄ガス脱臭
に土壌脱臭法を適用できるようにして、廃棄ガス脱臭の
コストの低減、作業の合理化を図り河川の富栄養化等の
外部に対する悪影響のない廃棄ガス脱臭装■を提供する
ことを目的とするものである。
Purpose of the Invention The present invention has been made in view of the above-mentioned conventional circumstances, and it is possible to apply the soil deodorization method to deodorize waste gas generated in each production process such as the casting process, thereby reducing the cost of waste gas deodorization. The purpose of this project is to provide a waste gas deodorizer that reduces waste gas emissions, streamlines work, and does not have negative effects on the outside world such as eutrophication of rivers.

発明の構成 すなわちこの発明の廃棄ガス脱臭装置は、頂部を開放し
たllI2臭槽本体の下側に、外部から廃棄ガスを導入
するための廃棄ガス導入室を形成し、その廃棄ガス導入
室と脱臭槽本体との間に通気可能な支持部を設けて、そ
の支持部上の脱臭槽本体内に土壌を充填し、前記廃棄ガ
ス導入室内と土壌上方とに散水管を配設したことを特徴
とするものである。
The constitution of the invention, that is, the waste gas deodorizing device of the present invention is such that a waste gas introduction chamber for introducing waste gas from the outside is formed on the lower side of the llI2 odor tank body with the top open, and the waste gas introduction chamber and the deodorizing chamber are connected to each other. A ventilated support part is provided between the tank body and the deodorizing tank body on the support part is filled with soil, and a watering pipe is arranged in the waste gas introduction chamber and above the soil. It is something to do.

実施例 以下にこの発明の廃棄ガス脱臭装置の一実施例を第1図
を参照して説明する。
EXAMPLE An example of the waste gas deodorizing apparatus of the present invention will be described below with reference to FIG.

第1図に示すように、脱臭槽本体1は頂部が外部に開放
され、またその底部を形成するプレート2には小径の孔
2aが多数設けられている。そのプレート2上には孔2
aの径よりも径の大きな小石が多数積層されたガス均一
分散用の積層部3が設けられ、それ等のプレート2aと
積層部3とによって通気可能な支持部が形成されている
。その小石が多数11j層された積層部3の上には脱臭
用土壌4が充填され、その充填された脱臭用土壌4の上
面は外部に露出せしめられている。
As shown in FIG. 1, the top of the deodorizing tank body 1 is open to the outside, and a plate 2 forming the bottom thereof is provided with a large number of small-diameter holes 2a. There are holes 2 on the plate 2.
A laminated portion 3 for uniformly dispersing gas is provided, in which a large number of pebbles having a diameter larger than the diameter of a are laminated, and the plate 2a and the laminated portion 3 form a support portion that allows ventilation. Deodorizing soil 4 is filled on the layered portion 3 in which a large number of pebbles 11j are layered, and the upper surface of the filled deodorizing soil 4 is exposed to the outside.

上記プレート2aの下面に沿って、脱臭槽本体1の下側
にはガス導入室5が設けられ、そのガス導入室5には図
示しない鋳造工程で生じた廃棄ガスが送風機6によって
送給される。またそのガス導入v5の一側には、ガス導
入室5の底面より低位置に底面を有する貯水室7が形成
されている。
A gas introduction chamber 5 is provided below the deodorizing tank main body 1 along the lower surface of the plate 2a, and waste gas generated in the casting process (not shown) is supplied to the gas introduction chamber 5 by a blower 6. . Further, on one side of the gas introduction v5, a water storage chamber 7 having a bottom surface lower than the bottom surface of the gas introduction chamber 5 is formed.

さらにガス導入室5の内側には送風機6から貯水室7に
至る全長にわたり、散水管8が配設され、その散水管8
には一定間隔で散水孔9が設けられている。また、散水
管8の一端は貯水室7に配設されたポンプ10に接続さ
れ、このポンプ10によって汲み上げられる水が・散水
管8に供給される。
Furthermore, a water sprinkling pipe 8 is arranged inside the gas introduction chamber 5 over the entire length from the blower 6 to the water storage chamber 7.
Water holes 9 are provided at regular intervals. Further, one end of the water sprinkling pipe 8 is connected to a pump 10 disposed in the water storage chamber 7, and water pumped up by this pump 10 is supplied to the water sprinkling pipe 8.

一方、前記脱臭槽本体1内に充填された脱臭用土壌41
面の上方には、脱臭用土壌4に対し散水可能な位置関係
で、他の散水管11が設けられ、その散水管11には一
定間隔で散水孔12が設けられている。その散水管11
は電磁弁13を介して図示しない工業用水供給源に接続
されている。
On the other hand, the deodorizing soil 41 filled in the deodorizing tank main body 1
Another watering pipe 11 is provided above the surface in a positional relationship that allows watering to be applied to the deodorizing soil 4, and the watering pipe 11 is provided with watering holes 12 at regular intervals. The water pipe 11
is connected to an industrial water supply source (not shown) via a solenoid valve 13.

前記脱臭槽本体1内に充填された脱臭用土壌4に対して
は脱臭槽本体1の外部から周知の機構の水分計14の検
知体14aが差し込まれ、前記排ガス導入室5の一側に
設けられた貯水室7にはこれも周知の機構の水位計15
が配設されている。
A detection body 14a of a moisture meter 14 of a well-known mechanism is inserted into the deodorizing soil 4 filled in the deodorizing tank main body 1 from the outside of the deodorizing tank main body 1, and is installed on one side of the exhaust gas introduction chamber 5. In the water storage chamber 7, there is also a water level gauge 15 of a well-known mechanism.
is installed.

以上の水分計14および水位計15からは検知された水
分値もしくは水位値に応じた信号が制御装置16に出力
される。その制御装@16からは、水分計14および水
位計15からの入力信号に応じた信号が前記ポンプ10
および電磁弁13に出力され、ポンプ10および電磁弁
13は制御装置16からの入力信号に基づき作動する。
The moisture meter 14 and water level meter 15 described above output signals corresponding to the detected moisture value or water level value to the control device 16. The control device @16 sends signals corresponding to the input signals from the moisture meter 14 and the water level meter 15 to the pump 10.
and is output to the solenoid valve 13, and the pump 10 and the solenoid valve 13 operate based on the input signal from the control device 16.

なお、この実施例の排ガス用脱臭装置では脱臭槽本体1
は屋外に配置され、脱臭槽本体1内の土壌4に降雨時に
降り注ぐ雨水を遮ぎる遮蔽物は積極的に撤去される。
In addition, in the exhaust gas deodorizing device of this embodiment, the deodorizing tank body 1
is placed outdoors, and a shield that blocks rainwater that falls on the soil 4 in the deodorizing tank body 1 during rain is actively removed.

以上の実施例の廃棄ガス脱臭装置によれば、次のように
して廃棄ガスの脱臭が行なわれる。
According to the waste gas deodorizing apparatus of the above embodiment, waste gas is deodorized in the following manner.

図示しない鋳造工程で生じた廃棄ガスは、送風機4によ
って廃棄ガス導入室5に導入される。廃棄ガス導入室5
に導入された廃棄ガスは、脱臭槽本体1底部プレート2
の孔2aから脱臭槽本体1内に入る。脱臭槽本体1内に
入った廃棄ガスは積層部3で均一に分散して土壌4中に
侵入し、土壌4を通過して脱臭槽本体1上部から外部に
四散する。その過程で廃棄ガスのフェノール、アンモニ
ア、ホルムアルデヒド、クレゾール等の成分が土壌4を
形成する土粒に吸着し、あるいは土壌4が含有する水分
に吸収されて廃棄ガスは無臭化される。また、土壌4中
に残された各成分は土壌4中に極めて多数生息する微生
物によって分解されて浄化される。したがって以後継続
して廃棄ガスの脱臭が行なわれる。
Waste gas generated in a casting process (not shown) is introduced into a waste gas introduction chamber 5 by a blower 4. Waste gas introduction chamber 5
The waste gas introduced into the deodorizing tank main body 1 bottom plate 2
It enters the deodorizing tank main body 1 through the hole 2a. The waste gas that has entered the deodorizing tank main body 1 is uniformly dispersed in the laminated part 3, enters the soil 4, passes through the soil 4, and is dispersed from the upper part of the deodorizing tank main body 1 to the outside. In this process, components of the waste gas such as phenol, ammonia, formaldehyde, and cresol are adsorbed to the soil particles forming the soil 4 or absorbed by the moisture contained in the soil 4, and the waste gas is made odorless. Further, each component left in the soil 4 is decomposed and purified by microorganisms that inhabit the soil 4 in extremely large numbers. Therefore, the waste gas is continuously deodorized from then on.

しかし、土壌4の脱臭性能は土壌4の含水率により大き
く左右され、発明者が確認したところによると最適含水
率は30〜80%である。したがって、鋳造工程から送
給される乾燥した廃棄ガスの脱臭を長く継続して行なう
と土壌4の含水率が低下し、それに伴ない脱臭性能も低
下する。前述したようにこの実施例の廃棄ガス脱臭装置
は屋外に配置されており、土壌4の水分は降雨があると
きは雨水によって補充され得る。すなわち、降雨時には
その際の雨水が脱臭槽本体1の上部開口部から土壌4に
降りかかり、雨水は土壌4中を流下してプレート2の孔
2aから廃棄ガス導入室5内に流入し、廃棄ガス導入室
5の一側に設けられた貯水室7に貯留される。その過程
で土壌4には十分に水分が補われ、土壌4は良好な脱臭
性能を保持し、もしくは回復する。また、貯水室7に貯
留される雨水は、土壌4中を流下する過程で土壌4中に
未だ分解されずに残留するフェノール、アンモニア等の
廃棄ガスの悪臭成分を洗い流し、雨水自体はそれ等の成
分を含んだ状態となる。しかし、それ等の成分を含んだ
雨水は貯水室7に貯留されて後述するように再利用され
るから、外部に排出されることはなく、したがって外部
が汚染されることはない。
However, the deodorizing performance of the soil 4 is greatly influenced by the moisture content of the soil 4, and the inventor has confirmed that the optimum moisture content is 30 to 80%. Therefore, if the dry waste gas supplied from the casting process is continuously deodorized for a long time, the moisture content of the soil 4 will decrease, and the deodorization performance will also decrease accordingly. As mentioned above, the waste gas deodorizing device of this embodiment is placed outdoors, and the moisture in the soil 4 can be replenished by rainwater when it rains. That is, when it rains, the rainwater falls on the soil 4 from the upper opening of the deodorizing tank main body 1, the rainwater flows down through the soil 4, flows into the waste gas introduction chamber 5 through the hole 2a of the plate 2, and the waste gas is The water is stored in a water storage chamber 7 provided on one side of the introduction chamber 5. In this process, the soil 4 is sufficiently replenished with moisture, and the soil 4 maintains or recovers good deodorizing performance. In addition, the rainwater stored in the water storage chamber 7 washes away the foul-smelling components of waste gases such as phenol and ammonia that remain undecomposed in the soil 4 as it flows down the soil 4, and the rainwater itself washes away the foul-smelling components of waste gases such as phenol and ammonia that remain undecomposed in the soil 4. Contains ingredients. However, since rainwater containing these components is stored in the water storage chamber 7 and reused as described later, it is not discharged to the outside, and therefore the outside is not contaminated.

一方、以上のように降雨時の雨水によって土壌4に水分
を補充することができないときは、次のようにして土壌
4の含水率は11整される。
On the other hand, when the soil 4 cannot be replenished with water by rainwater as described above, the moisture content of the soil 4 is adjusted to 11 as follows.

前述したように脱臭槽本体1には水分計14が取付けら
れており、その水分計14で土fi44の含水率は常時
監視される。送風機6から廃棄ガスを送給し脱臭槽本体
1内の土壌4を通過させて脱臭処理を行なう間に土壌4
の含水率が一定以下になると水分計14に検知され、制
御l装置16の指令によりポンプ10が駆動し、散水管
8に貯水室7内に貯留された汚水が汲み上げられる。散
水管8に汲み上げられた汚水は散水孔9から廃棄ガス導
入室5内に散布され、それにより廃棄ガス導入室5から
脱臭槽本体1内に流入する廃棄ガスは加湿される。その
加湿された廃棄ガスが通過する結果、土壌4は所要の水
分を含有するに至る。
As mentioned above, the moisture meter 14 is attached to the deodorizing tank main body 1, and the moisture content of the soil fi 44 is constantly monitored by the moisture meter 14. The waste gas is fed from the blower 6 and passed through the soil 4 in the deodorizing tank main body 1 to deodorize the soil 4.
When the moisture content of water becomes below a certain level, it is detected by the moisture meter 14, and the pump 10 is driven by a command from the control device 16, and the waste water stored in the water storage chamber 7 is pumped up into the sprinkler pipe 8. The sewage pumped up into the water sprinkling pipe 8 is sprayed into the waste gas introduction chamber 5 through the water sprinkling hole 9, thereby humidifying the waste gas flowing into the deodorizing tank main body 1 from the waste gas introduction chamber 5. As a result of the passage of the humidified waste gas, the soil 4 ends up containing the required moisture.

以上のように貯水室7に貯留された水を汲み上げ、その
水による廃棄ガスに対する加湿が反復・継続して行なわ
れると、水分は脱臭槽本体11部から蒸発して徐々に失
われてゆくので、その過程で降雨がない場合、終には貯
水室7内に貯留される水が不足してしまう。前述したよ
うに、貯水室7には水位計15が取付けられ、貯水室7
内の水位は水位計15によって常時監視されている。し
たがって、上iするように貯水室7内の貯溜水が不足し
その水位が一定以下になると、水位計15から制御装置
16に信号が入り、加えて水分計14によって±114
の水分の不足が検知されているときは、制御装置l!1
6の指令に基づき電磁弁13が開き、図示しない工業用
水供給源から供給される工業用水が散水管11から土壌
4上に散水される。その結果土壌4は降雨時と同様に洗
浄され加湿される。
As described above, when the water stored in the water storage chamber 7 is pumped up and the waste gas is repeatedly and continuously humidified by the water, the water evaporates from the deodorizing tank main body 11 and is gradually lost. If there is no rain during this process, the water stored in the water storage chamber 7 will eventually become insufficient. As mentioned above, the water level gauge 15 is attached to the water storage chamber 7.
The water level inside is constantly monitored by a water level gauge 15. Therefore, when the stored water in the water storage chamber 7 becomes insufficient and the water level falls below a certain level as described above, a signal is sent from the water level meter 15 to the control device 16, and in addition, the moisture meter 14 sends a signal of ±114
When a lack of moisture is detected in the controller l! 1
Based on the command 6, the solenoid valve 13 opens, and industrial water supplied from an industrial water supply source (not shown) is sprinkled onto the soil 4 from the sprinkler pipe 11. As a result, the soil 4 is washed and moistened in the same way as when it rains.

以上の実施例の廃棄ガス脱臭装置の土壌4にアンモニア
除去に適合する土壌を用い、実際に鋳造工程からの廃棄
ガスの脱臭を行ない、アンモニアの除去率を測定した。
A soil suitable for removing ammonia was used as the soil 4 of the waste gas deodorizing apparatus of the above example, and waste gas from the casting process was actually deodorized, and the ammonia removal rate was measured.

その結果、従来の薬液洗浄法を適用した脱臭@置のアン
モニア除去率が85%程度だったのに対し、除去率95
%という良好な結果が得られた。
As a result, the removal rate of ammonia was 95%, compared to about 85% in deodorization using the conventional chemical cleaning method.
A good result of % was obtained.

発明の効果 以上のようにこの発明の廃棄ガス脱臭装置では、脱臭材
として土壌を用いるようにしたことによって、極めて良
好な脱臭性能が無理なく得られ、廃棄ガス脱臭のコスト
を低減することができる。また、土壌で脱臭するため薬
液を用いる場合のように過剰にNを含んだ排水が生じる
ようなことはなく、河川の富栄養化という問題が生じる
のを防止することができる。さらに土壌についてはその
保管・管理が比較的容易で、薬液を用いる場合のような
脱臭薬液の濃度調整という煩雑な作業が不要になるとい
う利点もある。
Effects of the Invention As described above, in the waste gas deodorizing device of the present invention, by using soil as the deodorizing material, extremely good deodorizing performance can be easily obtained, and the cost of waste gas deodorizing can be reduced. . Further, unlike when using a chemical solution to deodorize soil, wastewater containing excessive N is not produced, and the problem of eutrophication of rivers can be prevented. Furthermore, soil is relatively easy to store and manage, and there is also the advantage that the complicated work of adjusting the concentration of a deodorizing chemical solution, which is required when using a chemical solution, is not required.

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

第1図はこの発明の一実施例の廃棄ガス脱臭装置の概略
を示す模式図である。 1・・・脱臭槽本体、 2・・・プレート、 3・・・
積層部、4・・・土壌、 5・・・廃棄ガス導入室、 
6・・・送風機、7・・・貯水室、 8散水管、 10
・・・ポンプ、 11・・・散水管、 13・・・電磁
弁、 16・・・制mt装置。 出願人 トヨタ自動車株式会社 代理人 弁理士 豊 1)武 久 (ほか1名)
FIG. 1 is a schematic diagram showing an outline of a waste gas deodorizing apparatus according to an embodiment of the present invention. 1... Deodorizing tank body, 2... Plate, 3...
Laminated section, 4...Soil, 5...Waste gas introduction room,
6...Blower, 7...Water storage chamber, 8 Water sprinkler pipe, 10
...Pump, 11...Water pipe, 13...Solenoid valve, 16...Control mt device. Applicant Toyota Motor Corporation Representative Patent Attorney Yutaka 1) Hisashi Take (and 1 other person)

Claims (1)

【特許請求の範囲】[Claims] 頂部を開放した脱臭槽本体の下側に、外部から廃棄ガス
を導入するための廃棄ガス導入室を形成し、その廃棄ガ
ス導入室と脱臭槽本体との間に通気可能な支持部を設け
て、その支持部上の脱臭槽本体内に土壌を充填し、前記
廃棄ガス導入室内と土壌上方とに散水管を配設したこと
を特徴とする廃棄ガス脱臭装置。
A waste gas introduction chamber for introducing waste gas from the outside is formed on the lower side of the deodorizing tank main body with the top open, and a ventilable support part is provided between the waste gas introduction chamber and the deodorizing tank main body. A waste gas deodorizing device, characterized in that a deodorizing tank main body on the support portion thereof is filled with soil, and a watering pipe is arranged in the waste gas introduction chamber and above the soil.
JP59063809A 1984-03-31 1984-03-31 Deodorization of discarded gas Pending JPS60209227A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP59063809A JPS60209227A (en) 1984-03-31 1984-03-31 Deodorization of discarded gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP59063809A JPS60209227A (en) 1984-03-31 1984-03-31 Deodorization of discarded gas

Publications (1)

Publication Number Publication Date
JPS60209227A true JPS60209227A (en) 1985-10-21

Family

ID=13240068

Family Applications (1)

Application Number Title Priority Date Filing Date
JP59063809A Pending JPS60209227A (en) 1984-03-31 1984-03-31 Deodorization of discarded gas

Country Status (1)

Country Link
JP (1) JPS60209227A (en)

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