Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JPS607960B2 - Dry sludge gasification equipment - Google Patents
[go: Go Back, main page]

JPS607960B2 - Dry sludge gasification equipment - Google Patents

Dry sludge gasification equipment

Info

Publication number
JPS607960B2
JPS607960B2 JP20525181A JP20525181A JPS607960B2 JP S607960 B2 JPS607960 B2 JP S607960B2 JP 20525181 A JP20525181 A JP 20525181A JP 20525181 A JP20525181 A JP 20525181A JP S607960 B2 JPS607960 B2 JP S607960B2
Authority
JP
Japan
Prior art keywords
gas
combustion chamber
dry distillation
supplied
dry
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
JP20525181A
Other languages
Japanese (ja)
Other versions
JPS58109199A (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 JP20525181A priority Critical patent/JPS607960B2/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 JPS58109199A publication Critical patent/JPS58109199A/en
Priority to US06/689,105 priority patent/US4585463A/en
Priority to US06/689,210 priority patent/US4583470A/en
Publication of JPS607960B2 publication Critical patent/JPS607960B2/en
Expired legal-status Critical Current

Links

Landscapes

  • Gasification And Melting Of Waste (AREA)
  • Treatment Of Sludge (AREA)

Description

【発明の詳細な説明】 〔従来の技術〕 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
棄物であると考えられていた。
DETAILED DESCRIPTION OF THE INVENTION [Prior Art] Previously, 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っ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
焼却を果すシステムを開発し、特許出願をしている(袴
顔昭55一169165)。
The applicant has been conducting research on the incineration of sewage sludge for many years,
He has developed a system that can self-incinerate even low-calorie sewage sludge by skillfully using its own calories and without using too much auxiliary fuel, and has filed a patent application (Hakamagao Sho 55-1169165). ).

本発明の説明に先立って先づ先に特許出願をしたシステ
ムを第1図によって説明する。第1図において、機械的
な脱水法によって水分率90%程度まで脱水された下水
汚泥はホッパ」1内に供給され、該ホッパ−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ヤなどに強
制供給手段2によって先づ下水汚泥加熱器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
の熱によっ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を通る間に該高温の加
熱用気体によって加熱されて流動性になった下水汚泥は
次に流動砂床を有する乾燥炉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って
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
っ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によって段燃焼炉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器3を経て若干低温
に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
いづれかへ燃料として供給する。
Prior to explaining the present invention, the system for which a patent application has been filed will first be explained with reference to FIG. In Figure 1, sewage sludge that has been dehydrated to a moisture content of approximately 90% by mechanical dewatering is supplied into hopper 1, and the sewage sludge in hopper 1 is forced into a screw conveyor installed at the bottom of the hopper. The supply means 2 first supplies the sewage sludge heater 3 to the sewage sludge heater 3, and a part of the gas heated to a high temperature by the heat of the flue gas in the heat exchanger 8, which is a later step, is supplied as a heating gas. The supplied sewage sludge, which has been heated by the high-temperature heating gas while passing through the heater 3 and becomes fluid, is then supplied to a drying furnace 4 having a fluidized sand bed. A necessary amount of the gas heated to a high temperature by the heat of the flue gas in the heat exchanger 8, which is a process, is supplied as drying gas, and the dried product of the drying oven is separated into solids and gas by the separation means 5. The solid content is supplied to the stage combustion furnaces 7, 7' by the powder supply means 6, and the heating gas supplied to the heater 3 is cooled to a slightly lower temperature through the heater 3 and taken out. However, this gas is removed by drain separation means 15.
After removing the condensate, the fuel is supplied as fuel to either of the two-stage combustion furnaces 7 and 7'.

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子熱器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
生成ガスは先づ熱交換器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を通って灰分を除去し、貞
三風送風機10を通して9E風される。前記分離手段5
によって分離された気体分は送風機11を通って昇圧さ
れた前記熱交換器8によって加熱されて循環配管12を
通って気送され、必要量の高圧・高温気体が前記乾燥炉
4へ乾燥用気体として供給され、該必要量を乾燥炉へ供
給した残の気体分は前記加熱器3へ下水汚泥の加熱用気
体として供給されるシステムである。しかしながらその
後の研究によって下水汚泥は潜在的に多くの資源が含ま
れているから単に焼却して処理すべきものでなく、下水
汚泥の乾燥によって生じる乾燥生成物を農業用±穣改良
材としてあるし、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して供
するなど種々の資源として有効に利用できることが判明
されており、前記下水汚泥の焼却システムの2段燃焼炉
7に代え本発明に係る乾燥汚泥の・ガス化装置が開発さ
れる次第となった。
The combustion air to be supplied to the combustion furnaces 7 and 7' is
After being preheated through an air heater 14 provided as a jacket for the combustion chamber 1, it is supplied to the two-stage combustion furnaces 7, 7'. The combustion generated gas from the combustion furnace 7' is first supplied to a heat exchanger 8 for heat exchange to lower the temperature to a slightly lower temperature, then passed through a filter 9 to remove ash, and then passed through a Teizan blower 10 to be blown 9E. The separation means 5
The separated gas passes through the blower 11 and is heated by the heat exchanger 8, which raises the pressure, and is air-fed through the circulation pipe 12, and the required amount of high-pressure and high-temperature gas is sent to the drying oven 4 as a drying gas. After the required amount is supplied to the drying oven, the remaining gas is supplied to the heater 3 as a gas for heating the sewage sludge. However, subsequent research has shown that sewage sludge contains many latent resources, so it should not simply be incinerated and disposed of, but that the dried product produced by drying sewage sludge can be used as a soil improver for agriculture. is used as a raw material to produce gas fuel.
Alternatively, it has been found that the ash can be effectively used as various resources, such as by turning the ash into lumps and providing it as aggregate for cement. - Gasification equipment was developed.

〔目 的〕〔the purpose〕

本発明は乾燥炉4によって生じた生成物を分離手段5に
よって分離し、この分離によって得られた下水汚泥乾燥
生成物をさらに灰分とガス分とに分離しガス燃料を回収
する装置に関する。
The present invention relates to an apparatus for separating the product produced by the drying oven 4 by the separating means 5, further separating the dried sewage sludge product obtained by this separation into ash and gas, and recovering gaseous fuel.

〔発明の構成〕[Structure of the invention]

本発明の乾燥汚泥のガス化装置をその実施例を示した第
2図、第3図によって説明する。
The dry sludge gasification apparatus of the present invention will be explained with reference to FIGS. 2 and 3 showing an embodiment thereof.

第2図において中軸部下部にガスバーナ21を設けるM
談ガスバーナ21の周囲に丈の高い円筒形の燃焼室22
を設ける。
In Fig. 2, a gas burner 21 is provided at the lower part of the center shaft M
A tall cylindrical combustion chamber 22 is located around the gas burner 21.
will be established.

該燃焼室の外周部に乾溜室23を設ける。該乾溜室の外
周部を保温材24で包んで保温する。丈の高い円筒形の
燃焼室22はこの外周壁が回転するように回転手段25
を設ける。
A dry distillation chamber 23 is provided at the outer periphery of the combustion chamber. The outer periphery of the dry distillation chamber is wrapped with a heat insulating material 24 to keep it warm. The tall cylindrical combustion chamber 22 has a rotating means 25 so that its outer peripheral wall rotates.
will be established.

従って燃焼室外周壁は0.8pm乃至公pm程度のゆる
い速度で回転する。該外周壁外側に数個の外向きにした
濃浮羽根26,26′・・・・・・を設ける。この縄浮
羽根によって乾溜室23内において上部から供給された
乾燥汚泥は縄押され、該乾溜室下部から供給される過熱
水蒸気およびその他の気体とよく混合され、従ってガス
発生が活発になる。また該燃焼室22の上部には、第3
図の平断面図で示すごとく、数牧の内側向きに突出させ
て数枚の伝熱フィン27,27′・・・・・・を設ける
。この内側向き伝熱フィンによって燃焼室の発熱の乾溜
室23への熱伝導の効率の向上を図ることができ、該伝
熱フィンの取付位置の外側のすなわち乾溜室の比較的高
い位置において700午0の雰囲気にすることができる
。該燃焼室22の頂部に断熱材28で囲って燃焼排ガス
排出管29を設ける。該管から排出された燃焼排ガスは
前記熱交換器8へ供給される。燃焼室22の外周部に設
ける該乾溜室23の頂部に乾燥下水汚泥固体分の供給手
段30を設ける。乾燥汚泥はこの供聯合手段30によっ
て毎時恒量づっ乾溜室へ供給される。該乾溜室23の下
部に過熱蒸気と空気の混合など揮発促進用気体の供給管
31を設ける。該乾溜室23の底部に灰分取出部32を
設ける。灰分はこの灰分取出部32によって毎時恒量づ
つ係外に取出される。該乾溜室23の頂部に乾溜ガス燃
料の取出管33を設ける。〔本発明の作用効果〕本発明
の乾燥汚泥のガス化装置は上述の構造のものであって、
第1図における分離手段5によって取出される乾燥下水
汚泥固体分が供給される。
Therefore, the outer circumferential wall of the combustion chamber rotates at a slow speed of about 0.8 pm to about 100 pm. Several thick floating blades 26, 26', . . . facing outward are provided on the outside of the outer peripheral wall. Dried sludge supplied from the upper part of the dry distillation chamber 23 is rope-pushed by the rope floating blades and mixed well with superheated steam and other gases supplied from the lower part of the dry distillation chamber 23, so that gas generation becomes active. Additionally, a third
As shown in the plan sectional view of the figure, several heat transfer fins 27, 27', . These inwardly directed heat transfer fins can improve the efficiency of heat transfer from the combustion chamber to the dry distillation chamber 23. It is possible to create an atmosphere of 0. A combustion exhaust gas exhaust pipe 29 is provided at the top of the combustion chamber 22 surrounded by a heat insulating material 28. The combustion exhaust gas discharged from the pipe is supplied to the heat exchanger 8. At the top of the dry distillation chamber 23 provided on the outer periphery of the combustion chamber 22, a means 30 for supplying dried sewage sludge solids is provided. Dried sludge is supplied by this coupling means 30 to the drying chamber at a constant rate every hour. A supply pipe 31 for a gas for promoting volatilization, such as a mixture of superheated steam and air, is provided in the lower part of the dry distillation chamber 23. An ash extraction section 32 is provided at the bottom of the dry distillation chamber 23. A constant amount of ash is removed every hour by the ash removal section 32. A dry distillation gas fuel take-out pipe 33 is provided at the top of the dry distillation chamber 23. [Operations and effects of the present invention] The dry sludge gasification apparatus of the present invention has the above-mentioned structure,
The dry sewage sludge solids removed by the separating means 5 in FIG. 1 is supplied.

この乾燥汚泥はその直径が0.2肋あるいはそれ以下の
微粒子状乃至粉末状であって、水分率5%以下に乾燥さ
せているが、これらが本ガス発生室23の頂部に設けた
供給手段30‘こよってほぼ恒量づつ供給される。第4
図は供給される乾燥汚泥の成分および乾溜特性を示すグ
ラフである。
This dried sludge is in the form of fine particles or powder with a diameter of 0.2 or less, and is dried to a moisture content of 5% or less. 30' is thus supplied in a nearly constant amount. Fourth
The figure is a graph showing the components and dry distillation characteristics of the supplied dried sludge.

第4図に示すごとく、乾燥汚泥の約50%は灰分であっ
て、乾溜の結果取出される灰分はNaやKを塩として可
成多量含量するSi02,AI203を主成分とするア
ルカリ塩である。これらは本装置の灰敬出部32からほ
ぼ恒量づつ取出される。灰分を除いた残りの大部分量す
なわち約45%量が揮発分であり約5%量が固定炭素分
である。
As shown in Figure 4, about 50% of dried sludge is ash, and the ash extracted as a result of dry distillation is an alkali salt whose main components are Si02 and AI203, which contain considerable amounts of Na and K as salts. . These are taken out in almost constant amounts from the ash removal section 32 of this device. After removing the ash content, most of the remaining content, ie, about 45%, is volatile content, and about 5% is fixed carbon content.

なお第4図はこの揮発分は700%乃至500qoの乾
溜室23内の雰囲気において約1.流ご滞溜させること
によってほとんどの揮発分を乾溜させることができ、5
00午0以下では乾溜は円滑でないことを示している。
本発明のガス化装置においては乾燥汚泥が常に乾溜室2
3の上部すなわち伝熱フィンの上端位置にその表面があ
るように乾燥汚泥が供給され灰分が取り出されかつ乾燥
汚泥は該乾溜室23内に約10分間滞在するように供給
される。
In addition, FIG. 4 shows that this volatile matter is about 1.0% in the atmosphere in the dry distillation chamber 23 of 700% to 500qo. Most of the volatile matter can be dry distilled by accumulating in a stream, and 5
This indicates that dry distillation is not smooth below 00:00.
In the gasifier of the present invention, dry sludge is always kept in the dry distillation chamber 2.
Dry sludge is supplied so that its surface is at the top of the heat transfer fins 3, that is, at the upper end of the heat transfer fins, and the ash is removed.

該乾溜室23内はその下部の方がその上部より温度が高
いのであるが燃焼室22側に伝熱フィンを設けることに
よってガスバーナの燃焼室は120ぴ0であるが乾溜室
の乾燥汚泥堆積部分を500℃乃至70ぴ○雰囲気に保
つことができる。なお該乾溜室23内においては揮発促
進用の過熱蒸気が供v給され縄浮羽根による蝿拝が行な
われ、従って乾燥汚泥を揮発分と灰分とに分解・乾溜す
ることができる。該乾溜室の乾溜ガス燃料取出管33か
ら取出されたガス燃料の一部は本発明の装置のガスバー
ナー21へ供給される場合があり、また燃料資源として
発電用や暖房用に使用することができ、ボイラーに供給
して過熱蒸気を作ることもできる。
The lower part of the dry distillation chamber 23 has a higher temperature than the upper part, but by providing heat transfer fins on the combustion chamber 22 side, the combustion chamber of the gas burner has a temperature of 120 mm, but the dry sludge accumulation part of the dry distillation chamber can be maintained in an atmosphere of 500°C to 70p○. In addition, in the dry distillation chamber 23, superheated steam for promoting volatilization is supplied, and a floating rope is used to perform the fly worship, so that the dried sludge can be decomposed and dry distilled into volatile matter and ash. A part of the gas fuel taken out from the dry distillation gas fuel extraction pipe 33 of the dry distillation chamber may be supplied to the gas burner 21 of the apparatus of the present invention, and may also be used as a fuel resource for power generation or heating. It can also be supplied to a boiler to create superheated steam.

該乾溜室の灰分取出部32から取出される灰分は別に乾
燥汚泥灰分の処理装置によってコンクリートの砂利代用
品にすることができる。
The ash extracted from the ash extraction section 32 of the dry distillation chamber can be used as a gravel substitute for concrete by a separate dry sludge ash processing device.

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

第1図は本発明の出願人、および発明者が先に特許出願
し開発をした下水汚泥の焼却システムを示す。 第2図は本発明の乾燥下水汚泥固体分のガス化装置を示
す正断面図。第3図は第2図のガス化菱鷹の平断面図で
ある。第4図は本ガス化装置に供v給される乾燥下水汚
泥固体分の成分および乾溜特性を示すグラフである。2
1はガスバーナ、22は燃焼室、23は乾溜室、24は
保温材、25は燃焼室周壁の回転手段、26は礎梓羽根
、27は伝熱用フィン、28は断熱材、29は燃焼排ガ
ス排出管、30は乾燥下水汚泥固体分の供v給手段、3
1は揮発促進用気体供給管、32は灰分取出部、33は
ガス取世管。 紫1図 潔Z図 第3図 新4図
FIG. 1 shows a sewage sludge incineration system that the applicant and inventor of the present invention previously applied for a patent and developed. FIG. 2 is a front sectional view showing the dry sewage sludge solid gasification apparatus of the present invention. FIG. 3 is a plan cross-sectional view of the gasifier Hishitaka shown in FIG. 2. FIG. 4 is a graph showing the components and dry distillation characteristics of the dried sewage sludge solids supplied to the present gasifier. 2
1 is a gas burner, 22 is a combustion chamber, 23 is a dry distillation chamber, 24 is a heat insulating material, 25 is a means for rotating the peripheral wall of the combustion chamber, 26 is a foundation blade, 27 is a heat transfer fin, 28 is a heat insulating material, and 29 is a combustion exhaust gas a discharge pipe, 30 a supply means for dry sewage sludge solids;
1 is a gas supply pipe for promoting volatilization, 32 is an ash extraction section, and 33 is a gas transfer pipe. Purple 1st figure Jie Z figure 3rd figure New 4th figure

Claims (1)

【特許請求の範囲】[Claims] 1 中軸部下部にガスバーナ21を設け、その周囲に丈
の高い円筒形の燃焼室22を設け、該燃焼室の外周部に
乾溜室23を設け、該燃焼室22の外周壁を回転させる
回転手段25を設け、該燃焼室外周壁に固着させて外向
きに突出させて撹拌羽根数枚26,26′……を設け、
内向きに突出させて伝熱用フイン27,27′……を設
け、該乾溜室23の頂部に乾燥下水汚泥の供給手段30
を設け、下部に揮発促進用気体供給管31を設け、底部
に灰分取出部32を設け、頂部に乾溜ガス燃料の取出管
3を設け、該燃焼室22の頂部に燃焼排ガス排出管29
を設けた構造の乾燥汚泥のガス化装置。
1. A gas burner 21 is provided at the lower part of the central shaft portion, a tall cylindrical combustion chamber 22 is provided around the gas burner 21, a dry distillation chamber 23 is provided on the outer periphery of the combustion chamber, and a rotating means for rotating the outer peripheral wall of the combustion chamber 22. A stirring blade 25 is provided, and several stirring blades 26, 26' are provided by being fixed to the outer peripheral wall of the combustion chamber and protruding outward,
Heat transfer fins 27, 27', .
A gas supply pipe 31 for promoting volatilization is provided at the bottom, an ash removal section 32 is provided at the bottom, a dry distillation gas fuel removal pipe 3 is provided at the top, and a combustion exhaust gas discharge pipe 29 is provided at the top of the combustion chamber 22.
A dry sludge gasification device with a structure equipped with.
JP20525181A 1981-12-21 1981-12-21 Dry sludge gasification equipment Expired JPS607960B2 (en)

Priority Applications (6)

Application Number Priority Date Filing Date Title
JP20525181A JPS607960B2 (en) 1981-12-21 1981-12-21 Dry sludge gasification 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
JP20525181A JPS607960B2 (en) 1981-12-21 1981-12-21 Dry sludge gasification equipment

Publications (2)

Publication Number Publication Date
JPS58109199A JPS58109199A (en) 1983-06-29
JPS607960B2 true JPS607960B2 (en) 1985-02-28

Family

ID=16503887

Family Applications (1)

Application Number Title Priority Date Filing Date
JP20525181A Expired JPS607960B2 (en) 1981-12-21 1981-12-21 Dry sludge gasification equipment

Country Status (1)

Country Link
JP (1) JPS607960B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS60179491A (en) * 1984-02-24 1985-09-13 Ataka Kogyo Kk Conversion of organic sludge to energy
KR101017454B1 (en) 2010-09-01 2011-02-25 오수록 Wet waste carbonization unit
CN108624345A (en) * 2018-07-10 2018-10-09 济源润万家农业科技有限公司 Stalk, agriculture and forestry organic waste material refine combustible gas and charcoal equipment and method

Also Published As

Publication number Publication date
JPS58109199A (en) 1983-06-29

Similar Documents

Publication Publication Date Title
US4583470A (en) Ash disposer for system to recover resources from sludge
US4295281A (en) Drying solid materials
CN105948459A (en) Method using drying and incineration to treat sludge
US4291539A (en) Power generation system
US4232614A (en) Process of incineration with predrying of moist feed using hot inert particulates
US4516511A (en) Refuse incineration system
RU1838635C (en) Method of generation of electric and thermal energy
US5103743A (en) Method and apparatus for drying solid material
JPS6027895B2 (en) Method for drying and burning hydrated solid fuel
PL86087B1 (en)
GB2155599A (en) Improved refuse incineration system
JPS607960B2 (en) Dry sludge gasification equipment
SU1695091A1 (en) Fuel drying and combustion plant
DK142311B (en) Process for producing cement clinker of raw sludge and plant for carrying out the process.
CN109611870A (en) A kind of sludge shaft furnace incineration treatment method and device
JPS6042368B2 (en) Sewage sludge resource recovery equipment
JPH01213492A (en) Combustion of black liquor
US2777288A (en) Process and apparatus for the generation of mechanical energy from solid fuels having a high water content
EP3830481A1 (en) System and method for reducing volume of sewage sludge
SU1754760A1 (en) Method for thermal processing of high-ash fuel
JPS58106317A (en) Treating apparatus for dry sludge ash content
JPS6157964B2 (en)
EP0613867B1 (en) Method for manufacturing a pozzolanic material from paper sludge
JP3666940B2 (en) How to make sewage sludge into cement
JPS636319A (en) Fine powder coal boiler