JPH0762597B2 - Hot air generator - Google Patents
Hot air generatorInfo
- Publication number
- JPH0762597B2 JPH0762597B2 JP13359491A JP13359491A JPH0762597B2 JP H0762597 B2 JPH0762597 B2 JP H0762597B2 JP 13359491 A JP13359491 A JP 13359491A JP 13359491 A JP13359491 A JP 13359491A JP H0762597 B2 JPH0762597 B2 JP H0762597B2
- Authority
- JP
- Japan
- Prior art keywords
- air
- waste gas
- heat
- gas
- incinerator
- 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
Links
Landscapes
- Incineration Of Waste (AREA)
- Heat-Exchange Devices With Radiators And Conduit Assemblies (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は、汚泥や粕等の水分の多
い材料を焼却する場合、さらに、これらの材料を用いて
堆肥を製造する行程において、発生する高温多湿の廃棄
ガス中の熱エネルギーを再利用するための熱風発生装置
に関するものである。BACKGROUND OF THE INVENTION The present invention is applied to the case of incinerating materials having a large amount of water such as sludge and dregs, and further, in the process of producing compost using these materials, the heat generated in the high-temperature and high-humidity waste gas is generated. The present invention relates to a hot air generator for reusing energy.
【0002】[0002]
【従来の技術】従来、水分の多い材料の発酵や焼却の過
程においては、水分の蒸発に熱を奪われるために、焼却
や発酵が順調に進まないのは周知の通りである。このた
め、焼却の場合には、高圧の圧力窯の中で焼却して水分
の蒸発を抑えたり、また、燃焼ガスを用いて予め汚泥を
乾燥させたり、或は、廃棄ガスと供給空気とを熱交換し
たりして対策を立てていた。なお、熱交換によるものに
は、図3に示すようにヒートポンプ1を利用した室内2
の暖房装置がある。この装置はフロン等の冷媒を圧縮機
3、凝集器4を含む循環回路に封入したもので、送風機
5によって空気を凝集器4内を通過させて室内に暖気を
送るようにしている。また、湿度が多い場合には換気装
置を併用することがある。2. Description of the Related Art It is well known that, in the process of fermentation or incineration of a material having a large amount of moisture, heat is taken away by evaporation of moisture so that the incineration or fermentation does not proceed smoothly. For this reason, in the case of incineration, it is incinerated in a high-pressure pressure kiln to suppress the evaporation of water, or the sludge is dried in advance using combustion gas, or waste gas and supply air are mixed. I was taking measures by exchanging heat. In addition, as shown in FIG. 3, a room 2 using a heat pump 1 is used for heat exchange.
There is a heating system. In this device, a refrigerant such as Freon is enclosed in a circulation circuit including a compressor 3 and a flocculator 4, and air is passed through the flocculator 4 by a blower 5 to send warm air to the room. When the humidity is high, a ventilation device may be used together.
【0003】[0003]
【発明が解決しようとする課題】ところで、前述した廃
棄ガスと空気との熱交換器においては、廃棄ガスを熱交
換器の一次側とし空気を二次側としたときに、単に接触
させただけでは、出力として、廃棄ガスよりも高温の空
気は得られない。この二次空気を焼却炉に還元しても、
焼却による発熱量が余程多くなければ、廃棄ガスの温度
が徐々に低下する事は避けられず、従って、含水率の大
きな汚泥の焼却作業は困難である。なお、フロンを利用
したのでは高価で不経済であり、また、環境破壊、気温
の高低による作動不良の問題がある。In the heat exchanger for waste gas and air described above, when the waste gas is used as the primary side of the heat exchanger and the air is used as the secondary side, they are simply contacted with each other. Then, as the output, air having a temperature higher than that of the waste gas cannot be obtained. Even if this secondary air is returned to the incinerator,
If the amount of heat generated by incineration is not so large, it is inevitable that the temperature of the waste gas will gradually decrease, and therefore it is difficult to incinerate sludge having a high water content. It should be noted that the use of CFC is expensive and uneconomical, and there is a problem of malfunction due to environmental damage and high and low temperatures.
【0004】本発明は、フロン等の触媒を使用せず、焼
却や発酵の促進を図るために、廃棄ガス中の熱エネルギ
ーを回収して高温化した空気を送気する熱風発生装置を
提供することを目的とする。The present invention provides a hot air generator for recovering thermal energy in waste gas and sending hot air to promote incineration and fermentation without using a catalyst such as Freon. The purpose is to
【0005】[0005]
【課題を解決するための手段】上記目的を達成するため
に、本発明は、内筒と外筒を有し、内筒の内部に空気タ
ービンを配設すると共に内筒の一端部にターボ圧縮機を
配設し、該一端部側に焼却炉等に送気する送気ガスの送
気管を連接し、焼却炉等から放出された廃棄ガスを流す
送風管を、内筒と外筒との間に形成した廃棄ガス流路の
前記一端部側に連接したことを特徴とする。本発明で
は、高温の廃棄ガスを扱うことにより、廃棄ガスを加圧
して熱交換を行なう方法は取らず、空気を減圧して熱交
換を行なうようにしている。また、熱交換器の保護のた
めに、大気から得た空気と廃棄ガスを反対方向に流しな
がら大気圧下において熱交換し、さらに、空気を減圧し
た状態で熱交換を行ない、その後、大気圧に戻して送気
ガスを発生させる手段を用いる。また、空気タービンと
ターボ圧縮機とを共通の動力源に連係させるという手段
を用いる。In order to achieve the above object, the present invention has an inner cylinder and an outer cylinder, an air turbine is disposed inside the inner cylinder, and a turbo compression is provided at one end of the inner cylinder. A machine is provided, and an air supply pipe for supplying air to an incinerator or the like is connected to the one end side, and a blower pipe for flowing the waste gas discharged from the incinerator or the like is provided between the inner cylinder and the outer cylinder. It is characterized in that it is connected to the one end portion side of the waste gas flow channel formed therebetween. In the present invention, by handling the high temperature waste gas, the method of pressurizing the waste gas for heat exchange is not adopted, but the air is depressurized for heat exchange. In order to protect the heat exchanger, heat exchange is performed under atmospheric pressure while air and waste gas obtained from the atmosphere flow in opposite directions, and heat is exchanged while the air is depressurized. And a means for generating the gas to be sent is used. Also, a means is used in which the air turbine and the turbo compressor are linked to a common power source.
【0006】[0006]
【作用】上記の構成によって、先ず、内筒内に吸気され
る空気と、内筒と外筒との間を進んで来た高温多湿の廃
棄ガスとが熱交換される。この箇所で加熱された送気ガ
スは内部に進み空気タービンを通過して減圧され冷却さ
れた状態になる。この状態において廃棄ガスにより再度
加熱される。さらに、ターボ圧縮機を用いて圧縮されて
大気圧に戻り、廃棄ガスよりも高い温度の乾燥した熱風
(送気ガス)となる。なお、減圧時に水蒸気が凝結する
と、温度が低下しにくくなるので不経済となるが、減圧
前に大気圧下において余熱されているので水蒸気が凝結
する事はない。また、送気ガスと廃棄ガスの流れが反対
方向で有るので、送気ガスは熱交換の最終段階におい
て、初めて熱交換に参加する新手の廃棄ガスに加熱され
て、廃棄ガスとほぼ等しい温度となり、その後ターボ圧
縮機により圧縮されてほぼ大気圧に戻される際に更に温
度が上昇するので、得られた送気ガスの温度は必ず廃棄
ガスよりも高くなる。With the above structure, first, the air sucked into the inner cylinder and the hot and humid waste gas that has advanced between the inner cylinder and the outer cylinder are heat-exchanged. The insufflation gas heated at this point proceeds inside, passes through the air turbine, and is decompressed and cooled. In this state, the waste gas is heated again. Furthermore, it is compressed using a turbo compressor to return to atmospheric pressure, and becomes dry hot air (air supply gas) having a temperature higher than that of the waste gas. It is uneconomical if steam condenses during depressurization because the temperature is less likely to drop, but since steam is preheated under atmospheric pressure before depressurization, steam does not condense. In addition, since the flow of the air supply gas and the flow of the waste gas are in opposite directions, the air supply gas is heated by the new waste gas that participates in the heat exchange for the first time at the final stage of heat exchange, and the temperature becomes almost equal to that of the waste gas. However, since the temperature further rises when it is compressed by the turbo compressor and returned to almost atmospheric pressure, the temperature of the obtained gas is always higher than that of the waste gas.
【0007】勿論、廃棄ガスの温度は、減圧空気、常圧
空気により熱交換が行なわれるので、大気中に放出され
るときには外気よりも若干高い。なお、水蒸気の凍結を
回避するために放出時に零度以上でなければならない
が、送気ガスの熱量は廃棄ガスよりも幾分少ないので、
100パーセント廃棄ガスの熱が回収される訳ではな
く、燃焼や発酵に伴う発熱が有るので多少の損失は許容
し得る。Of course, the temperature of the waste gas is a little higher than that of the outside air when it is released into the atmosphere because heat exchange is performed by the depressurized air and the atmospheric pressure air. In addition, in order to avoid freezing of water vapor, it must be above zero at the time of discharge, but since the calorific value of the insufflation gas is somewhat smaller than the waste gas,
Since 100% of the heat of waste gas is not recovered and there is heat generated by combustion and fermentation, some loss can be tolerated.
【0008】[0008]
【実施例】以下、本発明の実施例を添付図面に基づいて
説明する。一例として、図2に示すように、熱風発生装
置6を焼却炉7と併設した場合について述べる。焼却炉
7は円筒状に乾燥室7aを形成しており、天井部にパラ
ボラ状の衝突板8が設けられている。衝突板8の焦点部
には上半分に多数の孔を均一に開けた散泥球9が設置さ
れている。また、乾燥室7a下部には、外周縁を側壁に
固着し中央が低く中心に孔の開いた円錐状のシュート1
0が設けられ、中心位置に一面に棘の生えた燃焼ブロッ
ク11が設けられている。燃焼ブロック11の上方には
円錐状の遮蔽板12が設けられている。シュート10と
遮蔽板12の勾配は乾燥した粉末が滑り落ちるように十
分に大きくされている。そして、燃焼ブロック11の周
囲にバーナー13が設けられている。この発熱量は汚泥
の燃焼による発熱量よりも十分に大きくされ、燃焼ブロ
ック11の面積はなるべく小さくされている。Embodiments of the present invention will be described below with reference to the accompanying drawings. As an example, as shown in FIG. 2, a case where the hot air generator 6 is installed together with the incinerator 7 will be described. The incinerator 7 has a cylindrical drying chamber 7a, and a parabolic collision plate 8 is provided on the ceiling. At the focal point of the collision plate 8, a spattering ball 9 having a large number of holes uniformly formed in the upper half is installed. Further, in the lower part of the drying chamber 7a, a conical chute 1 having an outer peripheral edge fixed to the side wall and having a low center and a hole at the center is formed.
0 is provided, and a combustion block 11 having a barbed surface is provided at the central position. A conical shielding plate 12 is provided above the combustion block 11. The gradient between the chute 10 and the shield 12 is made large enough for the dry powder to slip off. A burner 13 is provided around the combustion block 11. This calorific value is made sufficiently larger than the calorific value due to the combustion of sludge, and the area of the combustion block 11 is made as small as possible.
【0009】焼却炉7の天井部に位置する散泥球9は送
泥管14と連通され、送泥装置15の貯溜槽16内に設
置した送泥ポンプ17と接続されている。The mud ball 9 located on the ceiling of the incinerator 7 is connected to the mud feed pipe 14 and is connected to the mud feed pump 17 installed in the storage tank 16 of the mud feed device 15.
【0010】また、焼却炉7の上部周壁には吸気リング
18が設けられ、吸気管19を介して散水装置20の散
水室21上部と連通されている。散水室21は多数の孔
が万遍なく上向きに空けられた多数の散水管22を天井
に配設しており、それぞれの孔の上方に弧状の衝突板2
3が装着されている。また、散水室21下部に送風管2
4の一端が接続され、その他端は熱風発生装置6の外筒
25と内筒26との間の流路に開口されており、送風管
24の管路途中に送風機27が設けられている。An intake ring 18 is provided on the upper peripheral wall of the incinerator 7, and is connected to the upper part of the water spray chamber 21 of the water spray device 20 via an intake pipe 19. The water sprinkling chamber 21 has a large number of water sprinkling pipes 22 in which a large number of holes are evenly opened upward, and the arc-shaped collision plate 2 is provided above each hole.
3 is installed. Further, the blower pipe 2 is provided below the sprinkling chamber 21.
4 is connected to one end, and the other end is opened to the flow path between the outer cylinder 25 and the inner cylinder 26 of the hot air generator 6, and a blower 27 is provided in the middle of the duct of the blower pipe 24.
【0011】一方、焼却炉7の乾燥室7aの下部周壁に
送気リング28が設けられ、その下方のシュート10の
内縁の下面に送風リング29が設けられている。送気リ
ング28は送気管30と接続され、送風リング29は風
量調節弁31を介して送気管30と接続されている。そ
して、送気管30は外筒25内を貫通する内筒26の、
送風管24を取付けた側に接続されており、内筒26の
他端は大気中に開口されている。On the other hand, an air supply ring 28 is provided on the lower peripheral wall of the drying chamber 7a of the incinerator 7, and an air supply ring 29 is provided on the lower surface of the inner edge of the chute 10 below the air supply ring 28. The air supply ring 28 is connected to the air supply pipe 30, and the air supply ring 29 is connected to the air supply pipe 30 via an air volume control valve 31. Then, the air supply pipe 30 of the inner cylinder 26 penetrating the inside of the outer cylinder 25,
It is connected to the side to which the blower pipe 24 is attached, and the other end of the inner cylinder 26 is open to the atmosphere.
【0012】次は、熱風発生装置6の構成について説明
する。図1に示すように、内筒26の外周には中空の螺
旋状の吸熱リング32が連設され、吸熱リング32の山
側と外筒25内周面との間に、同じく螺旋状のフィン3
3が固着されている。また、吸熱リング32の谷側(内
筒26の内周面)と芯材34との間に螺旋状の邪魔板3
5が固着されている。そして、フィン33により区切ら
れた外筒25の底の各区画には、排水管36から分岐し
た各一端が開口し、排水管36の他端は排水槽37の底
面近くに開口され、排水槽37の水深は外筒25内の気
圧に応じて十分に大きくされている。また、内筒26の
中程に空気タービン38が配置され、末端にターボ圧縮
機39が設けられており、互いの回転軸を同軸にして外
部に突出され、これらは一つのモーター40と変速機4
1に連結されている。Next, the structure of the hot air generator 6 will be described. As shown in FIG. 1, a hollow spiral heat absorbing ring 32 is continuously provided on the outer circumference of the inner cylinder 26, and the spiral fin 3 is also provided between the mountain side of the heat absorbing ring 32 and the inner peripheral surface of the outer cylinder 25.
3 is fixed. The spiral baffle plate 3 is provided between the core 34 and the valley side of the heat absorbing ring 32 (the inner peripheral surface of the inner cylinder 26).
5 is fixed. Then, one end branched from the drain pipe 36 is opened in each section of the bottom of the outer cylinder 25 divided by the fins 33, and the other end of the drain pipe 36 is opened near the bottom surface of the drain tank 37. The water depth of 37 is made sufficiently large according to the atmospheric pressure in the outer cylinder 25. Further, an air turbine 38 is arranged in the middle of the inner cylinder 26, and a turbo compressor 39 is provided at the end, and they are projected to the outside with their rotation axes being coaxial, and these are one motor 40 and a transmission. Four
It is connected to 1.
【0013】上記の空気タービン38による減圧の程度
は汚泥等が燃料を要せずに燃焼し得るようになる送気の
温度から決定され、また空気タービン38の位置はその
ように減圧した場合に、空気中の水蒸気が凝結しない限
度内において、なるべく上流におかれている。また、上
記の各装置の外気に接する部分には断熱材が施されてい
る事は言うまでもない。The degree of decompression by the air turbine 38 is determined from the temperature of the air supply which allows sludge or the like to burn without the need for fuel, and the position of the air turbine 38 is determined by such decompression. As far as the water vapor in the air does not condense, it is placed as upstream as possible. Further, it goes without saying that a heat insulating material is applied to a portion of each of the above devices that is in contact with the outside air.
【0014】次は作用について説明する。先ず、熱風発
生装置6で発生した空気(以下、送気ガスと言う。)は
焼却炉7内に送られ、焼却炉7内で発生した燃焼ガスと
入り混じって百度以上の高温多湿の空気(以下、廃棄ガ
スと言う。)になる。廃棄ガスは吸気リング18から吸
気管19を通って散水装置20の散水室21内に流入さ
れる。散水室21内では、散水管22の孔から吹き出し
衝突板に当たって微細になった水滴が落下することによ
って、廃棄ガス中の煤煙が洗い流される。清浄された廃
棄ガスは、熱風発生装置6の汚れを少なくし、煤煙によ
る大気汚染の問題も生じない。なお、焼却炉7の乾燥室
7a内において、後述の通りに汚泥が確実に瞬時に乾燥
するために、廃棄ガスの温度が100度以上となるが、
散水室21内において、水分の蒸発に熱を奪われてその
温度は100度以下となるので、取り扱いも楽になる。Next, the operation will be described. First, the air generated by the hot air generator 6 (hereinafter, referred to as air supply gas) is sent into the incinerator 7 and mixed with the combustion gas generated in the incinerator 7 to mix with the hot and humid air of 100 degrees or more ( Hereinafter referred to as waste gas). The waste gas flows from the intake ring 18 through the intake pipe 19 into the water spray chamber 21 of the water spray device 20. In the water spray chamber 21, the soot and smoke in the waste gas are washed away by the water droplets that have become fine and have hit the collision plate through the holes of the water spray pipe 22. The cleaned waste gas reduces fouling of the hot air generator 6 and does not cause the problem of air pollution due to soot. In addition, in the drying chamber 7a of the incinerator 7, the temperature of the waste gas becomes 100 degrees or more in order to surely dry the sludge instantaneously as described below.
In the sprinkling chamber 21, the heat is taken away by the evaporation of the water and the temperature becomes 100 degrees or less, so that the handling becomes easy.
【0015】送気ガスは熱風発生装置6から焼却炉7に
送られるが、熱風発生装置6では外気がターボ圧縮機3
9に吸引されて内筒26内に入り、内筒26内に入った
空気は邪魔板35に沿って周回して流れる。廃棄ガスは
反対方向から外筒25内のフィン33に沿って周回しな
がら流れ、内筒26、吸熱リング32を介して送気ガス
に熱を伝達する。The blown gas is sent from the hot air generator 6 to the incinerator 7. In the hot air generator 6, the outside air is the turbo compressor 3.
9 is sucked into the inner cylinder 26, and the air that has entered the inner cylinder 26 circulates along the baffle plate 35 and flows. The waste gas flows from the opposite direction while circulating along the fins 33 in the outer cylinder 25, and transfers heat to the gas to be sent through the inner cylinder 26 and the heat absorbing ring 32.
【0016】ここで、廃棄ガスから熱を回収し得る限度
について説明する。上述のように空気が熱せられる一
方、熱する方の廃棄ガスは冷却されるが、焼却炉7の乾
燥室7a内と散水室21内において発生した水蒸気が冷
却されるにつれて凝結し気化の潜熱が放出されて、再び
顕熱に変わり廃棄ガスが冷えにくくなり、送気ガスの加
熱において有効である。これにより、廃棄ガスの温度が
低くなっても送気ガスを加熱することへは影響がない。
なお、大気中に放出される際の廃棄ガス温度が外気と等
しければ、廃棄ガスの熱は100パーセント回収された
事になる。Now, the limit of heat recovery from waste gas will be described. As described above, while the air is heated, the heated waste gas is cooled, but as the steam generated in the drying chamber 7a of the incinerator 7 and the sprinkling chamber 21 is cooled, the latent heat of vaporization is condensed. After being discharged, it becomes sensible heat again and the waste gas becomes difficult to cool, which is effective in heating the gas to be sent. As a result, even if the temperature of the waste gas becomes low, there is no effect on the heating of the gas to be fed.
If the temperature of the waste gas when released into the atmosphere is equal to that of the outside air, 100% of the heat of the waste gas has been recovered.
【0017】廃棄ガスが大気中に放出される際、熱交換
が最後まで有効に行なわれるためには、熱交換を終えて
外筒25の末端から大気中に放出される際の廃棄ガスと
外気との温度差が十分であり、また廃棄ガス中の水蒸気
が凍結しない事が必要である。例えば、外気の温度が零
下10度程度の場合を想定すれば、廃棄ガスと外気の温
度差は十数度になる。従って、廃棄ガスの熱量を100
パーセント回収する事は不可能であり、若干の損失は避
けられない。従って、送気ガスの熱量は廃棄ガスよりも
若干少なくなるが、その損失熱量は、後述の減圧の程度
を大きくして送気ガスの温度を高くし風量を少なくすれ
ば、少なくなる。When the waste gas is released into the atmosphere, in order to effectively perform the heat exchange to the end, the waste gas and the outside air when the heat exchange is finished and released from the end of the outer cylinder 25 into the atmosphere. It is necessary that the temperature difference between and is sufficient and that the water vapor in the waste gas does not freeze. For example, assuming a case where the temperature of the outside air is about 10 degrees below zero, the temperature difference between the waste gas and the outside air is ten and several degrees. Therefore, the calorific value of the waste gas is 100
Percentage recovery is impossible and some loss is inevitable. Therefore, the calorific value of the air supply gas is slightly smaller than that of the waste gas, but the heat loss quantity thereof is decreased by increasing the degree of decompression described later to increase the temperature of the air supply gas and reduce the air volume.
【0018】熱風発生装置6の説明に戻る。内筒26の
入口で予め余熱された送気ガスは、空気タービン38を
通過する。この際に動力が取出され、空気タービン38
とターボ圧縮機39が同一の変速機41に連結されてい
るので、ターボ圧縮機39を駆動するモーター40の出
力を小さくすることができる。また、上記のように減圧
の程度を考慮にいれて予め余熱されているので、送気ガ
ス中の水蒸気が凝結し気化の潜熱が放出されて、減圧に
伴う温度低下の能率が悪くなる事はない。さらに、まだ
外筒25に入ったばかりで、全く冷えていない新手の廃
棄ガスにより約100度近くまで熱せられる。最後に、
ターボ圧縮機39を通過してほぼ大気圧に戻されるの
で、送気管30を通り焼却炉7に送られる送気ガスの温
度は百度を遥かに超える温度となる。Returning to the description of the hot air generator 6. The insufflation gas preheated at the inlet of the inner cylinder 26 passes through the air turbine 38. At this time, power is taken out and the air turbine 38
Since the turbo compressor 39 and the turbo compressor 39 are connected to the same transmission 41, the output of the motor 40 that drives the turbo compressor 39 can be reduced. Further, as described above, since the residual heat is preliminarily taken into consideration in consideration of the degree of decompression, the steam in the insufflation gas is condensed, the latent heat of vaporization is released, and the efficiency of the temperature decrease due to the decompression becomes worse. Absent. Further, the waste gas that has just entered the outer cylinder 25 and has not cooled at all can be heated up to about 100 degrees. Finally,
Since it is returned to the atmospheric pressure after passing through the turbo compressor 39, the temperature of the gas to be sent to the incinerator 7 through the gas pipe 30 becomes a temperature far exceeding 100 degrees.
【0019】上記の熱ポンプの効果の理解を図るため
に、次は焼却炉7関係の作用について説明する。散泥球
9の上半分の孔から飛び出した汚泥は、パラボラ状の衝
突板8に当たり、砕けて小さな水滴となって乾燥室7a
内をほぼ鉛直に落下するが、燃焼ガスと送気リング28
から吹き出した熱風が下から吹き上げるので、水分が瞬
時に蒸発し固形分だけになる。固形分はシュート10と
遮蔽板12の上に舞い降りて、いずれも最後にはシュー
ト10の内縁から滑り落ち、送風調節弁7aにより適当
に風量を調節されて、その下縁の送風リング29から吹
き出す微風に乗って、焼けた燃焼ブロック11部分に集
められて燃焼する。また、上記のとおり風量が適当に調
節されているので、空気によって燃焼ブロック11が徒
らに冷やされる事がなく、燃焼ブロック11の大きさが
適当に小さくされ、しかも熱が逃げないように燃焼部分
が遮蔽板12に覆われているので、燃焼ブロック11の
周囲の部分の温度は極めて高く、従って円滑に燃焼が進
む。このように一段階で乾燥と燃焼が行なえることは、
百数十度の熱風を発生させ得る熱風発生装置6がなけれ
ば不可能である。In order to understand the effect of the above heat pump, the operation related to the incinerator 7 will be described below. The sludge jumping out of the upper half hole of the sludge ball 9 hits the parabolic collision plate 8 and is broken into small water droplets, which is dried in the drying chamber 7a.
Although it falls almost vertically inside, the combustion gas and the air supply ring 28
Since the hot air blown out from the bottom blows up from below, the water instantly evaporates and becomes only solids. The solid content descends on the chute 10 and the shielding plate 12, and finally both slide down from the inner edge of the chute 10 and the air volume is appropriately adjusted by the air blowing control valve 7a, and the solid content is blown out from the air blowing ring 29 at the lower edge. Riding in a breeze, they are collected in the burned combustion block 11 and burned. Moreover, since the air volume is appropriately adjusted as described above, the combustion block 11 is not cooled by air, the size of the combustion block 11 is appropriately reduced, and the combustion is performed so that heat does not escape. Since the portion is covered with the shielding plate 12, the temperature of the portion around the combustion block 11 is extremely high, so that the combustion proceeds smoothly. In this way, drying and burning can be done in one step,
This is impossible without the hot air generator 6 that can generate hot air of a hundred and several tens of degrees.
【0020】また、上記のように送気ガスの熱量は廃棄
ガスよりも若干少ないが、焼却炉7内で発生した燃焼に
より損失熱量が補填されるので、燃焼が続けられる。勿
論、燃焼の開始時においては、バーナー13により加温
する必要が有るが、上記のようにバーナー13の発熱量
が汚泥の焼却による発熱量よりも十分に大きくされてい
るので、徐々に送気ガスの温度が上昇し、間もなく上述
のような正常な運転状態となる。Further, as described above, the amount of heat of the gas to be sent is slightly smaller than that of the waste gas, but since the amount of heat loss is compensated by the combustion generated in the incinerator 7, the combustion is continued. Of course, at the start of combustion, it is necessary to heat with the burner 13, but since the calorific value of the burner 13 is made sufficiently larger than the calorific value due to the incineration of sludge as described above, the air is gradually fed. The temperature of the gas rises and soon the normal operating condition as described above is reached.
【0021】次は、外筒25内において生じた凝結水の
排出作用について説明する。外筒25内は僅かに正圧と
なっているが、これに拮抗して排水管36内の水面は排
水槽37内よりも僅かに低くなっており、また上記の通
り排水槽37の水深が十分に大きくされているので、廃
棄ガスが排水管36から吹き出す事はない。また、加圧
過程において必要となる動力エネルギーの大半を、減圧
過程において回収するので、動力源を節減できるという
効果がある。Next, the discharging action of the condensed water generated in the outer cylinder 25 will be described. Although the positive pressure is slightly inside the outer cylinder 25, the water level inside the drainage pipe 36 is slightly lower than that inside the drainage tank 37 in opposition to this, and the water depth of the drainage tank 37 is as described above. Since it is made sufficiently large, the waste gas does not blow out from the drain pipe 36. Further, most of the power energy required in the pressurizing process is recovered in the depressurizing process, so that the power source can be saved.
【0022】[0022]
【発明の効果】本発明は、以上のように構成したもので
あるから、多量に発生する高温多湿の廃棄ガスの熱エネ
ルギーを回収して、高温低湿の送気ガスを発生させるの
で、従来、水分が多いために多量の燃料を要していた分
野において再利用することができ、燃料の節減を図るこ
とができる。また、熱回収の損失は極めて僅かであり、
焼却炉等に併設した場合、送気ガスの温度を廃棄ガスよ
りも遥かに高くさせ、しかも低湿であるので、送気ガス
をそのまま使用することができ、汚泥等を瞬時に乾燥さ
せて、焼却させる事ができる。EFFECTS OF THE INVENTION Since the present invention is constructed as described above, the thermal energy of waste gas of high temperature and high humidity which is generated in large quantities is recovered to generate the gas of high temperature and low humidity. It can be reused in a field that requires a large amount of fuel due to its high water content, and fuel can be saved. Also, the loss of heat recovery is very small,
When installed in an incinerator, etc., the temperature of the gas to be sent is much higher than that of the waste gas, and since the humidity is low, the gas to be sent can be used as it is, and sludge etc. can be instantly dried and incinerated. You can let me do it.
【図1】本発明にかかる熱風発生装置の構成図である。FIG. 1 is a configuration diagram of a hot air generator according to the present invention.
【図2】汚泥を焼却する焼却炉に併設した熱風発生装置
の全体の構成図である。FIG. 2 is an overall configuration diagram of a hot air generator installed in an incinerator that incinerates sludge.
【図3】従来のヒートポンプの構成図である。FIG. 3 is a configuration diagram of a conventional heat pump.
7…焼却炉 24…送風管 25…外筒 26…内筒 30…送気管 38…空気タービン 39…ターボ圧縮機 7 ... Incinerator 24 ... Blower pipe 25 ... Outer cylinder 26 ... Inner cylinder 30 ... Air pipe 38 ... Air turbine 39 ... Turbo compressor
Claims (1)
ービンを配設すると共に内筒の一端部にターボ圧縮機を
配設し、該一端部側に焼却炉等に送気する送気ガスの送
気管を連接し、焼却炉等から放出された廃棄ガスを流す
送風管を、内筒と外筒との間に形成した廃棄ガス流路の
前記一端部側に連接したことを特徴とする熱風発生装
置。1. An inner cylinder and an outer cylinder, an air turbine is arranged inside the inner cylinder, a turbo compressor is arranged at one end of the inner cylinder, and the turbo compressor is sent to an incinerator or the like at the one end. An air supply pipe for the air supply gas to be connected is connected, and a blower pipe for flowing the waste gas discharged from the incinerator is connected to the one end side of the waste gas flow path formed between the inner cylinder and the outer cylinder. A hot air generator characterized in that.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP13359491A JPH0762597B2 (en) | 1991-05-09 | 1991-05-09 | Hot air generator |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP13359491A JPH0762597B2 (en) | 1991-05-09 | 1991-05-09 | Hot air generator |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH04335931A JPH04335931A (en) | 1992-11-24 |
JPH0762597B2 true JPH0762597B2 (en) | 1995-07-05 |
Family
ID=15108464
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP13359491A Expired - Fee Related JPH0762597B2 (en) | 1991-05-09 | 1991-05-09 | Hot air generator |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH0762597B2 (en) |
-
1991
- 1991-05-09 JP JP13359491A patent/JPH0762597B2/en not_active Expired - Fee Related
Also Published As
Publication number | Publication date |
---|---|
JPH04335931A (en) | 1992-11-24 |
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