JPS6363809B2 - - Google Patents

Info

Publication number
JPS6363809B2
JPS6363809B2 JP14637080A JP14637080A JPS6363809B2 JP S6363809 B2 JPS6363809 B2 JP S6363809B2 JP 14637080 A JP14637080 A JP 14637080A JP 14637080 A JP14637080 A JP 14637080A JP S6363809 B2 JPS6363809 B2 JP S6363809B2
Authority
JP
Japan
Prior art keywords
ash
incinerator
storage tank
dust
soot
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
JP14637080A
Other languages
Japanese (ja)
Other versions
JPS5770315A (en
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 filed Critical
Priority to JP14637080A priority Critical patent/JPS5770315A/en
Publication of JPS5770315A publication Critical patent/JPS5770315A/en
Publication of JPS6363809B2 publication Critical patent/JPS6363809B2/ja
Granted legal-status Critical Current

Links

Landscapes

  • Gasification And Melting Of Waste (AREA)
  • Incineration Of Waste (AREA)

Description

【発明の詳細な説明】 この発明はボイラ定期検査後に運転を開始する
ときしばらくの期間、捕集される煤塵、所謂定検
灰を処理する方法に関する。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for treating soot and dust, so-called periodic inspection ash, which is collected for a while when starting operation after a boiler periodic inspection.

ボイラの定期検査、所謂定検に際しては炉内や
ダクトその他の機器の検査が行われ、機器の手入
れ、再取付けその他の振動等により相当量の錆が
排出され単なる掃除では充分な除去がされず、定
検後しばらくの間、例えば約20日位の間は捕集灰
には相当な量例えば約40%もの錆(Fe2O3)等の
不燃成分が含有されることとなる。またこの捕集
灰には重原油の燃焼による未燃カーボン,脱硝に
よる硫安等が含まれており流動層炉で燃焼しその
保有エネルギーの回収減容の処理をするが、この
錆量が多いことは流動媒体の小塊形成,多孔板上
への堆積等により流動層炉の運転を悪化させつい
には停止をしなければならぬという問題がある。
During periodic inspections of boilers, the inside of the furnace, ducts, and other equipment are inspected, and a considerable amount of rust is removed due to equipment maintenance, reinstallation, vibration, etc., and simple cleaning is not sufficient to remove it. For a while after the regular inspection, for example, for about 20 days, the collected ash will contain a considerable amount of non-combustible components such as rust (Fe 2 O 3 ), for example, about 40%. In addition, this collected ash contains unburned carbon from the combustion of heavy crude oil, ammonium sulfate from denitrification, etc., and is burned in a fluidized bed furnace to recover the retained energy and reduce the volume. However, there is a problem in that the operation of the fluidized bed furnace deteriorates due to the formation of small lumps of the fluidized medium, deposits on the perforated plate, etc., and the operation of the fluidized bed furnace eventually has to be shut down.

この発明はこのような問題を解決するもので定
検灰の焼却する処理方法を提案することを目的と
する。
The purpose of this invention is to solve such problems and to propose a method for incinerating regularly inspected ash.

要するにこの発明は、定検灰中の不燃成分を除
去し可燃成分のみを流動層炉に供給し燃焼させて
処理する方法であることを特徴とする。
In short, the present invention is characterized in that it is a method of removing non-combustible components from periodically inspected ash and supplying only combustible components to a fluidized bed furnace for combustion.

まず一例として実稼動の発電用ボイラにおける
捕集灰の量と性状は下記の通りである。
First, as an example, the amount and properties of collected ash in a power generation boiler in actual operation are as follows.

排ガス量 37000 Nm3/h 重原油灰 17Ton/日 (710Kg/hr) (未燃成分75%含有の場合) (a) 重原油灰性状 未燃炭素(強熱減量)30〜75% (NH4 5〜15% SO420〜40%) 発熱量(ドライベース)2550〜5960Kcal/
Kg (b) 定検灰の性状 水分 70〜80% 未然炭素(強熱減量) 5〜
15% 電気集塵装置捕集灰(EP灰と称す) 錆(Fe2O3)含有量 35〜40% なお発電所には通常数基のボイラが設置されて
いる。もとより一基のボイラ(ユニツトボイラ)
に一基の焼却炉を設けることは不経済であり数基
のボイラの捕集灰を一の集合貯槽に送りここから
焼却炉に供給し燃焼処理をしている。
Exhaust gas amount 37000 Nm 3 /h Heavy crude oil ash 17Ton/day (710Kg/hr) (When containing 75% unburned components) (a) Heavy crude oil ash properties Unburned carbon (ignition loss) 30-75% (NH 4 5-15% SO 4 20-40%) Calorific value (dry base) 2550-5960Kcal/
Kg (b) Properties of regularly inspected ash Moisture 70-80% Unexploited carbon (loss on ignition) 5-
15% Electrostatic precipitator collected ash (referred to as EP ash) Rust (Fe 2 O 3 ) content 35-40% A power plant is usually equipped with several boilers. Originally, one boiler (unit boiler)
It is uneconomical to install a single incinerator in the area, so the collected ash from several boilers is sent to one collective storage tank, from where it is supplied to the incinerator for combustion.

その管系統を第1図に示す。 The pipe system is shown in Figure 1.

1A,1B,1Cは夫々独立して運転されてい
るボイラを示す。ボイラ1A,1B,1Cからの
排ガスは夫々の集塵装置2A,2B,2Cで含有
する煤塵が捕集され単位貯槽3A,3B,3Cに
夫々送入される。捕集された煤塵(捕集灰)はこ
の単位貯槽からクツシヨンタンク3A′,3B′,
3C′を経由しトランスミツタ4A,4B,4Cに
より低圧空気(約2.0Kg/cm2g)で更に管路5A,
5B,5C,弁6A,6B,6C、切換箱7、主
管路8、弁9を経由し集合貯槽10に送入され
る。圧送用の空気は管路11から焼却炉14に送
られ燃焼用の空気の一部として使用される。
1A, 1B, and 1C each indicate independently operated boilers. The exhaust gases from the boilers 1A, 1B, and 1C are collected with dust collectors 2A, 2B, and 2C, and are sent to unit storage tanks 3A, 3B, and 3C, respectively. The collected soot dust (collected ash) is transferred from this unit storage tank to cushion tanks 3A', 3B',
3C' and transmitters 4A, 4B, and 4C with low pressure air (approximately 2.0 kg/cm 2 g) to pipes 5A,
5B, 5C, valves 6A, 6B, 6C, switching box 7, main pipe 8, and valve 9, and are sent to collection tank 10. The pressurized air is sent to the incinerator 14 from the pipe 11 and is used as part of the combustion air.

集合貯槽10内の捕集灰は弁10aを経由し、
必要あるときは供給装置(図示せず)を使用し管
路10bを経由して焼却炉14に送られ焼却処理
される。助燃焼料は管路12より焼却炉14に供
給され流動用兼用燃焼用空気、及び燃焼用空気は
送風機13から管路15を経由して焼却炉14に
供給される。
The collected ash in the collection tank 10 passes through the valve 10a,
When necessary, the material is sent to the incinerator 14 via the pipe 10b using a feeding device (not shown) and is incinerated. The auxiliary combustion material is supplied to the incinerator 14 through the pipe 12, and the fluidizing and combustion air and the combustion air are supplied from the blower 13 to the incinerator 14 via the pipe 15.

しかしこのような装置では定検後の錆等の不燃
性の成分を多量に含む煤塵の燃焼は流動層炉等の
燃焼装置で処理することは先に述べたように各種
の困難を生ずるものである。
However, with this type of equipment, burning soot and dust containing a large amount of non-combustible components such as rust after a periodic inspection is treated with a combustion equipment such as a fluidized bed furnace, which causes various difficulties as mentioned earlier. be.

この発明は定検灰からこのような錆等を除去し
可燃成分のみを燃焼させ安定した運転をしようと
するもので、その実施にかかる装置の管系統を第
2図に示す。この発明においては切換箱7と集合
貯槽10を接続する主管路8をバイパスするバイ
パス管路16を設ける。この管路には弁17,サ
イクロンセパレータ18,バツグフイルタ19が
切換箱7の側より順に配置される。錆等を含む定
検灰は弁9を閉にすることにより集合貯槽10に
直接流入せずバイパス管路16に流れ弁17から
サイクロンセパレータ18に流入し比重の大なる
錆等は殆んど分離除去される。分析室で分析の結
果では100μ以上の煤塵のFe含有量は80%以上で
あり、一方サイクロンセパレータでは通常20ミク
ロン以上のダストが容易に捕集され、しかも効率
98%程度が得られていることによりすればこのサ
イクロンセパレータで錆等の不燃成分の除去が充
分にされることが判る。可燃成分たる未燃カーボ
ン,硫安成分は管路16a経由バツグフイルタ1
9に流入し捕集される。この捕集灰は管路16b
を経由集合貯槽10に送られる。
This invention aims to remove such rust etc. from regularly inspected ash and burn only the combustible components to achieve stable operation. The piping system of the apparatus used for this purpose is shown in Fig. 2. In this invention, a bypass pipe line 16 is provided that bypasses the main pipe line 8 connecting the switching box 7 and the collection storage tank 10. A valve 17, a cyclone separator 18, and a bag filter 19 are arranged in this conduit in this order from the switching box 7 side. By closing the valve 9, regularly inspected ash containing rust, etc. does not flow directly into the collection tank 10, but instead flows into the bypass pipe 16, and flows into the cyclone separator 18 through the valve 17, so that most of the rust, etc., which has a large specific gravity, is separated. removed. As a result of analysis in the laboratory, the Fe content of soot dust of 100 μm or more is more than 80%, while the cyclone separator usually easily collects dust of 20 μm or more and is efficient.
The fact that about 98% was obtained indicates that this cyclone separator can sufficiently remove non-combustible components such as rust. Unburned carbon and ammonium sulfate components, which are combustible components, are passed through the bag filter 1 through a pipe 16a.
9 and is collected. This collected ash is transferred to pipe 16b
is sent to the collection storage tank 10 via the storage tank 10.

また特に定検後最初のボイラ起動に際しての捕
集灰についてはバイパス管路16を更にバイパス
する弁22を含む管路23を設け、定検ホツパ2
4に収容するようにする。前記サイクロンセパレ
ータ18、バツグフイルタ19の点検又は捕集時
にもこの定検ホツパ24を利用することができ
る。バイパス管路16の圧送空気は管路20を経
由し、定検ホツパ24への圧送空気は管路26を
経由し焼却炉14に供給し2次燃焼用空気として
使用する。
In particular, for the collected ash when starting the boiler for the first time after a regular inspection, a pipe line 23 including a valve 22 that further bypasses the bypass line 16 is provided,
4. The regular inspection hopper 24 can also be used when inspecting or collecting the cyclone separator 18 and bag filter 19. The pressurized air from the bypass pipe 16 passes through the pipe 20, and the pressurized air to the regular inspection hopper 24 is supplied to the incinerator 14 via the pipe 26 to be used as secondary combustion air.

定検ホツパ24の定検灰は不燃成分分離装置2
5を経由し、要すれば水分除去装置(乾燥機)
(図示せず)を経由し可燃成分のみを管路27よ
り集合貯槽10に送ることができる。
The regular inspection ash from the regular inspection hopper 24 is sent to the non-combustible component separation device 2.
5, and if necessary, a moisture removal device (dryer)
(not shown), only the combustible components can be sent to the collection tank 10 from the pipe line 27.

またクツシヨンタンク3A′,3B′,3C′から
トランスミツタ4A,4B,4Cに供給する定検
灰は錆等の含有量が多いので1回の輸送量をボイ
ラ定格運転時のほぼ1/5位の量にすることが定検
灰の輸送には好ましい結果を与える。なおこのト
ランスミツタから集合貯槽までの距離は約700m
もある場合がある。一例ではクツシヨンタンクの
容量を約600とし輸送管内をプラグ状態にして
秒速2〜3mの速度で輸送する。捕集灰をクツシ
ヨンタンクに供給し、輸送を完了し管内を清掃す
る時間を含め700m輸送で1サイクル、10分/回
程度にすることがよい。定検灰のときは従つて一
回の輸送では約120/回にするとよい。また定
検灰が定格運転時の灰の状態に復帰するには約3
週間かかることを経験した。
In addition, the periodic inspection ash supplied from the cushion tanks 3A', 3B', 3C' to the transmitters 4A, 4B, 4C contains a lot of rust, etc., so the amount transported at one time is approximately 1/5 of the boiler's rated operation. A similar amount will give favorable results for the transportation of regularly inspected ash. The distance from this transmitter to the collective storage tank is approximately 700m.
There are also cases. In one example, the capacity of the cushion tank is about 600, and the inside of the transport pipe is in a plug state, and the product is transported at a speed of 2 to 3 meters per second. It is preferable to supply the collected ash to the cushion tank, complete the transport, and clean the inside of the pipe in one cycle of 700 m, or about 10 minutes per cycle. Therefore, when transporting regularly inspected ash, it is recommended to transport approximately 120 times. Also, it takes about 30 minutes for regular inspection ash to return to the ash state at rated operation.
I experienced that it took a week.

この発明を実施することにより集合貯槽に供給
される煤塵はほぼ可燃成分のみとなり焼却炉の連
続運転を可能とし、またその運転を安定したもの
にでき、従来の定検灰の処理におけるような焼却
炉の停止ということは全くなくなるという効果を
奏するものである。
By carrying out this invention, the soot and dust supplied to the collective storage tank will be almost exclusively combustible components, making it possible to operate the incinerator continuously and stably. This has the effect of completely eliminating the need for the furnace to shut down.

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

第1図は従来のボイラ排ガス中の煤塵処理装置
の管系統図、第2図はこの発明の実施にかかる定
検灰処理装置の管系統図である。 1A,1B,1C……ボイラ、3A,3B,3
C……単位貯槽、3A′,3B′,3C′……クツシ
ヨンタンク、4A,4B,4C……トランスミツ
タ、7……切換箱、8……主管路、10……集合
貯槽、14……焼却炉、16……バイパス管路、
18……サイクロンセパレータ、19……バツグ
フイルタ、24……定検ホツパ。
FIG. 1 is a pipe system diagram of a conventional apparatus for treating soot and dust in boiler exhaust gas, and FIG. 2 is a pipe system diagram of a periodic inspection ash processing apparatus according to the present invention. 1A, 1B, 1C...Boiler, 3A, 3B, 3
C...Unit storage tank, 3A', 3B', 3C'...Cushion tank, 4A, 4B, 4C...Transmitter, 7...Switching box, 8...Main conduit, 10...Combined storage tank, 14... ...Incinerator, 16...Bypass pipeline,
18...Cyclone separator, 19...Bag filter, 24...Regular inspection hopper.

Claims (1)

【特許請求の範囲】 1 ボイラ排ガスから捕集した煤塵を収容する単
位貯槽から焼却炉近傍に位置する集合貯槽に前記
捕集煤塵を管路輸送しさらに焼却炉に供給して燃
焼処理する方法において、前記管路に切換箱を設
けこの切換箱と集合貯槽を主管路で接続し、かつ
この主管路にバイパス管路を設け、ボイラ定検後
捕集灰が通常の重原油灰の組成になるまでの間
は、前記バイパス管路に設けた不燃成分除去装置
により不燃成分を除去し、可燃成分を焼却炉に供
給して燃焼させることを特徴とする定検灰の処理
方法。 2 前記不燃成分除去装置をバイパス管路に設け
たサイクロンセパレータ、バツグフイルタとし、
バツグフイルタで捕集した灰を焼却炉で燃焼処理
することを特徴とする特許請求の範囲第1項記載
の定検灰の処理方法。 3 定検灰を燃焼処理する間は、単位貯槽のクツ
シヨンタンクから管路圧送する単位圧送煤塵量を
ボイラ定格運転時の単位圧送煤塵量のほぼ1/5と
することを特徴とする特許請求の範囲第1項又は
第2項記載の定検灰の処理方法。 4 定検灰の圧送用空気を重原油灰貯槽に接続す
るバツグフイルタ経由焼却炉の2次燃焼用空気と
して焼却炉に供給することを特徴とする特許請求
の範囲第1項ないし第3項のいずれかに記載の定
検灰の処理方法。 5 前記バイパス管路を更にバイパスする管路を
設けこの管路に定検灰ホツパと不燃成分分離装置
を設けることを特徴とする特許請求の範囲第1項
記載の定検灰の処理方法。
[Scope of Claims] 1. A method for transporting the collected soot and dust through pipes from a unit storage tank for storing soot and dust collected from boiler exhaust gas to a collective storage tank located near an incinerator, and then supplying the soot and dust to the incinerator for combustion treatment. , a switching box is provided in the pipeline, the switching box and the collection storage tank are connected through a main pipeline, and a bypass pipeline is provided in the main pipeline, so that after a regular inspection of the boiler, the collected ash has the composition of normal heavy crude oil ash. Until then, non-combustible components are removed by a non-combustible component removal device provided in the bypass pipe, and combustible components are supplied to an incinerator and burned. 2. The non-flammable component removal device is a cyclone separator or bag filter provided in a bypass pipe,
2. The method for treating periodically inspected ash according to claim 1, wherein the ash collected by the bag filter is burned in an incinerator. 3. A patent claim characterized in that, during the combustion treatment of periodically inspected ash, the amount of soot and dust pumped through the pipe from the cushion tank of the unit storage tank is approximately 1/5 of the amount of soot and dust that is pumped per unit during rated operation of the boiler. A method for processing regularly inspected ash as described in item 1 or 2. 4. Any one of claims 1 to 3, characterized in that the air for pressure-feeding periodically inspected ash is supplied to the incinerator as secondary combustion air for the incinerator via a bag filter connected to the heavy crude oil ash storage tank. Processing method for regularly inspected ash described in ``Kani''. 5. The method for processing periodically inspected ash according to claim 1, characterized in that a pipeline further bypassing the bypass pipeline is provided, and this pipeline is provided with a regularly inspected ash hopper and a non-combustible component separation device.
JP14637080A 1980-10-21 1980-10-21 Treatment of ashes at regular inspection Granted JPS5770315A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP14637080A JPS5770315A (en) 1980-10-21 1980-10-21 Treatment of ashes at regular inspection

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP14637080A JPS5770315A (en) 1980-10-21 1980-10-21 Treatment of ashes at regular inspection

Publications (2)

Publication Number Publication Date
JPS5770315A JPS5770315A (en) 1982-04-30
JPS6363809B2 true JPS6363809B2 (en) 1988-12-08

Family

ID=15406177

Family Applications (1)

Application Number Title Priority Date Filing Date
JP14637080A Granted JPS5770315A (en) 1980-10-21 1980-10-21 Treatment of ashes at regular inspection

Country Status (1)

Country Link
JP (1) JPS5770315A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0362106A (en) * 1988-06-09 1991-03-18 Samsung Electron Co Ltd Temperature detecting circuit of automatic bakery equipment and method of controlling the same

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH0362106A (en) * 1988-06-09 1991-03-18 Samsung Electron Co Ltd Temperature detecting circuit of automatic bakery equipment and method of controlling the same

Also Published As

Publication number Publication date
JPS5770315A (en) 1982-04-30

Similar Documents

Publication Publication Date Title
CN102165255B (en) Method for incinerating waste by two-stage swirling flow fluidized bed incinerator
JPS61175241A (en) Gasified coal combined power generating device
US4055125A (en) Incinerator, especially for burning waste material
US4416855A (en) Radioactive waste treatment apparatus
US5964921A (en) Method and device for removing harmful substances, in particular, dioxin
JP3549843B2 (en) Method and apparatus for removing deposits on a fluidized bed
JPS6363809B2 (en)
AU4940199A (en) A method of cleaning flue gases
US20090010720A1 (en) Use of air activated gravity conveyors in a continuous particulate removal process from an ESP or baghouse
JPS61186705A (en) Fuel supply method for high speed fluidized bed burning equipment
JPS6039607B2 (en) Gas pipe transportation method for fine powder coal
JPS5896913A (en) Solid fuel feeding method for fluidized bed combustion device
CN216644216U (en) Sludge and coal-fired power plant coupled disposal system
US2857854A (en) Coal burning generating electric loco-motive with improved ash separation and storagesystem
JP2003262308A (en) Removing method for bed material deposit and fluidized bed type incinerator with removing device for bed material deposit
CN208074979U (en) A kind of chemical engineering incinerator tails dedusting heat-exchanger rig
JPH0335930Y2 (en)
JPH08291909A (en) Fly ash treating equipment of boiler for power generation
JPS5661515A (en) Treating device of uncombusted carbon
JPS62125891A (en) Treatment of fly ash
CN113803723A (en) Sludge is coal fired power plant coupling processing system in coordination
JPS6410731B2 (en)
CN112105870A (en) Optimized method and system for producing hot fluid by combustion of fuel
JPS61259004A (en) Method of igniting solid fuel
CN110500597A (en) A kind of pressure vessel mixed aerosol system