JPS60101415A - Deodorizing method of sludge combustion exhaust gas - Google Patents
Deodorizing method of sludge combustion exhaust gasInfo
- Publication number
- JPS60101415A JPS60101415A JP58208769A JP20876983A JPS60101415A JP S60101415 A JPS60101415 A JP S60101415A JP 58208769 A JP58208769 A JP 58208769A JP 20876983 A JP20876983 A JP 20876983A JP S60101415 A JPS60101415 A JP S60101415A
- Authority
- JP
- Japan
- Prior art keywords
- exhaust gas
- rotary kiln
- waste
- sludge
- combustion exhaust
- 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.)
- Pending
Links
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/08—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating
- F23G5/14—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating including secondary combustion
- F23G5/16—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating including secondary combustion in a separate combustion chamber
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/008—Incineration of waste; Incinerator constructions; Details, accessories or control therefor adapted for burning two or more kinds, e.g. liquid and solid, of waste being fed through separate inlets
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/001—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals for sludges or waste products from water treatment installations
Abstract
Description
【発明の詳細な説明】
〔産業上の利用分野〕
本発明は産業111水等の処理過程で発生する汚泥を燃
焼したときに生ずる排ガスの脱臭方法に関するものであ
る。DETAILED DESCRIPTION OF THE INVENTION [Field of Industrial Application] The present invention relates to a method for deodorizing exhaust gas generated when sludge generated in the treatment process of industrial 111 water is burned.
排水汚泥処理方法の一つとして従来からロータリキルン
、竪型多段炉及びストーカ−炉等による焼却処理が行な
われているが、汚泥自体が多量の水分を含んでいて発熱
量が少ないため、排ガスの龜緻が低く、臭気を燃焼分屏
せしめることができない。Incineration in rotary kilns, vertical multistage furnaces, stoker furnaces, etc. has traditionally been used as a method for treating wastewater sludge, but since the sludge itself contains a large amount of water and has a low calorific value, The density is low and the odor cannot be filtered out by combustion.
例えは、ロータリキルンの場合にげ向流式になるが、空
気の入る炉の出口のバーナー幌亀が600℃で中央部で
800℃でも、炉の人口から出る排ガスの温度が約30
0℃に低下するので臭気濃度が高いま\排出されること
になる。なお並流式ロータリキルンではバーナーに近い
炉の人口附近では600ないし700℃であるが出口方
向に温度が低下するので汚泥が完全に焼却されない。従
って並流式ロータリキルンは採用ばれない。For example, in the case of a rotary kiln, the counterflow type is used, but even if the burner hood at the outlet of the furnace where air enters is 600°C and the central part is 800°C, the temperature of the exhaust gas coming out of the furnace is about 30°C.
Since the temperature drops to 0°C, the odor concentration remains high and is emitted. In a co-current rotary kiln, the temperature is 600 to 700°C near the furnace near the burner, but the temperature decreases toward the outlet, so the sludge is not completely incinerated. Therefore, a parallel flow rotary kiln is not adopted.
このような理由で、公害防止上焼却炉とは別に脱臭炉を
設け、焼却炉の燃焼1ノ[ガスを更に脱臭処理している
。通常、脱臭炉はlli燃方式で、へ重油等の燃料を助
燃剤として600ないし700℃で臭気を燃焼させてい
るが、燃料を多量に使用するため省エネルギーの面から
はあまり有効な手段ではない。For this reason, in order to prevent pollution, a deodorizing furnace is installed separately from the incinerator, and the combustion gas from the incinerator is further deodorized. Normally, deodorizing furnaces are lli combustion type, which burns odors at 600 to 700 degrees Celsius using fuel such as heavy oil as a combustion aid, but this is not a very effective means from an energy saving perspective as it uses a large amount of fuel. .
本発明は上記の問題点に鑑み、エネルギー消費袖の少な
い汚泥燃焼排ガス脱臭方法の提供を目日勺とするもので
ある。In view of the above problems, the present invention aims to provide a method for deodorizing sludge combustion exhaust gas that consumes less energy.
本発明者等は既存の産業廃棄物焼却設備の中で、発熱量
の大きな投入物を対象とする並流式ロータリキルンの燃
焼熱を利用しイυることに着排水汚泥宿英気を発生する
燃焼物の燃焼1ノ1ガスを並流式ロータリキルン内に導
き、静拶トガス中の臭気金高#!1量廃棄物とともに燃
焼せしめることw q”r徴とするものである。The present inventors have developed an existing industrial waste incineration facility that utilizes the combustion heat of a parallel flow rotary kiln, which is used for input materials with a large calorific value, to generate wastewater sludge retention air. The combustion gas of the combustible material is guided into the parallel flow type rotary kiln, and the odor in the gas is high! It is intended to be incinerated together with a certain amount of waste.
自動車工場等においては廃油、塗料滓、廃プラスチック
ス等が大Mに発生し、これを処理するのにロータリキル
ンを用いて焼却している。In automobile factories and the like, large amounts of waste oil, paint slag, waste plastics, etc. are generated, and rotary kilns are used to incinerate these wastes.
」1記の廃莱IlグCよ発熱量が高いため、炉の中央部
が約1000℃となり、投入物が完全に焼却されるばか
りでなく、排気中の臭気も嗅覚に感じない程1扶に除去
される。但し投入物の水分が少ないため炉の入口ト1(
近で着火するので回流式ロータリキルンを用いた場合に
は約800℃の高温ガスが炉の人口からダクト内に流れ
込み、臭気力玉タ゛クト内で燃焼することになる。これ
に対して1p流式ロータリキルンの場合には臭気ガス力
玉炉の中で燃えつきるため、ダクト内で燃焼する恐iL
がなく、高熱情廃乗物の焼却に増している。本発明はこ
のような特徴を汚泥燃焼Iトガスの脱臭に利用したもの
であり、以下、実施例4図11uに従って説明する。Because of the high calorific value of the waste Ilg C described in 1., the temperature at the center of the furnace reaches approximately 1000°C, which not only completely incinerates the input material, but also causes the odor in the exhaust to reach a temperature so high that it cannot be detected by the sense of smell. will be removed. However, since the moisture content of the input material is low, the temperature at the inlet of the furnace is
If a recirculation rotary kiln is used, high-temperature gas of about 800°C will flow into the duct from the furnace and burn in the odor duct. On the other hand, in the case of a 1p flow type rotary kiln, the odor gas burns out in the kiln, so there is a risk of combustion in the duct.
There is an increasing number of people with high passion for incinerating waste vehicles. The present invention utilizes such characteristics for deodorizing sludge combustion I gas, and will be described below with reference to FIG. 11u of Example 4.
第1図は従来の汚泥の焼却及び初ガス脱芙工程の一例を
ボす。Figure 1 shows an example of the conventional sludge incineration and initial gas removal process.
図示されてないバンカーに貯W(された汚泥か、同じく
図示されてないスクリューコンベア、ベルトコンベアに
より4込−れて、投入口1から向流式ロータリキルン2
に投入される。3は燃料入口、4は燃焼用空気入ロ會7
Jクシ、ロータリキルンz内は空気誘引ファン5によっ
て負圧に保たれている。6は焼却灰出口會71< L、
、l’j泥と排ガスが互いに同流・に訛れている。投
入時の汚泥は水分60ないし85係、固形分15ないし
40係、発熱量は1000ないし6000 kc al
1Kgすl程度である。このように多量の水分のため
、炉の中心部でd約600℃であるが排ガス錨fiiは
300℃に低下してし甘う、燃焼排ガスはマルチサイク
ロン7(L″経て脱臭炉8に入り、燃料人口9からへ重
油等の燃料を添加されて1α接燃焼方式により700C
で脱臭される。このようにして脱臭炉8の人口で50,
000以上の英気g(lJtが出口では1000u、−
Fとなる。The sludge stored in a bunker (not shown) is transported by a screw conveyor and a belt conveyor (also not shown), and is fed from an inlet 1 to a countercurrent rotary kiln 2.
will be put into the 3 is the fuel inlet, 4 is the combustion air intake hole 7
The interior of the J comb and rotary kiln z is maintained at negative pressure by an air induction fan 5. 6 is the incineration ash outlet meeting 71<L,
, l'j mud and exhaust gas sound similar to each other. The sludge at the time of input has a moisture content of 60 to 85 parts, a solid content of 15 to 40 parts, and a calorific value of 1000 to 6000 kcal.
It is about 1 kg sl. Due to this large amount of moisture, the temperature at the center of the furnace is about 600℃, but the exhaust gas anchor fii drops to 300℃.The combustion exhaust gas enters the deodorizing furnace 8 through the multi-cyclone 7 (L'' , fuel such as heavy oil is added from fuel population 9 to 700C by 1α tangential combustion method.
deodorized. In this way, the population of deodorizing furnace 8 is 50,
More than 000 energy g (lJt is 1000u at the exit, -
It becomes F.
その後脱某伊ガスは冷却塔10で冷却をれて3000と
なり、′東気集塵磯11で微+1tlllなダストが集
塵され煙突12から大気中に放出される。なお13i、
i総合誘引ファンをボす。After that, the removed gas is cooled down to 3,000 yen in the cooling tower 10, and 1 tllll of dust is collected in the east air dust collection area 11 and released into the atmosphere from the chimney 12. Furthermore, 13i,
I beat the general attraction fan.
第21>Uは本ヴ6明の脱臭方法を組入れた汚泥燃焼」
−程の一例ケ表わし、第1図中の脱臭炉8に代λて並流
式ロータリキルン14會設け、高熱拓屏棄物の投入01
5から廃油を投入し、回流式ロータリキルン2で焼却処
理された汚泥の燃焼排ガス中の臭気ケ燃焼させる。廃油
の発熱量は3000ないし5000kcal/Kqであ
り、勾・の1.4] IcJf<5の一1v−がrJ1
000℃となり燃焼↑、Jl ソJスr−1」の英気濃
度111000以下に低下する。21>U is sludge combustion that incorporates the deodorizing method described in this book 6.
- An example of the process is shown in which a parallel flow rotary kiln 14 is installed in place of the deodorizing furnace 8 in Fig. 1, and high-temperature waste is input 01.
Waste oil is introduced from step 5, and the odor in the combustion exhaust gas of the sludge incinerated in the recirculation rotary kiln 2 is burned. The calorific value of waste oil is 3,000 to 5,000 kcal/Kq, and the gradient of 1.4] IcJf<5 is rJ1
000℃ and combustion↑, the concentration of air drops to below 111,000.
並流式ロータリキルン14 rJ:タコ内入(去わ1ガ
ス力玉適切な温1政に維持されるようにJ重ll駄条V
r奮f4i11企9される。丁なわち脱果−11,11
−ガスのvXJXl政力5700℃程度となるように1
’lCA (扇鵬指7J” fit囚会11目に七引)
でj外泊の川霧h¥をtttli伸[2、捷た並t+I
飄ロータIJキル刈4の出口1111に設けたPiUA
(LE〕j]旨7F l’j節酋外¥I′、)が負圧を
力(すように酩合詩弓1ファン13の回転数を調整する
ことにより操イS栴)fl−を1ill仰している。Parallel flow type rotary kiln 14 rJ: Inside the octopus
9 efforts were made. Ding, that is, the fall of fruit - 11, 11
- gas vXJXl political power 1 so that it is about 5700℃
'lCA (Ogiho finger 7J" fit prisoner's meeting 11th 7th pull)
Dej sleepover Kawagiri h ¥ tttli extension [2, shortened t+I
PiUA installed at exit 1111 of the rotor IJ kill 4
(LE] j] 7F l'j section ext.\I',) to apply negative pressure (by adjusting the rotation speed of the fan 13 of the fan 13) fl- I'm looking forward to it.
3止流弐〇−タリキルント1ヶ出たjl・2芙4J1ノ
jスe」、その後(f米の工程と回付に詮却塔1(1、
’+14磯集1υ)(へ511、煙突12(i−餅て大
気中にh(出ネオI;、)。ノit< 11.1ガス中
の、H鎖成分は5(JX200[)I)Ill y F
% NNOx100ppり上程世で嗅覚に感じない。な
お並流式ロータリキルン4か修j(i4 ’fj、−C
休市1イ〕体A合Vこ備ヌて従来方式の脱臭炉8ケil
+設し、燃焼わ「ノJスをバイパスさせるようにしであ
る。3 stop flow 2〇 - 1 Tarikirunt came out jl・2芙4J1ノjsu", then (f rice process and circulation 1 (1,
'+14 Isoshu 1υ) (to 511, chimney 12 (i-mochi into the atmosphere h (out neo I;,). Noit < 11.1 The H chain component in the gas is 5 (JX200 [) I) Ill y F
%NNOx100pp and above, I can't sense it in my sense of smell. In addition, parallel flow type rotary kiln 4 or modification (i4 'fj, -C
Shuichiichi 1 A] Conventional deodorizing furnace 8 liters
It is set so that the combustion engine is bypassed.
」1記の如く本発明により並流式ロータリキルンで高熱
量廃棄物を焼却しながら汚泥燃焼排ガスの脱臭を行なえ
るので従来の脱臭炉で使用していたへ重油等の燃料が不
要になり省エネルギー効果が大きい。As described in 1, the present invention enables deodorization of sludge combustion exhaust gas while incinerating high calorific waste in a co-current rotary kiln, which eliminates the need for fuel such as heavy oil used in conventional deodorization furnaces, resulting in energy savings. Great effect.
なお本発明は汚泥を処理するす亮却炉として向流式ロー
タリキルンのほか多段炉、ストーカ−炉等、広範囲の焼
却炉と組合せても実施することができるので英気ガス対
策上有用である。The present invention is useful as a countermeasure against air gas because it can be implemented in combination with a wide range of incinerators, such as countercurrent rotary kilns, multi-stage furnaces, and stoker furnaces as well as incinerators for treating sludge.
第1図は従来の千泥焼却より七トガス脱臭までの工程図
ケ表わし、
第2図は本発明実施例の工程図で表わす。
図中、
1・・・投入口 2・・・自流式ロータリキルン3・・
・燃料人口 4・・・燃焼用債気入口5・・・空気誘引
ファン 6川焼却灰出ロア・・・マルチサイクロン 8
・・・刀兄美炉9・・・燃料人口 1o・・・冷却塔
11・・・電気集塵機 12・・・煙突13・・・総合
線引ファン 14・・・並流式ロータリキルン15・・
・投入口
特許出願人 トヨタ自動車株式会社Figure 1 shows a process diagram from conventional incineration to seven gas deodorization, and Figure 2 shows a process diagram of an embodiment of the present invention. In the diagram, 1... Input port 2... Self-flow rotary kiln 3...
・Fuel population 4... Combustion bond air inlet 5... Air induction fan 6 River incineration ash output lower... Multi cyclone 8
・・・Toonai furnace 9...Fuel population 1o...Cooling tower 11...Electrostatic precipitator 12...Chimney 13...Comprehensive drawing fan 14...Parallel current rotary kiln 15...
・Input port patent applicant Toyota Motor Corporation
Claims (1)
式ロータリキルン内に導き、該排ガス中の臭気を筒熱量
廃棄物とともに燃焼せしめることを特徴とする汚泥燃焼
排ガスの脱臭方法。1. A method for deodorizing sludge combustion exhaust gas, which comprises introducing the combustion exhaust gas of a combustible material that generates an odor, such as drainage sludge, into a parallel flow type rotary kiln, and burning the odor in the exhaust gas together with the cylinder calorific waste.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP58208769A JPS60101415A (en) | 1983-11-07 | 1983-11-07 | Deodorizing method of sludge combustion exhaust gas |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP58208769A JPS60101415A (en) | 1983-11-07 | 1983-11-07 | Deodorizing method of sludge combustion exhaust gas |
Publications (1)
Publication Number | Publication Date |
---|---|
JPS60101415A true JPS60101415A (en) | 1985-06-05 |
Family
ID=16561782
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP58208769A Pending JPS60101415A (en) | 1983-11-07 | 1983-11-07 | Deodorizing method of sludge combustion exhaust gas |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPS60101415A (en) |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5249674A (en) * | 1975-10-16 | 1977-04-20 | Kobe Steel Ltd | Wastes incinerator |
JPS55140026A (en) * | 1979-04-18 | 1980-11-01 | Nippon Kokan Kk <Nkk> | Fusing type incinerator for refuse |
JPS5840419A (en) * | 1981-09-04 | 1983-03-09 | Ebara Infilco Co Ltd | Incineration by means of rotary kiln |
-
1983
- 1983-11-07 JP JP58208769A patent/JPS60101415A/en active Pending
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5249674A (en) * | 1975-10-16 | 1977-04-20 | Kobe Steel Ltd | Wastes incinerator |
JPS55140026A (en) * | 1979-04-18 | 1980-11-01 | Nippon Kokan Kk <Nkk> | Fusing type incinerator for refuse |
JPS5840419A (en) * | 1981-09-04 | 1983-03-09 | Ebara Infilco Co Ltd | Incineration by means of rotary kiln |
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