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JP3530791B2 - Garbage decomposition equipment - Google Patents

Garbage decomposition equipment

Info

Publication number
JP3530791B2
JP3530791B2 JP34291299A JP34291299A JP3530791B2 JP 3530791 B2 JP3530791 B2 JP 3530791B2 JP 34291299 A JP34291299 A JP 34291299A JP 34291299 A JP34291299 A JP 34291299A JP 3530791 B2 JP3530791 B2 JP 3530791B2
Authority
JP
Japan
Prior art keywords
air
pipe
residue
exhaust
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
JP34291299A
Other languages
Japanese (ja)
Other versions
JP2001157889A (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 JP34291299A priority Critical patent/JP3530791B2/en
Priority to CNB001212443A priority patent/CN1133511C/en
Priority to KR10-2000-0050301A priority patent/KR100434624B1/en
Priority to TW89122006A priority patent/TW496791B/en
Publication of JP2001157889A publication Critical patent/JP2001157889A/en
Priority to HK01106754A priority patent/HK1036239A1/en
Application granted granted Critical
Publication of JP3530791B2 publication Critical patent/JP3530791B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases
    • B01D53/74General processes for purification of waste gases; Apparatus or devices specially adapted therefor
    • 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

  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Chemical & Material Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Processing Of Solid Wastes (AREA)
  • Treating Waste Gases (AREA)
  • Treatment Of Sludge (AREA)

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】本発明は生ゴミを分解する処
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 a processing apparatus for decomposing food waste.

【0002】[0002]

【従来の技術】従来、水を張った処理槽の底面位置より
蓋側に向かって垂立させた略円筒形状の吸込み吹上げ筒
を設け吸込み吹上げ筒の一部を大径にしてエゼクター部
を形成し、該エゼクター内に空気送給管の先端部に設け
た空気噴出口を上向きにして取付け、吸込み吸上げ筒の
上端部に吸上げた気泡を拡散する拡散プレートと排気を
導出する排気制御蓋を設けた生ゴミ処理装置が知られて
いる(例えば特許第2704713号公報参照)。ま
た、分解槽の外側位置に蒸発固形化槽や消臭器を配設し
たものも知られている(例えば特開平11−16982
5号公報参照)。
2. Description of the Related Art Conventionally, a substantially cylindrical suction blow-up tube which is erected from the bottom position of a processing tank filled with water toward the lid side is provided, and a part of the suction blow-up tube has a large diameter to make an ejector portion. And the air jet port provided at the tip of the air supply pipe is installed inside the ejector with the air jet port facing upward, and a diffusion plate for diffusing the sucked bubbles to the upper end of the suction suction cylinder and an exhaust for discharging the exhaust A garbage processing device provided with a control lid is known (see, for example, Japanese Patent No. 2704713). Further, there is also known one in which an evaporative solidification tank and a deodorizer are arranged outside the decomposition tank (for example, Japanese Patent Laid-Open No. 11-16982).
(See Japanese Patent Publication No. 5).

【0003】[0003]

【発明が解決しようとする課題】従来の生ゴミ分解処理
装置においては、発泡現象を生じた場合に気水分離を行
なう機能を有してはいるが処理能力、例えばエアーの供
給量を多くすればする程発泡現象も著しく増大し、処理
能力には限界があり、また装置の各部位、例えば上部蓋
部等に漏洩が発生した場合には臭気ガスが分解槽外に流
出し、さらに循環ポンプを使用するために少容量移送時
には特にごみによる詰まりが発生しやすく、そのために
また別に動力源が必要となるためランニングコストが高
くなる問題点を有していた。本発明はこれらの問題点に
鑑み、発泡現象それ自体を抑制し、万一漏洩個所が発生
しても臭気ガスが分解槽外に流出することなく、また、
ランニングコストの低減にも寄与する生ゴミ分解処理装
置を提供することを目的として発明されたものである。
The conventional apparatus for decomposing food waste has a function of separating air and water when a foaming phenomenon occurs, but the processing capacity, for example, the supply amount of air is increased. The foaming phenomenon increases remarkably as it grows, and the processing capacity is limited.In addition, if a leak occurs in each part of the equipment, such as the upper lid, odorous gas flows out of the decomposition tank, and the circulation pump Therefore, there is a problem that clogging due to dust is liable to occur especially when transferring a small amount, and a separate power source is required for that purpose, resulting in high running cost. In view of these problems, the present invention suppresses the foaming phenomenon itself, and even if a leak location occurs, odorous gas does not flow out of the decomposition tank, and
The invention was invented for the purpose of providing an apparatus for decomposing food waste that also contributes to a reduction in running cost.

【0004】[0004]

【課題を解決するための手段】槽内で張った処理水内で
生ゴミを処理する処理槽本体の天井部と天井部上側に設
けた気水分離室とに水柱圧力計を付設して、エアーブロ
アーの吸引力で前記処理槽本体の天井部と前記気水分離
室とを負圧に制御する。処理槽本体の吸込み吹上げ筒
で発生させた気水混合体を負圧で吸上げ、前記気水分離
室内に形成した気水通過隙間と排気通過隙間を通過させ
て気水分離を実行すると共に発泡を潰す。生ゴミを移送
する移送エアーリフターの吸上げ側のスラリー状生ゴミ
送給管を前記負圧の天井部に連通配管し、残渣取出しエ
アーリフターの吸上げ側の残渣送給管を槽内の負圧でエ
アーを噴出するエアーの噴気管の吸引で負圧となった残
渣乾燥タンクに各々連通して吸上げ移送する。
[Means for Solving the Problem] A water column pressure gauge is attached to a ceiling part of a main body of a processing tank for treating food waste in treated water stretched in the tank and a steam separation chamber provided above the ceiling part. Separation of air and water from the ceiling of the processing tank body by the suction force of an air blower
Control the chamber and negative pressure. The steam-water mixture generated in the suction blow-up cylinder of the processing tank main body is sucked up with a negative pressure, and the steam-water separation gap and the exhaust passage gap formed in the steam-water separation chamber are passed to perform steam-water separation. Along with foaming. Transfer the raw garbage Slurry raw garbage feed pipe on the suction side of the air lifter is connected to the negative pressure ceiling, and the residue take-up residue suction pipe of the air lifter is placed on the negative side of the tank. The air is blown out by the pressure, and the air is blown up and transferred to each of the residue drying tanks that have become negative pressure due to the suction of the air blow tube.

【0005】[0005]

【発明の実施の形態】本発明を図面に基づいて説明する
と、図1〜図5において処理槽本体1は、例えばステン
レス鋼で形成することが好ましく、処理槽本体1の天井
面2を上方に向かって中空箱形に形成して内側に気水分
離室3を設ける。拡散プレート円板4は円板形に形成
し、気水分離室3の天板5の略中央位置に下向きに螺入
した調整螺子6の下端部に固着する。気水分離板7は縦
断面コ字形の平面視円形に形成し中央部に取付けた調整
螺子8を天板5に下向きに螺入し、気水分離板7を倒伏
コ字形に拡散プレート4上に設ける。排気制御部9は天
井面2側を大径に上端側を小径にした中空の円錐台形に
形成して天井面2に取付け、内側に前記拡散プレート4
を挿入して排気制御部9との間に気水通過隙間10を形
成する。さらに詳しくは排気制御部9の上端面11と前
記気水分離板7の下端面12とで隙間を設け、排気通過
隙間13を形成する。降水管14は天井面2に一端を開
口して取付け、他の一端側は垂下して鉛直方向に取付け
る。
BEST MODE FOR CARRYING OUT THE INVENTION The present invention will be described with reference to the drawings. In FIGS. 1 to 5, the processing tank body 1 is preferably made of, for example, stainless steel, and the ceiling surface 2 of the processing tank body 1 is directed upward. It is formed in a hollow box shape toward the inside, and the steam separation chamber 3 is provided inside. The diffusion plate disk 4 is formed in a disk shape, and is fixed to the lower end portion of the adjusting screw 6 screwed downward at a substantially central position of the top plate 5 of the steam separation chamber 3. The air / water separating plate 7 is formed in a circular shape in a plan view having a U-shaped vertical cross section, and an adjusting screw 8 attached to the central portion is screwed downward into the top plate 5, so that the air / water separating plate 7 is in the inverted U-shape on the diffusion plate 4. To be installed. The exhaust control unit 9 is formed into a hollow truncated cone shape having a large diameter on the ceiling surface 2 side and a small diameter on the upper end side, and is attached to the ceiling surface 2, and the diffusion plate 4 is provided inside.
Is inserted to form a water vapor passage gap 10 with the exhaust control unit 9. More specifically, a gap is provided between the upper end surface 11 of the exhaust control unit 9 and the lower end surface 12 of the steam / water separating plate 7 to form an exhaust passage gap 13. The downcomer pipe 14 is attached to the ceiling surface 2 with one end opened and the other end is hung and attached vertically.

【0006】吸込み吹上げ筒15は略円筒形に形成し、
処理槽本体1の略中央位置に縦方向に垂立させて取付け
る。さらに詳しくは、吸込み吹上げ筒15の下端部は処
理槽本体1の全高の下から略1/3の高さ位置に設けた
水槽底面16と吸込み隙間17を設けて取付け、吸込み
吹上げ筒15の全高の略中央位置の胴部を大径にしてエ
ゼクター胴部18を形成する。エアーの噴気管19は、
先端側を前記エゼクター胴部18内に挿入して略L字形
に上向きに曲げて取付ける。脱臭用活性炭20は、水槽
底面16と処理槽本体底面21間に充填する。脱臭器排
気入口管22と脱臭器排気出口管23は、例えば内側が
中空の鋼管を用い、中空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24と排気進入穴25を
各穿設して、脱臭用活性炭20中に横方向に埋設する。
The suction blow-up cylinder 15 is formed in a substantially cylindrical shape,
The processing tank main body 1 is vertically installed at a substantially central position. More specifically, the lower end of the suction blow-up tube 15 is attached with a water tank bottom surface 16 and a suction gap 17 provided at a height position of about 1/3 below the entire height of the treatment tank main body 1, and the suction blow-up tube 15 is attached. The ejector body portion 18 is formed by increasing the diameter of the body portion at a substantially central position of the entire height. The air fumes 19
The tip end side is inserted into the ejector body portion 18 and bent upward in a substantially L-shape to be attached. The deodorizing activated carbon 20 is filled between the water tank bottom surface 16 and the processing tank body bottom surface 21. For the deodorizer exhaust inlet pipe 22 and the deodorizer exhaust outlet pipe 23, for example, hollow steel pipes are used, and exhaust exhaust holes 24 and exhaust inlet holes that penetrate both ends of the hollow and penetrate the inner hollow portion at the peripheral surface are used. 25 are bored and embedded laterally in the deodorizing activated carbon 20.

【0007】エアーブロアー26は、吸入側は前記気水
分離室3内と一端側を連通したバキューム配管27を介
して配置し、吐出側は前記脱臭器排気入口管22の中空
内部と連通した排気送入管28と連通する。さらに詳し
くは、バキューム配管27の途中にはフロートスイッチ
29を設けることが望ましい。フロートスイッチ29を
設けることにより、万一配管中に水分が流れてきた場合
にエアーブロアー26の損傷を防げる。移送エアーリフ
ター30は、中空の略円錐台形に形成し、底部側面に投
入破砕槽31からの導入管32を内部と連通して配管
し、反対側の側面からは大気を吸込む大気吸込み管33
の一先端部をL字形に上向きに折曲げて挿入固着し、上
端部には一端側を処理槽本体1の天井面2の稍下側位置
の側面内部の天井部Tと連通したスラリー状生ゴミ送給
管34の他の一端部を内部と連通して配管する。
The air blower 26 is arranged on the suction side via a vacuum pipe 27 which communicates with the inside of the water / water separation chamber 3 at one end side, and on the discharge side, the exhaust air communicated with the hollow inside of the deodorizer exhaust inlet pipe 22. It communicates with the inlet pipe 28. More specifically, it is desirable to provide a float switch 29 in the middle of the vacuum pipe 27. By providing the float switch 29, it is possible to prevent the air blower 26 from being damaged if water flows into the piping. The transfer air lifter 30 is formed in a hollow, generally frustoconical shape, and has an inlet pipe 32 from the throwing-in crushing tank 31 in communication with the inside on the bottom side surface, and an atmosphere suction pipe 33 for sucking the atmosphere from the opposite side surface.
One tip end of the slurry is bent upward into an L-shape and fixedly inserted, and one end side of the upper end is connected to the ceiling portion T of the ceiling surface 2 of the processing tank main body 1 to communicate with the ceiling portion T inside the slurry-like raw material. The other end of the dust feed pipe 34 is connected to the inside to be piped.

【0008】残渣取出しエアーリフター35は前記移送
エアーリフター30と略同一構造に形成し、底部側面に
は前記水槽底面16からの残渣送出し管36を内部と連
通して配管し、反対側の側面からは大気を吸込む大気吸
込み管37の一端側を内部と連通して配管し、上端部に
は一端側を後述する残渣乾燥タンク38の内部と連通し
た残渣送給管39の他の一端部を内部と連通して配管す
る。さらに詳しくは、残渣取出しエアーリフター35の
内部と一端側を連通した大気吸込み管37の他の一端部
は図面に示す如く逆流を防止するために逆立ちU字形に
形成する。そして、大気吸込み管37の配管は逆立ちU
字管との中間から残渣乾燥タンク38の後述する内箱底
部に乾燥用空気送給管41を枝設配管し、乾燥用空気が
吹出すようにする。また、これらの部位と前記エアーブ
ロアー26とを一体にしたエアーブロアーのユニット4
0は図面では理解しやすいように処理槽本体1の外側位
置に配設しているが、処理槽本体1の底部に配設すると
熱損失が一層少なくなるので好ましい。
The residue take-out air lifter 35 is formed in substantially the same structure as the transfer air lifter 30, and a bottom surface of the bottom is provided with a residue delivery pipe 36 from the bottom 16 of the water tank so as to communicate with the inside thereof. From the above, one end side of an air suction pipe 37 for sucking air is connected to the inside for piping, and the other end portion of a residue feed pipe 39 having one end side communicating with the inside of a residue drying tank 38 described later is connected to the upper end portion. Plumb in communication with the inside. More specifically, the other end of the air suction pipe 37, which communicates with the inside of the residue extraction air lifter 35 at one end side, is formed in an inverted U shape so as to prevent backflow as shown in the drawing. And the piping of the air suction pipe 37 is upside down U
A drying air supply pipe 41 is branched from the middle of the character pipe to the inner box bottom of the residue drying tank 38, which will be described later, so that the drying air is blown out. Further, an air blower unit 4 in which these parts and the air blower 26 are integrated.
Although 0 is arranged at the outer position of the processing tank main body 1 for easy understanding in the drawing, it is preferable to arrange 0 at the bottom of the processing tank main body 1 because heat loss is further reduced.

【0009】残渣乾燥タンク38は底面42及び側面4
3に沿って一定間隔の排気熱回収溝44を形成した内箱
45を設けて、内箱45の外側にジャケット部を形成す
る。内箱45の内側に鋼材で籠状に形成した取出しネッ
ト46を設け、取出しネット46の底面47と内箱45
間に加熱ヒーター48を設ける。エアーの噴気管19に
一端部を連通したエアー通気管49の他の一端部は残渣
乾燥タンク38内に連通して配管する。また、残渣乾燥
タンク38の排気熱回収溝44の底部に排気熱通気管5
0の一端側を連通して配管し、排気熱通気管50の他端
側は脱臭器排気出口管23の一端内部と連通して配管す
る。水柱圧力計51は、気水分離室3内と連通する気水
分離室内連通管52と処理槽本体1内の天井面2の下部
位置の側面内部の天井部Tと連通する処理槽本体連通管
53とを枝設し、各々U字形に曲げ水を入れて形成した
気水分離室3内と大気圧との圧力差Pを計測する気水分
離室圧力計54と、気水分離室3内と処理槽本体1内と
の圧力差Pを計測する差圧計測圧力計55とを形成す
る。
The residue drying tank 38 has a bottom surface 42 and a side surface 4.
3, an inner box 45 having exhaust heat recovery grooves 44 formed at regular intervals is provided, and a jacket portion is formed on the outer side of the inner box 45. A basket-shaped take-out net 46 made of steel is provided inside the inner box 45, and the bottom 47 of the take-out net 46 and the inner box 45 are provided.
A heater 48 is provided between them. The other end of the air vent pipe 49, which has one end communicating with the air blast pipe 19, communicates with the inside of the residue drying tank 38 for piping. Further, the exhaust heat ventilation pipe 5 is provided at the bottom of the exhaust heat recovery groove 44 of the residue drying tank 38.
0 is connected to one end side of the exhaust heat ventilation pipe 50 and the other end of the exhaust heat ventilation pipe 50 is connected to the inside of one end of the deodorizer exhaust outlet pipe 23. The water column pressure gauge 51 includes a communication pipe 52 for communicating with the air / water separation chamber 3 that communicates with the inside of the water / water separation chamber 3, and a communication pipe for a treatment tank body that communicates with a ceiling portion T inside a side surface of the treatment tank body 1 at a lower position of the ceiling surface 2. 53 and a steam-water separation chamber pressure gauge 54 for measuring the pressure difference P between the inside of the steam-water separation chamber 3 formed by bending water into a U-shape and the atmospheric pressure, and the inside of the steam-water separation chamber 3. And a differential pressure measuring pressure gauge 55 for measuring a pressure difference P between the inside of the processing tank main body 1 and the inside of the processing tank main body 1.

【0010】[0010]

【実施例】エアーブロアー26の実機テストによる値を
下記に示す。 送風量 120l/分 吸込み圧力 P=−420mmAq (気水分離室内) 処理槽天井部と気水分離室内との圧力差 p=40mmAq また、拡散プレート円板4の直径100m/mの場合の
排気制御部9との気水隙間10は20m/m、排気制御
部9の上端面11と気水分離板7の下端面12とで形成
する排気通過隙間13は、20m/mに形成すると好結
果が得られる。次に移送エアーリフター30について
は、全高Hが200m/m、底面直径Rが65m/m、
導入管32の導入径は25m/m、スラリー状生ゴミ送
給管34の口径15m/m、大気吸込み管33の直径は
10m/mに形成すると好結果が得られた。
EXAMPLES The values of the actual test of the air blower 26 are shown below. Air flow rate 120 l / min Suction pressure P = -420 mmAq (air / water separation chamber) Pressure difference between the ceiling of the processing tank and the air / water separation chamber p = 40 mmAq Further, exhaust control when the diameter of the diffusion plate disk 4 is 100 m / m If the air / water gap 10 with the portion 9 is 20 m / m, and the exhaust passage gap 13 formed by the upper end surface 11 of the exhaust control unit 9 and the lower end surface 12 of the air / water separating plate 7 is 20 m / m, good results are obtained. can get. Next, regarding the transfer air lifter 30, the total height H is 200 m / m, the bottom surface diameter R is 65 m / m,
Good results were obtained when the introduction diameter of the introduction pipe 32 was 25 m / m, the diameter of the slurry-like garbage feed pipe 34 was 15 m / m, and the diameter of the air suction pipe 33 was 10 m / m.

【0011】次に本発明を実施使用する場合について述
べると、処理槽本体1内に水面Wの高さまで水を注入し
エアーブロアー26を作動さすとバキューム配管27を
介して気水分離室3内は−420mmAq、処理槽天井
部Tと気水分離室3内との圧力差は40mmAqと負圧
となるため、エアーの噴気管19から前記の負圧の吸引
力により気水混合体Kとなって吸上げられる。上昇した
気水混合体Kは拡散プレート円板4に衝突し周囲へ拡散
し、水は円錐台形の排気制御部9の傾斜板に沿って下部
の処理槽本体1内に流落する。そしてここで空気成分と
分離され、気水通過隙間10及び排気通過隙間13中を
通過してさらに気水分離板7に接触し、水分を分離除去
後気水分離された水分の一部は降水管14から下に流落
し、空気成分はバキューム配管27より排出される。さ
らに詳しくは、発泡現象を含んだ水がバキュームの作用
で上昇してくると気水通過隙間10及び排気通過隙間1
3の隙間でしぼられ、急激に圧力の低下をきたす為にこ
こで泡がひきちぎられるように破壊され発泡現象を簡単
に抑えられる。
Next, the case of implementing the present invention will be described. When water is injected to the height of the water surface W in the treatment tank main body 1 and the air blower 26 is operated, the inside of the steam separation chamber 3 is passed through the vacuum pipe 27. Is -420 mmAq, and the pressure difference between the treatment tank ceiling portion T and the inside of the steam / water separation chamber 3 is 40 mmAq, which is a negative pressure. Therefore, the air-fuel mixture K is formed by the suction force of the negative pressure from the air fusible pipe 19. Is sucked up. The rising water-water mixture K collides with the diffusion plate disk 4 and diffuses to the surroundings, and the water flows down into the lower processing tank body 1 along the inclined plate of the truncated cone-shaped exhaust control unit 9. Then, here, it is separated from the air component, passes through the air / water passage gap 10 and the exhaust air passage gap 13 and further contacts the air / water separation plate 7, and after the water is separated and removed, a part of the water separated by the water vapor is precipitated. The air component flows down from the pipe 14, and the air component is discharged from the vacuum pipe 27. More specifically, when the water containing the bubbling phenomenon rises due to the action of the vacuum, the air-water passage gap 10 and the exhaust passage gap 1
It is squeezed in the gap 3 and the pressure is suddenly lowered, so that the bubbles are broken like being torn off here and the foaming phenomenon can be easily suppressed.

【0012】また、投入破砕槽31内に投入されスラリ
ー状に破砕された生ゴミは移送エアーリフター30に送
られるが、此の場合、移送エアーリフター30のスラリ
ー状生ゴミ送給管34には前記の負圧(略400mmA
q)が作用しており、バキューム効果によりスラリー状
の生ゴミは吸上げられてスラリー状生ゴミ送給管34中
を上昇し、処理槽本体1内に供給される。
[0012] Further, the raw garbage thrown into the input crushing tank 31 and crushed into a slurry is sent to the transfer air lifter 30. In this case, the raw garbage transfer pipe 34 of the transfer air lifter 30 has a slurry-like raw garbage feed pipe 34. The negative pressure (approx. 400 mmA)
q) is acting, and the slurry-like raw dust is sucked up by the vacuum effect, rises in the slurry-like raw dust feed pipe 34, and is supplied into the processing tank main body 1.

【0013】水槽底面16に溜まった生ゴミの残渣は、
次に残渣取出しエアーリフター35を介して残渣乾燥タ
ンク38に送られる。さらに詳しくは、残渣乾燥タンク
38内は蓋をすると前記エアーの噴気管19からのバキ
ュームによる吸込みでエアー通気管49内は負圧とな
り、内箱45内も負圧となり、従って残渣乾燥タンク3
8内と一端部を連通する残渣送給管39内は負圧となっ
て、残渣取出しエアーリフター35内に水槽底面16か
ら流入した生ゴミの残渣Nは残渣乾燥タンク38内に送
られて取出しネット46中に送給する。そして残渣の乾
燥は内箱45の底部より吹出す空気によって行なう。ま
た、残渣乾燥タンク38の排気熱回収溝44内には、一
端部を脱臭器排気出口管23と連通した排気熱通気管5
0の他の一端部が連通されているため、エアーブロアー
26の吐出側の排気送入管28から脱臭器排気入口管2
2の排気噴出穴24から脱臭用活性炭20内に噴出し、
さらに脱臭器排気出口管23の排気進入穴25から入っ
た高温の排気が排気熱回収溝44に送給されて底部より
加熱し、生ゴミの残渣の乾燥効果を助長する。さらに詳
しくは、加熱ヒーター48で加熱することにより、寒冷
時の追い加熱及び乾燥残渣取出し時に殺菌のために70
〜100℃程度に加熱する。
The residue of the garbage collected on the bottom 16 of the water tank is
Next, the residue is sent to a residue drying tank 38 via an air lifter 35. More specifically, if the inside of the residue drying tank 38 is covered, the inside of the air vent pipe 49 becomes a negative pressure due to the suction of the air by the vacuum pipe 19 and the inside box 45 also becomes a negative pressure.
The inside of the residue feed pipe 39 that communicates between the inside of 8 and one end becomes a negative pressure, and the residue N of the raw garbage that has flowed into the residue removal air lifter 35 from the water tank bottom surface 16 is sent to the residue drying tank 38 and taken out. It is sent to the net 46. The residue is dried by air blown from the bottom of the inner box 45. Further, in the exhaust heat recovery groove 44 of the residue drying tank 38, the exhaust heat ventilation pipe 5 whose one end communicates with the deodorizer exhaust outlet pipe 23.
Since the other end of 0 is communicated, the deodorizer exhaust inlet pipe 2 is connected to the exhaust inlet pipe 28 on the discharge side of the air blower 26.
From the exhaust outlet 24 of No. 2 into the deodorizing activated carbon 20,
Further, the high-temperature exhaust gas that has entered through the exhaust gas entry hole 25 of the deodorizer exhaust gas exhaust pipe 23 is fed to the exhaust heat recovery groove 44 and heated from the bottom portion, thereby promoting the drying effect of the residue of raw garbage. More specifically, by heating with the heater 48, 70% for additional heating in cold weather and for sterilization during removal of dried residue.
Heat to about 100 ° C.

【0014】[0014]

【発明の効果】以上説明したように本発明は、強力な負
圧閉回路を処理槽本体及び気水分離室に形成することに
より発泡現象を抑制し、負圧を利用したエアーリフト移
送が可能となって少容量移送でもごみによる詰まりが無
くなり、ランニングコストも低減し、さらに装置に万一
漏洩個所が発生しても各部位が負圧であるため臭気ガス
を外に出さないシステムにすることができる。
As described above, according to the present invention, by forming a strong negative pressure closed circuit in the processing tank body and the water / water separation chamber, the foaming phenomenon is suppressed, and the air lift transfer utilizing the negative pressure is possible. Therefore, even if a small volume is transferred, clogging due to dust will be eliminated, running costs will be reduced, and even if a leak location should occur in the equipment, each part will have a negative pressure so that odorous gas will not be emitted to the outside. You can

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

【図1】生ゴミ分解処理装置の一部は縦断面で示す正面
図である。
FIG. 1 is a front view showing a part of a food waste decomposition processing device in a vertical section.

【図2】気水分離室部分の縦断面図である。FIG. 2 is a vertical sectional view of a steam separation chamber portion.

【図3】気水分離室部分の斜視図である。FIG. 3 is a perspective view of a steam separation chamber portion.

【図4】移送エアーリフターの縦断面図である。FIG. 4 is a vertical cross-sectional view of a transfer air lifter.

【図5】残渣乾燥タンクの斜視図である。FIG. 5 is a perspective view of a residue drying tank.

【符号の説明】[Explanation of symbols]

1 処理槽本体 3 気水分離室 4 拡散プレート円板 7 気水分離板 9 排気制御部 10 気水通過隙間 13 排気通過隙間 14 降水管 15 吸込み吹上げ筒 16 水槽底面 19 エアーの噴気管 20 脱臭用活性炭 22 脱臭器排気入口管 23 脱臭器排気出口管 26 エアーブロアー 27 バキューム配管 28 排気送入管 30 移送エアーリフター 31 投入破砕槽 34 スラリー状生ゴミ送給管 35 残渣取出しエアーリフター 36 残渣送出し管 37 大気吸込み管 38 残渣乾燥タンク 39 残渣送給管 41 乾燥用空気送給管 44 排気熱回収溝 45 内箱 46 取出しネット 48 加熱ヒーター 50 排気熱通気管 51 水柱圧力計 52 気水分離室内連通管 53 処理槽本体連通管 54 気水分離室圧力計 55 差圧計測圧力計 1 Processing tank body 3 steam separation room 4 Diffusion plate disk 7 steam separator 9 Exhaust control unit 10 Air / water passage gap 13 Exhaust passage gap 14 downcomer 15 Suction blow-up tube 16 Water tank bottom 19 Air fumes 20 Activated carbon for deodorization 22 Deodorizer exhaust inlet pipe 23 Deodorizer exhaust outlet pipe 26 Air blower 27 Vacuum piping 28 Exhaust pipe 30 transfer air lifter 31 input crushing tank 34 Slurry garbage feed pipe 35 Residue removal air lifter 36 Residue delivery pipe 37 Atmosphere suction pipe 38 Residue drying tank 39 Residue supply pipe 41 Drying air supply pipe 44 Exhaust heat recovery groove 45 inner box 46 Take-out net 48 heating heater 50 Exhaust heat ventilation pipe 51 Water column pressure gauge 52 Communication pipe for air / water separation chamber 53 Processing tank main body communication pipe 54 Air-Water Separation Chamber Pressure Gauge 55 Differential pressure measurement pressure gauge

───────────────────────────────────────────────────── フロントページの続き (56)参考文献 特開 平11−77003(JP,A) 特開2000−126723(JP,A) 特開 平9−1118(JP,A) 実開 昭54−150176(JP,U) (58)調査した分野(Int.Cl.7,DB名) B09B 3/00 - 5/00 C02F 3/00 - 3/24 C02F 11/02 ─────────────────────────────────────────────────── ─── Continuation of the front page (56) References JP-A-11-77003 (JP, A) JP-A-2000-126723 (JP, A) JP-A-9-1118 (JP, A) Actual development Sho-54-150176 (JP, U) (58) Fields surveyed (Int.Cl. 7 , DB name) B09B 3/00-5/00 C02F 3/00-3/24 C02F 11/02

Claims (4)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】 槽内に張った処理水内で生ゴミを処理す
る処理槽本体の天井部と天井部上側に設けた気水分離室
とに圧力計を付設してエアーブロアーのエアー吸引力で
前記処理槽本体の天井部および前記気水分離室を負圧に
制御し、前記処理槽本体内に水槽底面との間に吸込み隙
間を設けて縦方向に垂立させた吸込み吹上げ筒の一部を
大径にしてエゼクター胴部を形成し、該エゼクター胴部
内に空気送給管の先端部に設けた空気噴出口を上向きに
して取付け、前記吸込み吹上げ筒内で発生した気水混合
体を吸上げて気水分離室内で気水分離を実行し泡は破壊
し、前記天井部と生ゴミを供給する移送エアーリフター
の吸上げ側とを配管で接続し、スラリー状の生ゴミを負
圧で送給することを特徴とする生ゴミ分解処理装置。
1. An air suction force of an air blower by attaching a pressure gauge to a ceiling portion of a treatment tank main body for treating raw garbage in treated water stretched in the tank and a steam separation chamber provided above the ceiling portion. so
The ceiling of the processing tank body and the steam separation chamber are controlled to a negative pressure, and a suction gap is formed between the processing tank body and the bottom surface of the water tank.
A part of the suction blow-up tube that is set upright in the vertical direction with a space
The ejector body is formed with a large diameter, and the ejector body is formed.
The air outlet provided at the tip of the air supply pipe inside
Installed, the air-water mixture generated in the suction blow-up cylinder is sucked up, air-water separation is executed in the air-water separation chamber, bubbles are destroyed, and the ceiling portion and a transfer air lifter for supplying raw garbage are supplied. An apparatus for decomposing food waste, which is connected to the suction side with a pipe and feeds slurry-like food waste at a negative pressure.
【請求項2】 前記気水分離室が処理槽本体の天井面に
中空の円錐台形に形成した排気制御部とその内側に設け
られた円板状の拡散プレート円板と排気制御部の上側位
置に設けた気水分離板とで各々気水通過隙間、及び排気
通過隙間を形成したことを特徴とする請求項1記載の生
ゴミ分解処理装置。
2. An exhaust control unit in which the air / water separation chamber is formed in a hollow truncated cone shape on the ceiling surface of a processing tank main body, a disc-shaped diffusion plate provided inside the exhaust control unit, and an upper position of the exhaust control unit. The garbage disintegration processing device according to claim 1, wherein a steam passing gap and an exhaust passing gap are respectively formed with the steam separating plate provided in the.
【請求項3】 処理槽本体の外側位置に残渣取出しエア
ーリフターと排気熱回収溝を形成した残渣乾燥タンクと
を設け、残渣乾燥タンク内と処理槽本体内に設けた吸込
み吹上げ筒内のエアーの噴気管とをエアー通気管で連通
配管し、残渣取出しエアーリフターと残渣乾燥タンク内
とは残渣送給管で、残渣取出しエアーリフターと水槽底
面とは残渣送出し管で各々連通配管したことを特徴とす
る請求項1、または2記載の生ゴミ分解処理装置。
3. A residue take-out air lifter and a residue drying tank having an exhaust heat recovery groove are provided outside the processing tank main body, and air in a suction blowing cylinder provided in the residue drying tank and the processing tank main body is provided. The air blower pipe is used to connect the fumarole pipe to the residue extraction air lifter and the residue drying tank are residue feed pipes, and the residue extraction air lifter and the bottom of the water tank are residue discharge pipes. 3. The apparatus for decomposing food waste according to claim 1 or 2, characterized in that.
【請求項4】 処理槽本体の水槽底面の下側に脱臭用活
性炭を充填し脱臭用活性炭中に脱臭器排気入口管と脱臭
器排気出口管とを埋設し、脱臭器排気入口管には前記エ
アーブロアーの吐出側と連通配管し、脱臭器排気出口管
には前記残渣乾燥タンクの排気熱回収溝内と各々連通配
管したことを特徴とする請求項1、2、または3記載の
生ゴミ分解処理装置。
4. A deodorizing activated carbon is filled under the water tank bottom of the treatment tank main body, and a deodorizing device exhaust inlet pipe and a deodorizing device exhaust outlet pipe are buried in the deodorizing activated carbon, and the deodorizing device exhaust inlet pipe is provided with the above The raw garbage decomposing apparatus according to claim 1, 2 or 3, wherein the discharge side of the air blower is connected to a pipe, and the exhaust outlet pipe of the deodorizer is connected to an exhaust heat recovery groove of the residue drying tank. Processing equipment.
JP34291299A 1999-12-02 1999-12-02 Garbage decomposition equipment Expired - Fee Related JP3530791B2 (en)

Priority Applications (5)

Application Number Priority Date Filing Date Title
JP34291299A JP3530791B2 (en) 1999-12-02 1999-12-02 Garbage decomposition equipment
CNB001212443A CN1133511C (en) 1999-12-02 2000-08-10 Raw refuse decomposing and disposaling apparatus
KR10-2000-0050301A KR100434624B1 (en) 1999-12-02 2000-08-29 Apparatus for garbage decomposition and disposal
TW89122006A TW496791B (en) 1999-12-02 2000-10-18 Device for garbage decomposition and disposal
HK01106754A HK1036239A1 (en) 1999-12-02 2001-09-25 Apparatus for decomposition treatment of original garbage

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP34291299A JP3530791B2 (en) 1999-12-02 1999-12-02 Garbage decomposition equipment

Publications (2)

Publication Number Publication Date
JP2001157889A JP2001157889A (en) 2001-06-12
JP3530791B2 true JP3530791B2 (en) 2004-05-24

Family

ID=18357491

Family Applications (1)

Application Number Title Priority Date Filing Date
JP34291299A Expired - Fee Related JP3530791B2 (en) 1999-12-02 1999-12-02 Garbage decomposition equipment

Country Status (5)

Country Link
JP (1) JP3530791B2 (en)
KR (1) KR100434624B1 (en)
CN (1) CN1133511C (en)
HK (1) HK1036239A1 (en)
TW (1) TW496791B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
FR3013701B1 (en) * 2013-11-27 2017-07-21 Orege METHOD AND DIPSOSITIVE FOR TREATING AN ORGANIC EFFLUENT
JP5959129B1 (en) * 2015-07-10 2016-08-02 島産業株式会社 Airflow formation mechanism in weight reduction / volume reduction processing equipment and weight reduction / volume reduction processing equipment
CN109701778B (en) * 2018-11-16 2021-04-30 韶关市诚湃新能源科技有限公司 Automatic spraying device and spraying method for household garbage microbial degradation agent

Also Published As

Publication number Publication date
TW496791B (en) 2002-08-01
KR100434624B1 (en) 2004-06-05
CN1297791A (en) 2001-06-06
JP2001157889A (en) 2001-06-12
HK1036239A1 (en) 2001-12-28
KR20010067122A (en) 2001-07-12
CN1133511C (en) 2004-01-07

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