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JPS6042368B2 - Sewage sludge resource recovery equipment - Google Patents
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JPS6042368B2 - Sewage sludge resource recovery equipment - Google Patents

Sewage sludge resource recovery equipment

Info

Publication number
JPS6042368B2
JPS6042368B2 JP56205253A JP20525381A JPS6042368B2 JP S6042368 B2 JPS6042368 B2 JP S6042368B2 JP 56205253 A JP56205253 A JP 56205253A JP 20525381 A JP20525381 A JP 20525381A JP S6042368 B2 JPS6042368 B2 JP S6042368B2
Authority
JP
Japan
Prior art keywords
combustion chamber
sewage sludge
gas
ash
supplied
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
Application number
JP56205253A
Other languages
Japanese (ja)
Other versions
JPS58109198A (en
Inventor
靖夫 広瀬
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.)
Nippon Furnace Co Ltd
Original Assignee
Nippon Furnace 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 Nippon Furnace Co Ltd filed Critical Nippon Furnace Co Ltd
Priority to JP56205253A priority Critical patent/JPS6042368B2/en
Priority to US06/415,963 priority patent/US4507127A/en
Priority to DE19823238163 priority patent/DE3238163A1/en
Priority to FR8221215A priority patent/FR2518525B1/en
Publication of JPS58109198A publication Critical patent/JPS58109198A/en
Priority to US06/689,105 priority patent/US4585463A/en
Priority to US06/689,210 priority patent/US4583470A/en
Publication of JPS6042368B2 publication Critical patent/JPS6042368B2/en
Expired 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
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E50/00Technologies for the production of fuel of non-fossil origin
    • Y02E50/30Fuel from waste, e.g. synthetic alcohol or diesel

Landscapes

  • Processing Of Solid Wastes (AREA)
  • Treatment Of Sludge (AREA)
  • Gasification And Melting Of Waste (AREA)

Description

【発明の詳細な説明】 従来下水汚泥は補助の燃料を供給して焼却処理すべき
排棄物であると考へられていた。
DETAILED DESCRIPTION OF THE INVENTION Conventionally, sewage sludge was considered to be a waste that should be incinerated with supplementary fuel.

本出願人は、下水汚泥の焼却について永年間研究を進
め、可成低カロリーの下水汚泥であつても自己のカロリ
ーを巧みに利用しあまり補助燃料を 使用することなく
自己焼却を果す装置を開発し特許出願をしている(特願
昭55−169165)。
The applicant has been conducting research on the incineration of sewage sludge for many years, and has developed a device that skillfully uses its own calories to incinerate even low-calorie sewage sludge without using much auxiliary fuel. A patent application has been filed (Japanese Patent Application No. 169165-1983).

本発明の説明に先立つて、先ず先に特許出願をした装置
を第1図によつて説明する。 第1図において、機械的
な脱水法によつて水分率90%程度まで脱水された下水
汚泥はホッパー1内に供給され、該ホッパー1内の下水
汚泥はホッパー底部に設けたスクリュコンベアなど強制
供給手段2によつて先ず下水汚泥加熱器3へ供給され、
該加熱器へは後の工程である熱交換器8において排煙の
熱によつて加熱され高温にされた気体の一部が加熱用気
体として供給され、該加熱器3を通つて該高温の加熱用
気体によつて加熱され流動性になつた下水汚泥は次に流
動妙法を有する乾燥炉4へ供給され、該乾燥炉へは後の
工程である熱交換器8において排煙の熱によつて加熱さ
れ高温にされた気体の一部必要量が乾燥用気体として供
給され、該乾燥炉の乾燥生成物は分離手段5によつて固
体分と気体分とに分離され、固体分は粉”体供給手段6
によつて2段燃焼炉7、7’へ供給され、前記の加熱器
3へ供給した加熱用気体は該加熱炉3を経て若干低温さ
れて取出されるが、この気体をドレン分離手段15に供
給してドレンを除去した後該2段燃焼炉7、7’のいず
れかへ燃料として供給する。該燃焼炉7,7″へ供給す
べき燃焼用空気は該燃焼炉7″の外套として設けた空気
予熱器14を通して予熱した後2段燃焼炉7,7″へ供
給する。該燃焼炉7″の燃焼生成ガスは先ず熱交換器8
へ供給して熱交換させて若干低温にした後にフィルター
9を通して灰分を除去し排風送風機10を通して排風さ
れるのであるが、前記分離手段5によつて分離された気
体分は送風機11を通り前記熱交換器8を含む循環配管
12を通つて気送され該熱交換器8によつて排煙の熱に
よつて加熱され、必要量の気体が前記乾燥炉4へ乾燥用
気体として供給され該必要量を乾燥炉へ供給した後の気
体分は前記加熱器3への加熱用気体として供給される装
置である。しかしながらその後の研究によつて、下水汚
泥は潜在的に多くの者源が含まれているから単に焼却し
て処理すべきものでなく下水汚泥の乾燥によつて生じる
乾燥生成物を農業用土壌改良材としてあるいはガス燃料
を生成させる原料として、あるいはその灰分を塊状にし
てセメント用骨材に供するなど種々の資源にして有効に
利用することができることが判明された。
Prior to explaining the present invention, the apparatus for which a patent application has been applied will first be explained with reference to FIG. In Figure 1, sewage sludge that has been dewatered to a moisture content of approximately 90% by mechanical dewatering is supplied into a hopper 1, and the sewage sludge in the hopper 1 is forcibly fed to a screw conveyor installed at the bottom of the hopper. by the means 2 is first supplied to the sewage sludge heater 3;
A part of the gas that has been heated to a high temperature by the heat of flue gas in the heat exchanger 8 which is a later step is supplied to the heater as a heating gas, and the high temperature gas is supplied through the heater 3. The sewage sludge heated by the heating gas and made fluid is then supplied to a drying furnace 4 having a fluid flow method, and is fed to the drying furnace in a subsequent step by a heat exchanger 8 using the heat of flue gas. A necessary amount of the gas heated to a high temperature is supplied as a drying gas, and the dried product of the drying oven is separated into a solid component and a gas component by a separating means 5, and the solid component is separated into powder. Body supply means 6
The heating gas supplied to the two-stage combustion furnaces 7 and 7' is cooled to a slightly lower temperature after passing through the heating furnace 3, and then taken out. After the fuel is supplied and the drain is removed, it is supplied as fuel to either of the two-stage combustion furnaces 7 and 7'. Combustion air to be supplied to the combustion furnaces 7, 7'' is preheated through an air preheater 14 provided as a jacket of the combustion furnace 7'', and then supplied to the two-stage combustion furnaces 7, 7''. The combustion generated gas first passes through the heat exchanger 8.
After being cooled to a slightly lower temperature through heat exchange, the gas is passed through a filter 9 to remove ash and exhausted through an exhaust blower 10. The gas separated by the separation means 5 passes through a blower 11. Air is sent through the circulation pipe 12 including the heat exchanger 8, heated by the heat of the flue gas by the heat exchanger 8, and the required amount of gas is supplied to the drying oven 4 as a drying gas. After the necessary amount is supplied to the drying oven, the gas is supplied to the heater 3 as a heating gas. However, subsequent research has shown that sewage sludge is not something that should be simply incinerated and treated because it potentially contains many sources, but that the dry product produced by drying sewage sludge can be used as an agricultural soil improvement material. It has been found that the ash can be effectively used as a variety of resources, such as as a raw material for producing gas fuel, or by making the ash into lumps and using it as aggregate for cement.

さきに述べた第1図に示す下水汚泥の焼却装置において
、分離手段5によつて得られる乾燥下水汚泥固体分は第
2図に示すごとくその約50%が灰分であつて残の大部
分すなわち全体の約45%が揮発分でありあとの約5%
が固定炭素分である。
In the sewage sludge incinerator shown in FIG. 1 mentioned above, the solid content of the dried sewage sludge obtained by the separation means 5 is about 50% ash as shown in FIG. Approximately 45% of the total is volatile matter, and the remaining 5%
is the fixed carbon content.

従つて第1図に示す下水汚泥の焼却装置を第3図に示す
資源回収装置にし、得られるガス燃料および塊状灰を資
源として有効に利用することがで.きる。すなわち第3
図の資源回収装置においてはガス化装置21と灰分の処
理装置22を有している。なお、符号23は乾燥下水汚
泥固体分が農業用としてすなわち土壌改良剤として直接
使用される場合を示している。本発明に係る資源回収装
置を説明する以前に本発明の装置で使用する乾燥汚泥の
ガス化装置21と乾燥汚泥灰分の処理装置22について
それぞれ説明をする。
Therefore, it is possible to convert the sewage sludge incinerator shown in Figure 1 into the resource recovery equipment shown in Figure 3, and to effectively utilize the resulting gas fuel and lump ash as resources. Wear. That is, the third
The resource recovery device shown in the figure has a gasification device 21 and an ash processing device 22. Incidentally, reference numeral 23 indicates a case where the dried sewage sludge solid content is directly used for agricultural purposes, that is, as a soil conditioner. Before explaining the resource recovery device according to the present invention, the dry sludge gasification device 21 and the dry sludge ash processing device 22 used in the device of the present invention will be explained respectively.

第4図・第5図は第3図に示す本発明の装置で・使用す
る乾燥汚泥のガス化装置21であつて、中軸部下部にガ
スバーナ31を設けその周囲に丈の高い円筒形の燃焼室
32を設け該燃焼室の外周部に乾溜室33を設け、該燃
焼室の外周壁は回転手段35によつてゆるやかな速度で
回転され、該燃焼室外周壁に数枚の外方向へ突出させた
攪拌羽根36を設け、該乾溜室33の頂部に乾燥汚泥の
供給手段6″を設け、下部に過熱水蒸気など揮発促進気
体の供給管41を設け、底部に灰分取出管を設け、頂部
にガス取出管24を設けた構造のものである。
4 and 5 show a dry sludge gasifier 21 used in the apparatus of the present invention shown in FIG. A chamber 32 is provided, and a dry distillation chamber 33 is provided on the outer periphery of the combustion chamber. A dry sludge supply means 6'' is provided at the top of the dry distillation chamber 33, a supply pipe 41 for volatilization promoting gas such as superheated steam is provided at the bottom, an ash removal pipe is provided at the bottom, and a gas supply means 6'' is provided at the top. It has a structure in which a take-out pipe 24 is provided.

分離手段5によつて分離された乾燥下水汚泥固体分の一
部は粉体供給手段6″によつて該ガス化)装置21に供
給された燃焼室による加熱と過熱水蒸気など揮発促進ガ
スの供給と攪拌羽根によつて500℃乃至700℃の雰
囲気に約1.紛間滞溜させると乾燥汚泥が持つ揮発分の
大部分が気化されそれはガス取出管24によつて取出さ
れて燃料ガス資・源として使用することができる。
A part of the solid content of the dried sewage sludge separated by the separation means 5 is supplied to the gasification device 21 by the powder supply means 6'', where it is heated in a combustion chamber and supplied with volatilization-promoting gas such as superheated steam. When the dried sludge is allowed to stagnate in an atmosphere of about 500°C to 700°C using stirring blades, most of the volatile matter in the dried sludge is vaporized, and it is taken out by the gas extraction pipe 24 and used as fuel gas. can be used as a source.

燃焼室上部に設けた燃焼排ガス排出管39からの燃焼排
ガスは管27によつて熱交換器8へ導びかれる。灰分は
灰分取出管から取出され輸送手段によつて灰分の処理装
置22へ送られる。バーナ31へは加熱器3・へ送つた
加熱用気体をドレン分離手段15を通してドレンを除去
した後に供給して必要な燃焼を行わせることができる。
第6図は第3図に示す本発明の装置で使用する乾燥汚泥
灰分の処理装置22であつて、円筒形内周壁を有するサ
イクロン燃焼室51を設け、該サイクロン燃焼室に粉体
供給手段6″に連結して乾燥汚泥の他の一部が供給され
る乾燥汚泥供給管52を設け、該サイクロン燃焼室周側
壁に接線方向に1次空気供給管54を設け、該サイクロ
ン燃焼室の下部に若干しぼられた部分55を設け、該し
ぼられた部分の真下方に水槽56を設け、該サイクロン
燃焼室51と該水槽56の中間に側方向に炎道60を設
け、該炎道60の先方に第2段燃焼室61を設け、該第
2段燃焼室61に2次空気供給管62を設けた構造のも
のである。
The combustion exhaust gas from the combustion exhaust gas discharge pipe 39 provided at the upper part of the combustion chamber is guided to the heat exchanger 8 through the pipe 27. The ash is taken out from the ash removal pipe and sent to the ash processing device 22 by means of transportation. The heating gas sent to the heater 3 can be supplied to the burner 31 after removing the condensate through the condensate separating means 15 to perform necessary combustion.
FIG. 6 shows a dry sludge ash processing device 22 used in the device of the present invention shown in FIG. A dry sludge supply pipe 52 is provided connected to the cyclone combustion chamber to supply another part of the dried sludge, and a primary air supply pipe 54 is provided in the tangential direction on the peripheral side wall of the cyclone combustion chamber, and a primary air supply pipe 54 is provided in the lower part of the cyclone combustion chamber. A slightly constricted portion 55 is provided, a water tank 56 is provided directly below the constricted portion, a flame path 60 is provided laterally between the cyclone combustion chamber 51 and the water tank 56, and a It has a structure in which a second stage combustion chamber 61 is provided, and a secondary air supply pipe 62 is provided in the second stage combustion chamber 61.

該サイクロン燃焼室51へは前記ガス化装置21で灰分
取出部から取出された灰分を輸送手段25によつて供給
されることができる。該サイクロン燃焼室51内で発生
する火炎は中空火炎であつて周内側壁に近い位置で12
00℃以上の高温火炎を旋回するように形成させること
ができる。下水汚泥の灰分はナトリウムやカリウムを比
較的多量に含んだアルカリ塩であつて700℃乃至80
0℃の比較的低い融点のものであるから容易に周内側壁
面において溶融して周内側壁をつたつて下方に流れしぼ
れた部分55からある大きさの滴になりながら下方へ落
下して水槽56内に落ちて直ちに塊状に固化する。従つ
て取出管59からは適当な大きさの塊として取出し、容
器26内に回収することができる。この塊は可成硬度の
高いアルカリ塩であるからコンクリート用の保強材とし
て資源とすることができる。第2段燃焼室61から排出
される燃焼排ガスは管28によつて熱交換器8へ導びか
れる。本発明の下水汚泥の資源回収装置は第3図に示す
ごとく、分離手段5によつて分離された乾燥下水汚泥気
体分は送風機11によつて圧送され熱交換器8によつて
高温に加熱されて循環回路12によつて気送されその一
部である必要量は乾燥炉4へ乾燥用気体として供給され
該必要量を除いた他部は加熱器3へ加熱気体として供給
され該加熱後の気体分はドレン分離手段15を通つてド
レンを分離した後にガス燃料として供給される下水汚泥
の焼却装置において分離手段5によつて分離された固体
分の一部は粉体供給手段6および6″よつてガス化装置
21へ供給されるようにし該ガス化装置21の頂部に設
けたガス取出管24からガス燃料が取出されるようにし
分離手段5によつて分離された固体分の他の一部は粉体
供給手段6および6″によつてサイクロン燃焼室を第1
段燃焼室とする2段燃焼の灰分の処理装置22のサイク
ロン燃焼室へ供給されるようにし、前記ガス化装置21
の底部に設けた灰分取出管から取出された灰分も該灰分
の処理装置22のサイクロン燃焼室へ供給されるように
し、該灰分の処理装置のサイクロン燃焼室の下方に設け
た水槽底部に設けた灰分塊用容器26から灰分塊として
取出すようにし、該ガス化装置21の燃焼排ガスと該灰
分の処理装置22の第2段燃焼室の燃焼排ガスはそれぞ
れ管27・28によつて熱交換器8へ供給されるように
した下水汚泥の資源回収の装置である。本資源回収装置
は単に下水汚泥を焼却処理するだけでなくガス燃料を管
24から、またコンクリートの骨材となる灰分塊をその
取出手段によつて資源として回収することができる。
The cyclone combustion chamber 51 can be supplied with ash taken out from the ash removal section of the gasifier 21 by means of a transport means 25. The flame generated within the cyclone combustion chamber 51 is a hollow flame with 12
A high-temperature flame of 00° C. or higher can be formed in a swirling manner. The ash content of sewage sludge is an alkaline salt containing relatively large amounts of sodium and potassium, and the temperature ranges from 700℃ to 80℃.
Since it has a relatively low melting point of 0° C., it easily melts on the inner circumferential wall surface and flows downward through the inner circumferential wall from the constricted portion 55, forming droplets of a certain size and falling downward into the water tank 56. It falls into the interior and immediately solidifies into a lump. Therefore, it can be taken out from the take-out tube 59 as a lump of an appropriate size and collected into the container 26. Since this mass is an alkali salt with high formable hardness, it can be used as a resource as a reinforcing material for concrete. The combustion exhaust gas discharged from the second stage combustion chamber 61 is guided to the heat exchanger 8 by the pipe 28. In the sewage sludge resource recovery apparatus of the present invention, as shown in FIG. A necessary amount of the air is fed through the circulation circuit 12 and is supplied to the drying oven 4 as a drying gas. In the sewage sludge incinerator, a portion of the solids separated by the separation means 5 is supplied to the powder supply means 6 and 6''. Therefore, the gaseous fuel is supplied to the gasification device 21 and taken out from the gas extraction pipe 24 provided at the top of the gasification device 21, and the other part of the solid fraction separated by the separation means 5 is removed. The section supplies the cyclone combustion chamber to the first by means of powder supply means 6 and 6''.
The ash is supplied to the cyclone combustion chamber of the two-stage combustion ash processing device 22 which is a stage combustion chamber, and the gasification device 21
The ash taken out from the ash extraction pipe provided at the bottom of the ash processing device 22 is also supplied to the cyclone combustion chamber of the ash processing device 22, and the water tank provided at the bottom of the cyclone combustion chamber of the ash processing device The ash lumps are taken out from the ash lump container 26, and the combustion exhaust gas from the gasifier 21 and the combustion exhaust gas from the second stage combustion chamber of the ash processing equipment 22 are transferred to the heat exchanger 8 through pipes 27 and 28, respectively. This is a resource recovery device for sewage sludge that is supplied to This resource recovery device not only incinerates sewage sludge, but also recovers gas fuel from the pipe 24 and ash lumps, which serve as aggregate for concrete, as resources by means of their removal.

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

第1図は本出願人および本発明者がさきに開発した下水
汚泥の焼却装置を示す。 第2図は乾燥下水汚泥固体分の組成および揮発分の各温
度における揮発速度を示すグラフである。第3図は本発
明に係る下水汚泥の資源回収装置を示す。第4図.第5
図は本発明の資源回収装置において使用するガス化装置
21の側断面図と平面図である。第6図は本発明の資源
回収装置において使用する灰分の処理装置22の側断面
図ある。1はホッパー、2はスクリュコンベア、3は加
熱器、4は流動砂床を有する下水汚泥乾燥炉、5は分離
手段、6,6″,6″.6″″″は粉体の供給手段、8
は熱交換器、9はフィルター、10は排風機、11は送
風機、12は循環回路、15はドレン分離手段、21は
ガス化装置、22は灰分の処理装置、24はガス取出管
、25は灰分の供給手段、26は灰分塊用容器、27,
28は排ガス管、31はバーナ、32は燃焼室、33は
乾溜室、51は第1サイクロン燃焼室、55はしぼら゛
れた部分、56は水槽、59は灰分塊取出管、61は第
2段燃焼室。
FIG. 1 shows a sewage sludge incinerator previously developed by the present applicant and the present inventor. FIG. 2 is a graph showing the composition of solid components of dried sewage sludge and the volatilization rate of volatile components at various temperatures. FIG. 3 shows a sewage sludge resource recovery device according to the present invention. Figure 4. Fifth
The figures are a side sectional view and a plan view of a gasifier 21 used in the resource recovery apparatus of the present invention. FIG. 6 is a side sectional view of the ash processing device 22 used in the resource recovery device of the present invention. 1 is a hopper, 2 is a screw conveyor, 3 is a heater, 4 is a sewage sludge drying furnace having a fluidized sand bed, 5 is a separation means, 6, 6'', 6''. 6″″″ is a powder supply means, 8
is a heat exchanger, 9 is a filter, 10 is an exhaust fan, 11 is a blower, 12 is a circulation circuit, 15 is a drain separation means, 21 is a gasifier, 22 is an ash processing device, 24 is a gas extraction pipe, 25 is a ash supply means, 26 a container for ash lumps, 27;
28 is an exhaust gas pipe, 31 is a burner, 32 is a combustion chamber, 33 is a dry distillation chamber, 51 is a first cyclone combustion chamber, 55 is a squeezed part, 56 is a water tank, 59 is an ash lump removal pipe, 61 is a second Stage combustion chamber.

Claims (1)

【特許請求の範囲】[Claims] 1 下水汚泥乾燥炉と該下水汚泥乾燥炉の乾燥生成物を
気体分と固体分に分離する分離手段を設け、該分離手段
で分離された固体分に2つの粉体供給手段を設け、1の
粉体供給手段は燃焼室と乾溜室とよりなるガス化装置の
乾溜室に接続され、他の粉体供給手段は第1サイクロン
燃焼室と水槽と第2段燃焼室とよりなる灰分の処理装置
の第1サイクロン燃焼室に接続され該ガス化装置の乾溜
室にガス取出管を設け、該乾溜室で生じる灰分の供給手
段を前記第1サイクロン燃焼室に接続させて設け該第1
サイクロン燃焼室の下部の水槽に灰分塊取出手段を設け
、前記ガス化装置の燃焼室の排ガスと前記灰分の処理装
置の第2段燃焼室の排ガスは熱交換器を通つて排煙する
ようにし、前記分離手段で分離された気体分は送風機と
熱交換器を通つて下水汚泥乾燥炉へ供給するようにした
構造の下水汚泥の質源回収装置。
1. A sewage sludge drying furnace and a separation means for separating the dried product of the sewage sludge drying furnace into a gas component and a solid component are provided, two powder supply means are provided for the solid component separated by the separation means, and 1. The powder supply means is connected to the dry distillation chamber of the gasifier, which includes a combustion chamber and a dry distillation chamber, and the other powder supply means is connected to an ash processing device, which includes a first cyclone combustion chamber, a water tank, and a second stage combustion chamber. A gas extraction pipe is provided in the dry distillation chamber of the gasifier connected to the first cyclone combustion chamber, and a means for supplying ash produced in the dry distillation chamber is connected to the first cyclone combustion chamber.
An ash lump removal means is provided in the water tank at the lower part of the cyclone combustion chamber, and the exhaust gas from the combustion chamber of the gasifier and the exhaust gas from the second stage combustion chamber of the ash treatment device are discharged through a heat exchanger. . A sewage sludge material recovery device constructed such that the gas separated by the separation means is supplied to a sewage sludge drying furnace through a blower and a heat exchanger.
JP56205253A 1981-12-21 1981-12-21 Sewage sludge resource recovery equipment Expired JPS6042368B2 (en)

Priority Applications (6)

Application Number Priority Date Filing Date Title
JP56205253A JPS6042368B2 (en) 1981-12-21 1981-12-21 Sewage sludge resource recovery equipment
US06/415,963 US4507127A (en) 1981-12-21 1982-09-08 System for recovering resources from sludge
DE19823238163 DE3238163A1 (en) 1981-12-21 1982-10-14 SYSTEM FOR RECOVERING RAW MATERIAL FROM SLUDGE
FR8221215A FR2518525B1 (en) 1981-12-21 1982-12-17 DEVICE FOR RECOVERING PRODUCTS AND ENERGY FROM SLUDGE
US06/689,105 US4585463A (en) 1981-12-21 1985-01-07 Concentrator and feeder of sludge for system to recover resources from sludge
US06/689,210 US4583470A (en) 1981-12-21 1985-01-07 Ash disposer for system to recover resources from sludge

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP56205253A JPS6042368B2 (en) 1981-12-21 1981-12-21 Sewage sludge resource recovery equipment

Publications (2)

Publication Number Publication Date
JPS58109198A JPS58109198A (en) 1983-06-29
JPS6042368B2 true JPS6042368B2 (en) 1985-09-21

Family

ID=16503920

Family Applications (1)

Application Number Title Priority Date Filing Date
JP56205253A Expired JPS6042368B2 (en) 1981-12-21 1981-12-21 Sewage sludge resource recovery equipment

Country Status (1)

Country Link
JP (1) JPS6042368B2 (en)

Families Citing this family (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6044719A (en) * 1983-08-22 1985-03-09 Nippon Furnace Kogyo Kaisha Ltd Slag tap type cyclone burning furnace
JPS6044718A (en) * 1983-08-22 1985-03-09 Nippon Furnace Kogyo Kaisha Ltd Slag tap type cyclone burning furnace
JPS60116091A (en) * 1983-11-28 1985-06-22 株式会社日立製作所 automatic cash transaction device
JP4486377B2 (en) * 2004-02-24 2010-06-23 新日鉄エンジニアリング株式会社 Waste melting treatment method using powdery biomass
CN110947735B (en) * 2019-12-16 2020-06-30 广州市醇美环保科技有限公司 Comprehensive treatment method and treatment system for treating wastes with wastes in household garbage and sludge

Also Published As

Publication number Publication date
JPS58109198A (en) 1983-06-29

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