JP3490915B2 - Underwater decomposition type garbage processing equipment - Google Patents

Underwater decomposition type garbage processing equipment

Info

Publication number
JP3490915B2
JP3490915B2 JP31976998A JP31976998A JP3490915B2 JP 3490915 B2 JP3490915 B2 JP 3490915B2 JP 31976998 A JP31976998 A JP 31976998A JP 31976998 A JP31976998 A JP 31976998A JP 3490915 B2 JP3490915 B2 JP 3490915B2
Authority
JP
Japan
Prior art keywords
pipe
activated carbon
exhaust
decomposition tank
treated water
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.)
Expired - Fee Related
Application number
JP31976998A
Other languages
Japanese (ja)
Other versions
JP2000126723A (en
Inventor
潔 西村
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.)
ESU-TECH CO.,LTD.
Original Assignee
ESU-TECH CO.,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 ESU-TECH CO.,LTD. filed Critical ESU-TECH CO.,LTD.
Priority to JP31976998A priority Critical patent/JP3490915B2/en
Publication of JP2000126723A publication Critical patent/JP2000126723A/en
Application granted granted Critical
Publication of JP3490915B2 publication Critical patent/JP3490915B2/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
    • Y02WCLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
    • Y02W10/00Technologies for wastewater treatment
    • Y02W10/20Sludge processing

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】本発明は加熱活性炭脱臭器部
を底部に設けた水中分解式の生ゴミ処理装置に関するも
のである。
BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to an underwater decomposition type garbage disposal device having a heated activated carbon deodorizer unit at the bottom.

【0002】[0002]

【従来の技術】従来、分解槽内の温水中で曝気により好
気性微生物の活動を助長して生ゴミを分解し、その時発
生する多量の泡を処理する消泡気水分離器を天井蓋部に
設けた分解槽と、分解残留物を加熱して乾燥固形化する
蒸発固形化槽とこれらに付帯する消臭器等を設けた一連
の生ゴミ分解処理装置は既に開発されている(例えば特
許願平9−第356136号)。
2. Description of the Related Art Conventionally, a defoaming air / water separator that aerates aerial microorganisms in warm water in a decomposition tank to promote the activity of aerobic microorganisms to decompose garbage and to process a large amount of bubbles generated at that time A series of garbage decomposing devices equipped with a decomposing tank provided in the above, an evaporative solidifying tank for heating and solidifying the decomposed residue by drying, and a deodorizer attached to these have already been developed (for example, patents Japanese Patent Application No. 9-356136).

【0003】[0003]

【発明が解決しようとする課題】従来の水中分解式の生
ゴミ処理装置においては、分解槽内の温水中で曝気によ
り好気性微生物の活動を助長して生ゴミを分解する構成
上分解槽内で多量に発生する泡は、例えば図3に示す構
造の消泡気水分離器を採用し分解槽の天井部に取付けて
泡と排気とに分離し、排気は更に脱臭器中を通過させて
大気へ排出していた。しかしながら生ゴミ分解装置の脱
臭装置として活性炭を使用する場合、多量の蒸発水分が
排気空気中に含まれて脱臭装置に送り込まれているた
め、この水分が活性炭に吸着され極めて短時間で脱臭能
力が低下消失する問題点を有していた。
SUMMARY OF THE INVENTION In the conventional underwater decomposition type garbage disposal device, the decomposition of garbage is promoted by aeration in warm water in the decomposition tank to promote the activity of aerobic microorganisms. The foam generated in a large amount in step (3) adopts a defoaming air-water separator having the structure shown in Fig. 3 and is attached to the ceiling part of the decomposition tank to separate it into foam and exhaust gas, and the exhaust gas is further passed through the deodorizer. It was released to the atmosphere. However, when using activated carbon as a deodorizing device for a garbage decomposing device, a large amount of evaporated water is contained in the exhaust air and sent to the deodorizing device. It had a problem that it decreased and disappeared.

【0004】本発明はこれらの問題点に鑑み、蒸発水分
を多量に排気中に含む水中分解式の生ゴミ処理装置に採
用しても、脱臭能力が長時間維持することが可能な活性
炭を用いた水中分解式の生ゴミ処理装置を提供すること
を目的として発明されたものである。
In view of these problems, the present invention uses activated carbon capable of maintaining the deodorizing ability for a long time even when it is used in an underwater decomposition type garbage disposal device containing a large amount of evaporated water in the exhaust gas. The invention was invented for the purpose of providing an underwater decomposition type garbage treatment device.

【0005】[0005]

【課題を解決するための手段】水中分解式の生ゴミ処理
装置の処理水を張った処理水底面より下側位置の分解槽
の下半部内部に加熱用ヒーターで加熱する脱臭用活性炭
を充填し、脱臭用活性炭の内部に分解槽からの排気を導
入加熱し相対湿度を下げる与熱管と与熱管と連通し、前
記相対湿度の低下した排気を脱臭用活性炭中に流出する
脱臭器排気入口管と、前記脱臭用活性炭中に流出した排
気が進入して分解槽外へ排出する脱臭器排気出口管とを
設けて分解槽の下半部内部に加熱活性炭脱臭器部を形成
する。
[Means for Solving the Problems] Activated carbon for deodorization, which is heated by a heating heater, is filled in the lower half of the decomposition tank located below the bottom surface of the treated water filled with the treated water of an underwater decomposition type garbage treatment device. The exhaust gas from the decomposition tank is introduced into the activated carbon for deodorization, and the heating pipe for heating and lowering the relative humidity is connected to the heating pipe and the heating pipe, and the exhaust gas with the decreased relative humidity is discharged into the activated carbon for deodorization. And a deodorizer exhaust outlet pipe through which the exhaust gas that has flowed into the deodorizing activated carbon enters and discharges to the outside of the decomposition tank to form a heated activated carbon deodorizing unit inside the lower half of the decomposition tank.

【0006】[0006]

【発明の実施の形態】以下本発明を図面に基づいて説明
すると、図1及び図2において1は水中分解式の分解槽
で、分解槽1の下半部の内側に処理水底面2を縦断面略
V字形状に形成して処理水底面2上に処理水3を注水す
る。脱臭用活性炭4は、処理水底面2の下側位置の分解
槽1の内部に充填する。さらに詳しくは、脱臭用活性炭
4は分解槽1の下半部側壁に設けた脱臭用活性炭充填口
イから充填するようにするとよい。脱臭器排気入口管5
は、例えば内側が中空の鋼管を用い、中空部の両端部を
閉塞して周面に内側の中空部に貫通する排気噴出穴6,
6,…を穿孔して処理水底面2下の脱臭用活性炭4内に
横方向に埋設する。与熱管7は、例えば銅管で形成し一
端部を前記脱臭器排気入口管5の一端部分に内部の中空
部と連通せしめて取付け、U字形に曲げて脱臭用活性炭
4内に埋設してから他の一端部を分解槽1外へ導出し分
解槽1の天井部に取付けた気水分離器8の排気出口9に
連通して一次側排気管10で配管する。脱臭器排気出口
管11は、例えば内側が中空の鋼管を用い、中空部の両
端部を閉塞して、周面に内側の中空部に貫通する排気進
入穴12,12,…を穿設し脱臭器排気入口管5と略平
行に脱臭用活性炭4内に横方向に埋設した状態で、例え
ば一端部を分解槽1の内面13に取付け固定する。さら
に詳しくは、前記分解槽1の下半部に充填した加熱する
脱臭用活性炭中に埋設した与熱管7と脱臭器排気入口管
5と脱臭器排気出口管11とで加熱活性炭脱臭器部Kを
分解槽1の下半部に形成することを特徴とする。二次側
排気管14は一端部を脱臭器排気出口管11の一端部に
内部の中空部と連通せしめて取付け、ドレン15を介し
て他の一端側を分解槽1外へ導出して配管する。加熱ヒ
ーター16は分解槽1の底面17に取付け、底面17か
ら加熱して、前記脱臭用活性炭4、与熱管7、脱臭器排
気入口管5、処理水3等を順次加熱する。循環水用水中
ポンプ18は処理水3内に配置し、水面19上に設置し
た循環水噴射管20に通水管21を配管して接続する。
ターボファン22は循環水噴射管20から噴き上げる噴
霧水23の高さ位置の分解槽1の側壁に設けた吹込み口
24内にエアーを吹込むように設ける。生ゴミ投入部2
5は、例えば底部に傾斜面を有するホッパー形に形成
し、下部には破砕ディスポーザー26を設けて生ゴミ送
給管27を配管して分解槽1の処理水3内と連通せしめ
て生ゴミを処理水3内に供給する。サイクロン残留物分
離器28は分解槽1の外側に設けられており、例えば図
4に示す如く筒胴29の上下端部には、各々低比重取出
し管30と重比重取出し管31を設け、筒胴29の全高
の略中央位置に処理水導入管32を設けて分解槽1内の
通水管21と処理水通水管33を配管して接続する。分
離水取出し筒34は、上端部には筒胴29より突出する
戻り管35を形成し、下端側はL字形に折り曲げて処理
水導入管32の上側位置に開口した分離水取水口36を
形成して戻り管35には、分解槽1内と連通する処理水
返送管37を配管する。残留物乾燥固形化槽38は、例
えば槽内に残留物取出し枠39を設け、底部には加熱ヒ
ーター40を設けて周囲は保温材41を巻繞し、前記サ
イクロン残留物分離器28の重比重取出し管31部と重
比重液送給管42を配管して接続し、重比重液を残留物
乾燥固形化槽38内に取込み乾燥固形化させて取出す。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention will be described below with reference to the drawings. In FIG. 1 and FIG. 2, 1 is an underwater decomposition type decomposition tank, and a treated water bottom surface 2 is longitudinally cut inside the lower half of the decomposition tank 1. The treated water 3 is poured onto the treated water bottom surface 2 by forming the surface into a substantially V-shape. The deodorizing activated carbon 4 is filled inside the decomposition tank 1 below the treated water bottom surface 2. More specifically, the deodorizing activated carbon 4 may be filled from the deodorizing activated carbon filling port a provided on the lower half side wall of the decomposition tank 1. Deodorizer exhaust inlet pipe 5
Is, for example, a steel pipe having a hollow inside, and both ends of the hollow portion are closed to exhaust gas exhaust holes 6, which penetrate the inner hollow portion at the peripheral surface.
6 are perforated and embedded laterally in the deodorizing activated carbon 4 below the bottom surface 2 of the treated water. The heating pipe 7 is formed of, for example, a copper pipe, and one end of the heating pipe 7 is attached to one end of the deodorizer exhaust inlet pipe 5 so as to communicate with the internal hollow portion, and is bent into a U shape and embedded in the deodorizing activated carbon 4 The other end is led out of the decomposition tank 1 and communicated with the exhaust outlet 9 of the steam separator 8 attached to the ceiling of the decomposition tank 1, and is connected by the primary exhaust pipe 10. As the deodorizer exhaust outlet pipe 11, for example, a hollow steel pipe is used, both ends of the hollow portion are closed, and exhaust inlet holes 12, 12, ... Penetrating to the inner hollow portion are formed in the peripheral surface to deodorize. For example, one end is attached and fixed to the inner surface 13 of the decomposition tank 1 in a state of being embedded laterally in the deodorizing activated carbon 4 substantially in parallel with the equipment exhaust inlet pipe 5. More specifically, the heating activated carbon deodorizer section K is formed by the heating pipe 7, the deodorizer exhaust inlet pipe 5, and the deodorizer exhaust outlet pipe 11 embedded in the heated deodorizing activated carbon filled in the lower half of the decomposition tank 1. It is characterized in that it is formed in the lower half of the decomposition tank 1. One end of the secondary side exhaust pipe 14 is attached to one end of the deodorizer exhaust outlet pipe 11 so as to communicate with the internal hollow portion, and the other end side is led out to the outside of the decomposition tank 1 through the drain 15 for piping. . The heater 16 is attached to the bottom surface 17 of the decomposition tank 1, and is heated from the bottom surface 17 to sequentially heat the deodorizing activated carbon 4, the heating pipe 7, the deodorizer exhaust inlet pipe 5, the treated water 3 and the like. The submersible pump 18 for circulating water is arranged in the treated water 3, and a circulating pipe 21 is connected to a circulating water jet pipe 20 installed on the water surface 19.
The turbo fan 22 is provided so as to blow air into a blow-in port 24 provided on a side wall of the decomposition tank 1 at a height position of the spray water 23 jetted from the circulating water jet pipe 20. Garbage dumper 2
5 is formed, for example, in a hopper shape having an inclined surface at the bottom, and provided with a crushing disposer 26 at the bottom and a raw garbage feed pipe 27 is connected to communicate with the inside of the treated water 3 of the decomposition tank 1 to remove the raw garbage. It is supplied into the treated water 3. The cyclone residue separator 28 is provided outside the decomposition tank 1. For example, as shown in FIG. 4, a low specific gravity take-out pipe 30 and a heavy specific gravity take-out pipe 31 are provided at the upper and lower ends of a barrel 29, respectively. A treated water introduction pipe 32 is provided at a substantially central position of the entire height of the body 29, and the water pipe 21 and the treated water pipe 33 in the decomposition tank 1 are connected by piping. The separated water take-out pipe 34 has a return pipe 35 protruding from the barrel 29 at the upper end and a separated water intake port 36 opened at the upper position of the treated water introducing pipe 32 by being bent into an L shape at the lower end. Then, a treated water return pipe 37 communicating with the inside of the decomposition tank 1 is connected to the return pipe 35. The residue drying and solidifying tank 38 is provided with, for example, a residue take-out frame 39 in the tank, a heater 40 at the bottom, and a heat insulating material 41 wound around the residue, and the cyclone residue separator 28 has a specific gravity. The take-out pipe 31 part and the heavy-gravity liquid feed pipe 42 are connected by piping, and the heavy-gravity liquid is taken into the residue dry solidification tank 38, dried and solidified, and taken out.

【0007】[0007]

【実施例】脱臭器排気入口管5及び脱臭器排気出口管1
1は、実施例では各1本が図示されているが複数本使用
してもよいことは勿論である。さらに、パンチングプレ
ートで形成した循環水落下緩衝板43を循環水噴射管2
0と水面19間に設けると循環水の落下力が緩衝されて
水面19からの水滴の飛び散りを防止でき噴霧水23の
微細粒環境が損なわれることがない。また、排気に残存
する熱量を有効に利用するために、排気熱回収交換器4
4を形成して排気管14から分解槽1内に取込むか、或
はターボファン22の空気吸込み側に設けた排気熱回収
交換器44′の排気入口45に二次側排気管14からの
排気を送給してターボファン22からの吹込み空気の加
熱に利用してもよい。
[Example] Deodorizer exhaust inlet pipe 5 and deodorizer exhaust outlet pipe 1
In the embodiment, one is shown for each one, but it is a matter of course that a plurality may be used. Further, the circulating water drop buffer plate 43 formed of a punching plate is attached to the circulating water jet pipe 2
If it is provided between 0 and the water surface 19, the drop force of the circulating water is buffered, water droplets can be prevented from scattering from the water surface 19, and the fine particle environment of the spray water 23 is not impaired. In addition, in order to effectively use the amount of heat remaining in the exhaust gas, the exhaust heat recovery exchanger 4
4 to take in from the exhaust pipe 14 into the decomposition tank 1 or to the exhaust inlet 45 of the exhaust heat recovery exchanger 44 'provided on the air intake side of the turbofan 22 from the secondary side exhaust pipe 14. Exhaust gas may be sent to be used for heating the air blown from the turbo fan 22.

【0008】次に本発明の作用に就いて述べると、処理
水3は循環水用水中ポンプ18により上方に揚水され循
環水噴射管20より噴霧水23となって噴射されこの噴
霧水23に向かって側方からターボファン22で圧搾空
気を吹き付けと噴霧水23の吹き上げ時と落下時に前記
送り込まれた空気と接触し、多量に酸素を含んだ噴霧水
23は水面19上に落下して処理水3となり、好気性バ
クテリアの増殖、分解作用に必要な十分な酸素を含んだ
処理水を得ることができ、生ゴミ投入部25内に投入さ
れた生ゴミは破砕ディスポーザー26で破砕されて生ゴ
ミ送給管27を通り処理水3内に送り込まれて分解され
る。次に処理水3は好気性バクテリアの増殖、分解作用
を行なうために多量の泡を発生し、多量の泡を含んだ排
気は気水分離器8に到達し、回転する回転羽根46で泡
は吹き飛ばされて排気のみが排気出口9から外に出て一
次側排気管10を通って与熱管7側へ向かうが、此の場
合気水分離器8から出た排気は高湿度(一例、温度35
℃、湿度95%)であるが、与熱管7中を通過する間に
与熱管7が加熱ヒーター16により加熱されている脱臭
用活性炭4中を蛇行通過する構成となっているため、排
気は与熱管7中で35℃より43℃程度迄加熱され、相
対湿度は60%となる。さらに詳しくは、此の場合脱臭
用活性炭4は加熱ヒーター16により温度50℃、湿度
40%に設定することが好ましい。次に上記加熱により
相対湿度が60%に低下した排気は与熱管7より脱臭器
排気入口管5に進入し、脱臭器排気入口管5の排気噴出
穴6,6,…より一斉に脱臭用活性炭4中に噴出し、噴
き出された排気は下部に向かって脱臭しながら流れ、更
に相対湿度を低くしつゝ脱臭器排気出口管11へと流れ
て排気進入穴12より脱臭器排気出口管11内に進入
し、二次側排気管14を通って分解槽1外へと排出され
る。また、処理水3内の分解残留物は処理水と共に処理
水通水管33からサイクロン残留物分離器28中に送給
し、サイクロン残留物分離器28で分離された重比重の
処理水は重比重取出し管31から出て重比重液送給管4
2を通って残留物乾燥固形化槽38に入り加熱ヒーター
40により加熱され固形化して外に出す。さらに処理水
3内に没入して設けた排気熱回収交換器44に二次排気
管14から排気を導入すると処理水3の加熱に寄与し排
熱の回収が計れる。また、二次排気管14の排気をター
ボファン22の吸込み側に設けた排気熱回収交換器4
4′の排気入口45側に送給してターボファン22から
の吹込み空気の温度を高めても排熱の回収が計れる。
Next, the operation of the present invention will be described. Treated water 3 is pumped upward by a circulating water submersible pump 18 and sprayed as circulating water 23 from a circulating water injection pipe 20 toward the spraying water 23. When the compressed air is blown from the side by the turbo fan 22 and the sprayed water 23 is blown up and dropped, the sprayed water 23 comes into contact with the sent air, and the sprayed water 23 containing a large amount of oxygen falls on the water surface 19 to be treated water. 3, the treated water containing sufficient oxygen necessary for the growth and decomposition of aerobic bacteria can be obtained. It is sent into the treated water 3 through the feed pipe 27 and decomposed. Next, the treated water 3 produces a large amount of bubbles in order to grow and decompose aerobic bacteria, the exhaust containing the large amount of bubbles reaches the steam separator 8, and the bubbles are generated by the rotating rotary blades 46. Only the exhaust gas blown away goes out from the exhaust gas outlet 9 and goes toward the heating pipe 7 side through the primary side exhaust pipe 10. In this case, the exhaust gas from the steam separator 8 has high humidity (for example, a temperature of 35
Although the temperature is 95 ° C. and the humidity is 95%), the heating pipe 7 meanders through the deodorizing activated carbon 4 heated by the heater 16 while passing through the heating pipe 7, so that the exhaust gas is not emitted. It is heated from 35 ° C. to about 43 ° C. in the heat tube 7, and the relative humidity becomes 60%. More specifically, in this case, the deodorizing activated carbon 4 is preferably set to a temperature of 50 ° C. and a humidity of 40% by the heater 16. Next, the exhaust gas whose relative humidity has dropped to 60% by the above heating enters the deodorizer exhaust inlet pipe 5 through the heating pipe 7, and is simultaneously discharged from the exhaust outlet holes 6, 6, ... of the deodorizer exhaust inlet pipe 5. 4, the exhaust gas flowing out flows toward the lower part while deodorizing, and further lowers the relative humidity to flow to the deodorizer exhaust outlet pipe 11 and from the exhaust inlet hole 12 to the deodorizer exhaust outlet pipe 11 It enters the inside and is discharged to the outside of the decomposition tank 1 through the secondary side exhaust pipe 14. Further, the decomposition residue in the treated water 3 is sent together with the treated water from the treated water passage pipe 33 into the cyclone residue separator 28, and the treated water of the specific gravity separated by the cyclone residue separator 28 has a specific gravity. Out of the take-out pipe 31, the heavy-gravity liquid feed pipe 4
After passing through 2, the residue drying and solidifying tank 38 enters into the residue drying and solidifying tank 38, which is heated by a heater 40 to be solidified and discharged. Further, when exhaust gas is introduced from the secondary exhaust pipe 14 into the exhaust heat recovery exchanger 44 that is provided so as to be immersed in the treated water 3, it contributes to the heating of the treated water 3 and the exhaust heat can be recovered. Further, the exhaust heat recovery exchanger 4 in which the exhaust gas of the secondary exhaust pipe 14 is provided on the suction side of the turbo fan 22.
Exhaust heat can be recovered even if the temperature of the air blown from the turbofan 22 is increased by feeding it to the exhaust inlet 45 side of 4 '.

【0009】[0009]

【発明の効果】以上説明したように本発明は分解槽の下
半部に内蔵した加熱脱臭用活性炭中の与熱管内を通過さ
せて排気を温度上昇により相対湿度を低くしてから脱臭
用活性炭中に送り込み脱臭を行なうため、活性炭の水分
吸着量が抑制され急激な脱臭能力の低下が防止できて脱
臭能力を長時間維持することができ、また、残存排気熱
も有効に利用することが可能である。
As described above, according to the present invention, the deodorized activated carbon is passed through the heating pipe of the activated deodorizing activated carbon contained in the lower half of the decomposition tank to lower the relative humidity of the exhaust gas by increasing the temperature and then the deodorizing activated carbon. Since it is sent into the interior for deodorization, the amount of water adsorbed by activated carbon is suppressed, and it is possible to prevent a rapid decrease in deodorization ability, and to maintain the deodorization ability for a long time, and it is also possible to effectively use the residual exhaust heat Is.

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

【図1】水中分解式の生ゴミ処理装置の分解槽周辺の一
例を示す正面図である。
FIG. 1 is a front view showing an example of the periphery of a decomposition tank of an underwater decomposition type garbage treatment device.

【図2】水中分解式の生ゴミ処理装置のシステムの全容
の一例を示す図である。
FIG. 2 is a diagram showing an example of the entire system of an underwater decomposition type garbage treatment device.

【図3】気水分離器の一例を示す縦断面図である。FIG. 3 is a vertical cross-sectional view showing an example of a steam separator.

【図4】サイクロン残留物分離器の一例を示す縦断面図
である。
FIG. 4 is a vertical sectional view showing an example of a cyclone residue separator.

【符号の説明】[Explanation of symbols]

1 分解槽 2 処理水底面 3 処理水 4 脱臭用活性炭 5 脱臭器排気入口管 7 与熱管 8 気水分離器 11 脱臭器排気出口管 14 二次側排気管 16 加熱ヒーター 17 底面 18 循環水用水中ポンプ 19 水面 20 循環水噴射管 22 ターボファン 23 噴霧水 25 生ゴミ投入部 28 サイクロン残留物分離器 30 低比重取出し管 31 重比重取出し管 32 処理水導入管 38 残留物乾燥固形化槽 40 加熱ヒーター 43 循環水落下緩衝板 44 排気熱回収交換器 46 回転羽根 1 decomposition tank 2 Treated water bottom 3 treated water 4 Activated carbon for deodorization 5 Deodorizer exhaust inlet pipe 7 Heating tube 8 steam separator 11 Deodorizer exhaust outlet pipe 14 Secondary side exhaust pipe 16 heating heater 17 Bottom 18 Submersible pump for circulating water 19 Water surface 20 Circulating water injection pipe 22 turbo fan 23 Spray water 25 Raw Garbage Disposal Department 28 Cyclone residue separator 30 Low specific gravity extraction pipe 31 Gravity specific gravity extraction pipe 32 Treated water inlet pipe 38 Residue dry solidification tank 40 heating heater 43 Circulating water drop buffer plate 44 Exhaust heat recovery exchanger 46 rotating blades

───────────────────────────────────────────────────── フロントページの続き (58)調査した分野(Int.Cl.7,DB名) B09B 3/00 C02F 11/02 ─────────────────────────────────────────────────── ─── Continuation of the front page (58) Fields surveyed (Int.Cl. 7 , DB name) B09B 3/00 C02F 11/02

Claims (3)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 好気性微生物による水中分解式の生ゴミ
処理装置において、処理水を入れた処理水底面より下側
位置の分解槽の下半部内部に加熱用ヒーターで加熱する
脱臭用活性炭を充填し、脱臭用活性炭の内部に分解槽か
らの排気を導入加熱し相対湿度を下げる与熱管と、与熱
管と連通し前記相対湿度の低下した排気を脱臭用活性炭
中に流出する脱臭器排気入口管と、前記脱臭用活性炭中
に流出した排気が進入して分解槽外へ排出する脱臭器排
気出口管とを設けて分解槽の下半部内部に加熱活性炭脱
臭器部を形成したことを特徴とする水中分解式の生ゴミ
処理装置。
1. In an underwater decomposition type garbage treatment device using aerobic microorganisms, deodorizing activated carbon heated by a heater is placed inside the lower half of the decomposition tank located below the bottom of the treated water containing the treated water. Introduce exhaust gas from the decomposition tank into the activated carbon for deodorization and heat the heating pipe to lower the relative humidity by heating, and communicate with the heating pipe to discharge the exhaust gas with reduced relative humidity into the activated carbon for deodorization. It is characterized in that the heating activated carbon deodorizer section is formed inside the lower half of the decomposition tank by providing a pipe and a deodorizer exhaust outlet pipe through which the exhaust gas flowing out into the deodorizing activated carbon enters and discharges to the outside of the decomposition tank. Underwater decomposition type food waste treatment equipment.
【請求項2】 前記分解槽の処理水の水面上に循環水落
下緩衝板とその上側位置に循環水噴射管と分解槽の天井
部には気水分離器とを各配設し、分解槽の外側には循環
水噴射管の噴霧水中に空気を噴入するターボファンと、
生ゴミを分解槽内に送給する生ゴミ投入部と、処理残留
物を分離するサイクロン残留物分離器と、残留物乾燥固
形化槽とを配設したことを特徴とする請求項1記載の水
中分解式の生ゴミ処理装置。
2. The circulating water drop buffer plate on the surface of the treated water in the decomposition tank, the circulating water injection pipe above the circulating water drop buffer plate, and the steam separator on the ceiling of the decomposition tank are respectively disposed. A turbo fan that injects air into the spray water of the circulating water injection pipe outside the
The raw garbage feeding section for feeding the raw garbage into the decomposition tank, the cyclone residue separator for separating the processing residue, and the residue drying and solidifying tank are arranged. Underwater decomposition type garbage treatment device.
【請求項3】 前記分解槽の下半部に形成した加熱活性
炭脱臭器部の脱臭器排気出口管から出る二次排気を処理
水中に通して処理水を加熱する排気熱回収交換器を処理
水内に配設し、前記二次排気をターボファンの吸込み側
に連通させて吸込む排気熱回収交換器をターボファンの
吸込み側に設けたことを特徴とする請求項1または請求
項2記載の水中分解式の生ゴミ処理装置。
3. An exhaust heat recovery exchanger that heats the treated water by passing secondary exhaust gas from the deodorizer exhaust outlet pipe of the heated activated carbon deodorizer unit formed in the lower half of the decomposition tank to the treated water. 3. The underwater according to claim 1 or 2, wherein an exhaust heat recovery exchanger, which is disposed inside and communicates the secondary exhaust with the suction side of the turbofan and sucks the secondary exhaust, is provided on the suction side of the turbofan. Disassembly type garbage processing device.
JP31976998A 1998-10-21 1998-10-21 Underwater decomposition type garbage processing equipment Expired - Fee Related JP3490915B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP31976998A JP3490915B2 (en) 1998-10-21 1998-10-21 Underwater decomposition type garbage processing equipment

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP31976998A JP3490915B2 (en) 1998-10-21 1998-10-21 Underwater decomposition type garbage processing equipment

Publications (2)

Publication Number Publication Date
JP2000126723A JP2000126723A (en) 2000-05-09
JP3490915B2 true JP3490915B2 (en) 2004-01-26

Family

ID=18113984

Family Applications (1)

Application Number Title Priority Date Filing Date
JP31976998A Expired - Fee Related JP3490915B2 (en) 1998-10-21 1998-10-21 Underwater decomposition type garbage processing equipment

Country Status (1)

Country Link
JP (1) JP3490915B2 (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2003094019A (en) * 2001-09-27 2003-04-02 Shin Meiwa Ind Co Ltd Underwater decomposition type garbage treatment device
JP2006055734A (en) * 2004-08-19 2006-03-02 Shin Meiwa Ind Co Ltd Underwater decomposition type garbage disposal apparatus
JP2006075782A (en) * 2004-09-13 2006-03-23 Shin Meiwa Ind Co Ltd Foam suppressing unit of aeration tank and garbage treatment apparatus having the unit
JP2006087969A (en) * 2004-09-21 2006-04-06 Shin Meiwa Ind Co Ltd Sewage treatment device and underwater decomposition type garbage treatment apparatus provided with the same

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3023882U (en) 1995-10-18 1996-04-30 エステック株式会社 Garbage decomposition processing device equipped with defoaming liquefaction device

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3023882U (en) 1995-10-18 1996-04-30 エステック株式会社 Garbage decomposition processing device equipped with defoaming liquefaction device

Also Published As

Publication number Publication date
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