JP2001276565A - Method and column for quenching combustion exhaust gas of industrial waste - Google Patents

Method and column for quenching combustion exhaust gas of industrial waste

Info

Publication number
JP2001276565A
JP2001276565A JP2000096889A JP2000096889A JP2001276565A JP 2001276565 A JP2001276565 A JP 2001276565A JP 2000096889 A JP2000096889 A JP 2000096889A JP 2000096889 A JP2000096889 A JP 2000096889A JP 2001276565 A JP2001276565 A JP 2001276565A
Authority
JP
Japan
Prior art keywords
exhaust gas
tower
wall
quenching
industrial waste
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.)
Granted
Application number
JP2000096889A
Other languages
Japanese (ja)
Other versions
JP4673464B2 (en
Inventor
Hideyuki Moriaki
秀行 森明
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 Mining Holdings Inc
Eneos Corp
Original Assignee
Nippon Mining and Metals Co Ltd
Nippon Mining 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 Mining and Metals Co Ltd, Nippon Mining Co Ltd filed Critical Nippon Mining and Metals Co Ltd
Priority to JP2000096889A priority Critical patent/JP4673464B2/en
Publication of JP2001276565A publication Critical patent/JP2001276565A/en
Application granted granted Critical
Publication of JP4673464B2 publication Critical patent/JP4673464B2/en
Anticipated expiration legal-status Critical
Expired - Fee Related legal-status Critical Current

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  • Chimneys And Flues (AREA)
  • Treating Waste Gases (AREA)
  • Gas Separation By Absorption (AREA)

Abstract

PROBLEM TO BE SOLVED: To prevent the internal erosion generated in a quenching column for quenching exhaust gas formed by incinerating industral waste. SOLUTION: Exhaust gas is introduced into the quenching column 1 as a descending flow and successively passed through the first region 2 on the inlet side of the tower, where the cooling of the exhaust gas is generated by the heat conduction with the inner wall of the quenching column 1, the second region 5, where the cooling of exhaust gas is generated by the heat conduction with the inner wall and cooling water, of the tower and the third region 4, where the exhaust gas is quenched to at least a temperature range of 800-80 deg.C by cooling water ejected from a spray nozzle 3, of the tower. The inner wall of the second region 3 is constituted of SK30 refractory.

Description

【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION

【0001】[0001]

【発明の属する技術分野】本発明は、廃プラスチック、
廃油、汚泥、めっき廃液などの金属スクラップ以外の産
業廃棄物を焼却処理した排ガスを急冷処理する方法及び
急冷塔の内壁構造に関するものである。本出願人はこれ
ら産業廃棄物の処理を、「資源と素材、リサイクリング
大特集号」1997(113)、12、第1177頁に
て紹介したフローで、日産約100トン処理している。
又、BASF型焼却炉で発生した排ガス中にダイオキシン
を発生させないよう特定温度を急冷する急冷塔を使用し
ている。
TECHNICAL FIELD The present invention relates to a waste plastic,
The present invention relates to a method for quenching an exhaust gas obtained by incinerating industrial waste other than metal scrap such as waste oil, sludge, plating waste liquid, and the like, and an inner wall structure of a quenching tower. The applicant of the present invention processes about 100 tons of industrial waste daily according to the flow introduced in "Resources and Materials, Special Issue on Recycling", 1997 (113), 12, p. 1177.
In addition, a quenching tower is used to quench a specific temperature so as not to generate dioxin in exhaust gas generated in a BASF incinerator.

【0002】[0002]

【従来の技術】従来の排ガス急冷塔は、縦型塔の上部か
ら導入された1173K(900℃)〜1273K(1
000℃)程度の排ガスを下向きに吸引し、途中に設け
られたスプレー領域で約360m3 /hrの流量で水を噴射
し、973K(700℃)から343K(70℃)以下
に急冷してダイオキシンの発生を抑止している。冷却さ
れた排ガスは塔の下部からスクラバーに送って除塵し、
一方冷却水は排水処理設備に送って中和する。従来の排
ガス急冷塔の内壁はスプレー領域がカーボン煉瓦、その
上部のスプレー水が当たらない領域では耐火性骨材にア
ルミナセメントを混合した耐火キャスターが用いられて
いた。なお、焼却炉ではCr2O3含有耐火物が優れた性能
を示すとの報告があり(Taikabutsu 51[4]237〜
246(1999))、また汎用の耐火キャスターでも
実操業上の支障は来たしていない。
2. Description of the Related Art A conventional exhaust gas quenching tower is composed of 1173K (900 ° C.) to 1273K (1
Exhaust gas of about 000 ° C) downward, water is sprayed at a flow rate of about 360 m 3 / hr in a spray area provided on the way, and rapidly cooled from 973K (700 ° C) to 343K (70 ° C) or less. Is suppressed. The cooled exhaust gas is sent to the scrubber from the bottom of the tower to remove dust,
On the other hand, the cooling water is sent to a wastewater treatment facility for neutralization. The spray wall on the inner wall of the conventional exhaust gas quenching tower used a carbon brick, and a fire-resistant caster in which alumina cement was mixed with a fire-resistant aggregate was used in a region where spray water was not applied. In addition, it has been reported that refractories containing Cr 2 O 3 show excellent performance in incinerators (Taikabutsu 51 [4] 237-
246 (1999)), and even general-purpose refractory casters have not hindered actual operation.

【0003】[0003]

【発明が解決しようとする課題】上記した排ガス急冷塔
で実操業を行ない遭遇した問題は、スプレー領域直上の
耐火キャスターが1ヶ月程度で風化してしまい、耐火物
の再施工が必要になり、産業廃棄物の処理を中断せざる
を得ないことであった。一方焼却炉の耐火物寿命は数ヶ
月以上であり、またスプレー水が直接当る部分の耐火物
寿命にも問題がないために、ノズル噴射角度外で脇に反
れた少量のスプレー水と高温排ガスの競合作用による腐
食が起こっていると考えられ、従来このような現象を論
述した文献などがなかったので、本発明者らは各種耐火
・耐熱材料につき試験を行い産業廃棄物焼却操業の安定
化を実現することができた。
The problem encountered during the actual operation of the above-mentioned exhaust gas quenching tower is that the refractory caster immediately above the spray area is weathered in about one month, and the refractory must be reconstructed. Industrial waste disposal had to be interrupted. On the other hand, the refractory life of the incinerator is several months or more, and there is no problem with the refractory life of the part directly exposed to the spray water. It is considered that corrosion due to competitive action has occurred, and there was no literature that previously discussed such a phenomenon.Therefore, the present inventors conducted tests on various refractory and heat-resistant materials to stabilize the incineration operation of industrial waste. Could be realized.

【0004】[0004]

【課題を解決するための手段】本発明に係る方法は、産
業廃棄物を焼却して発生したダストを含みかつHCl濃
度が0.3〜1.5%、SO2 濃度が0.5〜3%、H
2O飽和濃度である排ガスを、急冷塔に下向きに導入
し、主として急冷塔の内壁との熱伝導により排ガスの冷
却が起こる塔入口側第1の領域、主として塔内壁との熱
伝導及び副次的に下記冷却水により冷却が起こる第2の
領域、及びスプレーノズルから噴射された冷却水により
少なくとも973K(700℃)から343K(70
℃)の温度範囲を急冷する第3の領域を順次通過せしめ
る産業廃棄物焼却排ガス急冷方法において、SK30耐
火物、もしくはSiO2 :65〜75% ,Al2O3 :25〜
30% , Fe2O3 :5%以下の組成を有するSK30耐火
物同等品から実質的になる第2領域を排ガスを通過せし
めることを特徴とする産業廃棄物焼却排ガス急冷方法で
あり、また本発明に係る急冷塔は、産業廃棄物を焼却し
て発生したダストを含む排ガスを、下向きに導入する入
口と、主として塔の内壁との熱伝導により冷却が起こる
塔入口側第1の領域と、主として塔内壁との熱伝導によ
り副次的に下記冷却水により冷却が起こり、排ガスと接
触する部分を、SK30耐火物、もしくはSiO2 :65
〜75% ,Al2O3 :25〜30% , Fe2O3 :5%以下の
組成を有するSK30耐火物同等品から実質的に構成し
た第2の領域と、スプレーノズルから噴射された冷却水
により少なくとも973K(700℃)から343K
(70℃)の温度範囲を急冷する第3の領域とを含んで
なるものである。以下本発明を詳しく説明する。
SUMMARY OF THE INVENTION The method according to the present invention is
Includes dust generated from incineration of industrial waste and
Degree 0.3-1.5%, SOTwoConcentration 0.5-3%, H
TwoExhaust gas with O saturation concentration is introduced downward into the quenching tower
The exhaust gas is cooled mainly by heat conduction with the inner wall of the quench tower.
In the first area on the entrance side of the tower where rejection occurs, mainly the heat of the inner wall of the tower
Secondly, cooling is caused by conduction and by the following cooling water
By area and cooling water injected from spray nozzle
At least 973K (700 ° C) to 343K (70
(° C), pass through the third region where the temperature range is rapidly cooled.
Industrial waste incineration exhaust gas quenching method, SK30 resistant
Fire or SiOTwo: 65-75% , AlTwoOThree: 25-
30% , FeTwoOThree: SK30 refractory having a composition of 5% or less
Exhaust gas through a second zone, which is substantially composed of
Industrial waste incineration exhaust gas quenching method
Yes, and the quenching tower according to the present invention incinerates industrial waste.
Exhaust gas containing dust generated by
Cooling occurs due to heat conduction between the mouth and the inner wall of the tower
Due to the heat conduction between the first area on the inlet side of the tower and the inner wall of the tower
As a result, cooling takes place by the following cooling water,
Touch the part with SK30 refractory or SiOTwo: 65
~ 75% , AlTwoOThree: 25-30% , FeTwoOThree: 5% or less
Consisting essentially of a SK30 refractory equivalent having the composition
And the cooling water injected from the spray nozzle
At least 973K (700 ° C) to 343K
(70 ° C.) in a third region for quenching the temperature range.
It becomes. Hereinafter, the present invention will be described in detail.

【0005】本発明に係る産業廃棄物の焼却法はいわゆ
る焼却炉法に属し、本出願人の特開平10―18515
4号公報で提案した流動床は使用してもよいが、一般に
は使用しない。発生する排ガスは主としてCO,CO2,H2O,O
2,N2からなり、少量の有機物を含有するが、腐食性成分
として濃度が0.3〜1.5%のHCl、濃度が0.5
〜3%のSO2を含有している。以下、図1を参照して
第1〜3領域を説明する。
[0005] The incineration method of industrial waste according to the present invention belongs to the so-called incinerator method, and is disclosed by the present applicant in Japanese Patent Application Laid-Open No. Hei 10-18515.
The fluidized bed proposed in JP-A No. 4 may be used, but is generally not used. The generated exhaust gas is mainly CO, CO 2 , H 2 O, O
2 , N 2 , containing a small amount of organic substances, but having a concentration of 0.3-1.5% HCl as a corrosive component, and a concentration of 0.5
Containing the 3% of SO 2. Hereinafter, the first to third regions will be described with reference to FIG.

【0006】急冷塔1を下向きに流れる排ガスは、冷却
水が全く当たらない第1の領域2では主として塔内壁1
aとの熱交換により冷却がされ、一部は輻射冷却が起こ
る。この第1の領域2は、長さは1.5m程度であり、
温度降下は少なく、1173K(900℃)から112
3K(850℃)程度まであり、また侵食の問題は起こ
らないので通常の耐火キャスターを使用することができ
る。冷却ノズル3の最先端開き角度により決定される噴
射角度(α)、例えばα=90°の範囲内に入る第3の
領域4では冷却水と排ガスの熱交換が主となり、気―液
間伝熱以外は無視できる程度である。この領域4の長さ
は3.5m程度であり、ノズル3は縦方向には3段に、
円周方向には16個を等間隔に配列する。ここでの温度
降下は少なくとも973K(700℃)から343K
(70℃)の温度範囲を急速降下であり、ダイオキシン
の発生が阻止される。
The exhaust gas flowing downward through the quenching tower 1 is mainly in the first area 2 where the cooling water does not hit at all.
Cooling is performed by heat exchange with a, and radiation cooling occurs partially. The first region 2 has a length of about 1.5 m,
Temperature drop is small, from 1173K (900 ° C) to 112
Since the temperature is up to about 3K (850 ° C.) and the problem of erosion does not occur, ordinary refractory casters can be used. In the third region 4 which falls within the range of the injection angle (α) determined by the leading end opening angle of the cooling nozzle 3, for example, α = 90 °, heat exchange between the cooling water and the exhaust gas is mainly performed, and gas-liquid transfer is performed. Other than heat is negligible. The length of this area 4 is about 3.5 m, and the nozzles 3 are vertically arranged in three stages.
Sixteen are arranged at equal intervals in the circumferential direction. The temperature drop here is at least 973K (700 ° C) to 343K
(70 ° C.) is a rapid fall, and the generation of dioxin is prevented.

【0007】これら領域2,4の中間に位置する第2の
領域5では、冷却水が蒸発した蒸気や、噴射角度外にβ
=約30°の範囲で散逸するスプレー水6により排ガス
は冷却され、また排ガスは塔内壁1aとの熱交換によっ
ても冷却される。この領域5の長さは0.8m程度であ
り、ここでの温度降下は1123K(850℃)から9
73K(700℃)程度である。この第2の領域5にお
いて急冷塔1の内壁は原因不明であるが激しく侵食を受
ける。侵食は激しい場合は耐火構造の内部が崩壊し、通
常の場合は表面が大きく損耗する。そこで本発明者らは
鋭意検討の結果、JIS2304に規定される粘土質煉
瓦であるSK30(その同等品も含む)が意外にも極め
て高い耐侵食性をもつことを見出した。ここで、同等品
とは、JIS2304に規定される耐火度、カサ比重、
圧縮強度がSK30とほぼ同じであり、SK28、32
の規格を満足せず、さらにSiO2 =65〜75% ,Al2O3
=25〜30% , Fe2O3 =5%以下の組成をもつもので
ある。また、この領域では煉瓦を固定する結合材や目地
材以外はSK30煉瓦とする。
In a second region 5 located between these regions 2 and 4, steam evaporated from the cooling water and β
The exhaust gas is cooled by the spray water 6 scattered in the range of about 30 °, and the exhaust gas is also cooled by heat exchange with the inner wall 1a of the tower. The length of this area 5 is about 0.8 m, and the temperature drop here is 923 K (850 ° C.) to 9 m.
It is about 73K (700 ° C). In this second area 5, the inner wall of the quenching tower 1 is severely eroded for unknown reasons. If the erosion is severe, the inside of the refractory structure collapses, and the surface is usually greatly worn in normal cases. The present inventors have conducted intensive studies and found that SK30 (including its equivalent), which is a clay brick specified in JIS2304, has unexpectedly extremely high erosion resistance. Here, the equivalent products are fire resistance, bulk specific gravity,
The compressive strength is almost the same as SK30, and SK28, 32
Does not satisfy the standard, and SiO 2 = 65-75% , Al 2 O 3
= 25-30% , Fe 2 O 3 = 5% or less. In this area, SK30 bricks are used except for the binder and the joint material for fixing the bricks.

【0008】図2には急冷塔の全体概略構造を示す。急
冷塔30は全体の高さが5.9m程度であり、内容積が
27m3の縦型塔であって、第2の領域にはSK30煉
瓦35を内張りしている。塔内部に冷却水を弁32を介
して噴射するノズル31a,31b,31cを3段に、
かつ各段に16個周設しており、少なくとも1073K
(800℃)から353K(80℃)の温度範囲で排ガ
スを急冷する。なお、かかる水冷により排ガスに含まれ
るHCl及びSO2は殆んどが水に溶解される。全噴射
ノズルからのスプレー水量は320〜360m3 /hr
である。かかる冷却水噴射の結果、ダストの一部とHC
l,H2SO4などを含有する処理液は底部出口30bか
ら処理液溜り31に溜まり、この処理液は苛性ソーダの
添加による中和を経て冷却水として再利用される。一
方、噴射水により343K(70℃)以下に冷却された
排ガスは、主成分が水蒸気、CO2、O2等であり、流量
は400〜450Nm3/hr、ダスト量は0.1〜
0.2g/Nm3(排ガス容積)である。かかる冷却排
ガスは塔下部に設けられた排ガス出口33から排出され
る。続いて、本発明者が実機で行なった試験の結果を説
明する。
FIG. 2 shows the overall schematic structure of the quenching tower. The quenching tower 30 is a vertical tower having an overall height of about 5.9 m and an internal volume of 27 m 3 , and a SK30 brick 35 is lined in the second area. Nozzles 31a, 31b and 31c for injecting cooling water through a valve 32 into the tower are provided in three stages.
In addition, 16 pieces are provided in each stage, and at least 1073K
The exhaust gas is rapidly cooled in a temperature range from (800 ° C.) to 353 K (80 ° C.). Most of the HCl and SO 2 contained in the exhaust gas are dissolved in water by the water cooling. The spray water amount from all injection nozzles is 320 to 360 m 3 / hr
It is. As a result of such cooling water injection, part of the dust and HC
The processing liquid containing l, H 2 SO 4 and the like accumulates in the processing liquid reservoir 31 from the bottom outlet 30b, and this processing liquid is reused as cooling water through neutralization by adding caustic soda. On the other hand, the exhaust gas cooled to 343 K (70 ° C.) or lower by the injection water is mainly composed of steam, CO 2 , O 2, etc., the flow rate is 400 to 450 Nm 3 / hr, and the dust amount is 0.1 to
0.2 g / Nm 3 (exhaust gas volume). Such cooling exhaust gas is discharged from an exhaust gas outlet 33 provided at the lower part of the tower. Next, the results of a test performed by the inventor on an actual machine will be described.

【0009】図3及び4には各種耐火材及び耐熱合金を
試験した状況が図解されている。試験した材料20は
カリガラス系耐酸キャスタブル(サワーアイゼン社製品
No.54LW,比較例)、耐火・耐酸キャスタブル
(日本ガイシ製品Ez3−2700、比較例),SK
30粘土質煉瓦(実施例)、抗火石、耐酸・耐アルカ
リキャスタブル(ヨータイ製品、AS−100、比較
例)粘土質耐酸・耐水キャスタブル(旭ガラス製品、
WPC−100、比較例),ハステロイC(比較例)
(登録商標)、オーステナイト系ステンレス鋼(比較
例)(日本冶金製品NAS64),SUS316(比較例)であ
り、〜はブロック(煉瓦)状のものであり、〜
は金属板(3t×1000×1000)である。これら
の材料のうち〜は図4に示すように冷却塔内の第2
領域に配列し、〜はこれらを固定するSUS316
L製固定治具の表面に〜を配列した。これら材料2
0はSUS316製固定治具23により前面を抑え、かつ耐酸
キャスター21(サワーアイゼン社製品No54LW)
内に埋め込んだ。なお22は急冷塔本体と入口ガス道と
の接続フランジである。2ヶ月の実操業後各材料20
〜を評価したところ次の結果が得られた。 上部端面の損耗が激しく、一部に欠損が見られた。下
部は良好であった。 骨材のセルベンが残っているものの、微粉部がなくな
り、損耗していた。 表面がざらついていたが損耗は微少であった。 損耗が激しく、内部組織も崩壊していた。 表面が大きく損耗していた。 表面が大きく損耗していた。 試験途中で金属板を止めているボルトが脱落したので
評価できなかった。 約2ヶ月で金属板よりは紙片と言わざるを得ない程度
まで腐食した。腐食による重量減は約90%である。 腐食による重量減は約20%であった。
FIGS. 3 and 4 illustrate the situation in which various refractory materials and heat-resistant alloys were tested. The tested materials 20 were potable glass acid-resistant castables (Sour Eisen Co., Ltd., product No. 54LW, comparative example), fire-resistant and acid-resistant castables (NGK product Ez3-2700, comparative example), SK.
30 clay brick (Example), anti-firestone, acid- and alkali-resistant castable (Yotai product, AS-100, comparative example) clay-acid- and water-resistant castable (Asahi glass product,
WPC-100, Comparative Example), Hastelloy C (Comparative Example)
(Registered trademark), austenitic stainless steel (comparative example) (Nippon Yakin's product NAS64) and SUS316 (comparative example).
Is a metal plate (3t × 1000 × 1000). Of these materials, as shown in FIG.
SUS316, which is arranged in a region and fixes these
Are arranged on the surface of the L-fixing jig. These materials 2
In the case of No. 0, the front surface is suppressed by the SUS316 fixing jig 23, and the acid-resistant caster 21 (Sour Eisen Co. product No. 54LW)
Embedded inside. Reference numeral 22 denotes a connection flange between the quenching tower main body and the inlet gas path. Each material 20 after actual operation for 2 months
The following results were obtained by evaluating. The upper end face was severely worn, and some parts were missing. The lower part was good. Although selven as an aggregate remained, the fine powder portion disappeared and was worn. The surface was rough but the wear was minimal. It was heavily worn and the internal structure had collapsed. The surface was heavily worn. The surface was heavily worn. Since the bolt holding the metal plate dropped off during the test, it could not be evaluated. In about two months, it corroded to a point where it had to be called a piece of paper rather than a metal plate. Weight loss due to corrosion is about 90%. Weight loss due to corrosion was about 20%.

【0010】この試験結果よりSK30が優れた性能を
もち、他の耐火物や耐熱鋼、耐熱合金は不良であること
が分る。
The test results show that SK30 has excellent performance, and that other refractories, heat-resistant steels and heat-resistant alloys are defective.

【0011】[0011]

【発明の効果】以上説明したように本発明によると、焼
却廃ガス急冷塔の補修による中断なく産業廃棄物の焼却
を実施でき、さらにまた排ガス急冷塔の寿命が延びるな
どの、実操業上重要な利点が達成される。
As described above, according to the present invention, incineration of industrial waste can be carried out without interruption due to repair of the incineration waste gas quenching tower, and further, the life of the exhaust gas quenching tower is prolonged. Benefits are achieved.

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

【図1】 本発明法における第1〜3領域を説明する模
式図である。
FIG. 1 is a schematic diagram illustrating first to third regions in the method of the present invention.

【図2】 本発明の一実施例に係る急冷塔の全体説明図
である。
FIG. 2 is an overall explanatory view of a quenching tower according to one embodiment of the present invention.

【図3】 各種供試材料を冷却塔のどの位置に配置した
かを図解する図である。
FIG. 3 is a diagram illustrating the positions of various test materials in a cooling tower.

【図4】 各種供試材料の配列平面図である。FIG. 4 is an arrangement plan view of various test materials.

【符号の説明】[Explanation of symbols]

1−急冷却塔 2−第1の領域 3−冷却ノズル 4−第3の領域 5−第2の領域 1-Quenching tower 2-First area 3-Cooling nozzle 4-Third area 5-Second area

───────────────────────────────────────────────────── フロントページの続き Fターム(参考) 3K065 AA24 AB01 AC01 BA01 HA02 HA03 3K070 DA03 DA05 DA37 DA77 4D002 AA02 AA19 BA02 BA13 BA14 CA01 DA35 4D020 AA06 AA10 BA23 BB03 CB25 CC14 CC17  ────────────────────────────────────────────────── ─── Continued on the front page F term (reference) 3K065 AA24 AB01 AC01 BA01 HA02 HA03 3K070 DA03 DA05 DA37 DA77 4D002 AA02 AA19 BA02 BA13 BA14 CA01 DA35 4D020 AA06 AA10 BA23 BB03 CB25 CC14 CC17

Claims (2)

【特許請求の範囲】[Claims] 【請求項1】 産業廃棄物を焼却して発生したダストを
含み、かつHCl濃度が0.3〜1.5%、SO2 濃度
が0.5〜3%、H2O飽和濃度である排ガスを、急冷
塔に下向きに導入し、主として急冷塔の内壁との熱伝導
により排ガスの冷却が起こる塔入口側第1の領域、主と
して塔内壁との熱伝導及び副次的に下記冷却水により冷
却が起こる第2の領域、及びスプレーノズルから噴射さ
れた冷却水により少なくとも973K(700℃)から
343K(70℃)の温度範囲を急冷する第3の領域を
順次通過せしめる産業廃棄物焼却排ガス急冷方法におい
て、SK30耐火物、もしくはSiO2 :65〜75% ,A
l2O3 :25〜30% ,Fe2O3 :5%以下の組成を有する
SK30耐火物同等品から実質的になる内壁を有する前
記第2領域を排ガスを通過せしめることを特徴とする産
業廃棄物焼却排ガス急冷方法。
1. Exhaust gas containing dust generated by incineration of industrial waste, having an HCl concentration of 0.3 to 1.5%, an SO 2 concentration of 0.5 to 3%, and a H 2 O saturation concentration. Is introduced downward into the quenching tower, and the first area on the tower inlet side where the exhaust gas is cooled mainly by heat conduction with the inner wall of the quenching tower, mainly cooled by heat conduction with the inner wall of the tower and secondarily by the following cooling water A method of quenching industrial waste incineration flue gas in which the wastewater is sequentially passed through a second region in which cooling occurs and a third region in which a temperature range of at least 973K (700 ° C) to 343K (70 ° C) is rapidly cooled by cooling water injected from a spray nozzle. SK30 refractory or SiO 2 : 65-75% , A
l 2 O 3 : 25-30% , Fe 2 O 3: SK30 refractory industrial waste incineration flue gas quenching method of the second region, characterized in that allowed to pass through the exhaust gas having an inner wall consisting essentially equivalent having a composition of 5%.
【請求項2】 産業廃棄物を焼却して発生したダストを
含む排ガスを、下向きに導入する入口と、主として塔の
内壁との熱伝導により冷却が起こる塔入口側第1の領域
と、主として塔内壁との熱伝導により副次的に下記冷却
水の一部により冷却が起こり、SK30耐火物、もしくはSi
O2 :65〜75% ,Al2O3 :25〜30% , Fe2O3
5%以下の組成を有するSK30耐火物同等品から実質
的になる内壁を有する第2の領域と、スプレーノズルか
ら噴射された冷却水により少なくとも973K(700
℃)から343K(70℃)の温度範囲を急冷する第3
の領域とを含んでなる産業廃棄物焼却排ガス急冷塔。
2. An inlet for introducing exhaust gas containing dust generated by incineration of industrial waste downward, a first area on a tower inlet side where cooling is mainly performed by heat conduction with an inner wall of the tower, As a result of the heat conduction with the inner wall, a part of the following cooling water cools down, and SK30 refractory or Si
O 2: 65~75% , Al 2 O 3 : 25-30% , Fe 2 O 3 :
A second region having an inner wall substantially consisting of an SK30 refractory equivalent having a composition of 5% or less and at least 973 K (700
C) to 343K (70 ° C)
And an industrial waste incineration flue gas quenching tower.
JP2000096889A 2000-03-31 2000-03-31 Industrial waste incineration exhaust gas quenching method and quenching tower Expired - Fee Related JP4673464B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2000096889A JP4673464B2 (en) 2000-03-31 2000-03-31 Industrial waste incineration exhaust gas quenching method and quenching tower

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2000096889A JP4673464B2 (en) 2000-03-31 2000-03-31 Industrial waste incineration exhaust gas quenching method and quenching tower

Publications (2)

Publication Number Publication Date
JP2001276565A true JP2001276565A (en) 2001-10-09
JP4673464B2 JP4673464B2 (en) 2011-04-20

Family

ID=18611588

Family Applications (1)

Application Number Title Priority Date Filing Date
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Country Status (1)

Country Link
JP (1) JP4673464B2 (en)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2015148398A (en) * 2014-02-07 2015-08-20 Jx日鉱日石金属株式会社 Refractory structure of cooling tower inner wall and operation method of cooling tower
KR101565761B1 (en) * 2014-11-24 2015-11-04 오홍근 Filtration system

Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5391075A (en) * 1977-01-24 1978-08-10 Hitachi Plant Eng & Constr Co Ltd Washing tower of waste gas

Patent Citations (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5391075A (en) * 1977-01-24 1978-08-10 Hitachi Plant Eng & Constr Co Ltd Washing tower of waste gas

Cited By (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2015148398A (en) * 2014-02-07 2015-08-20 Jx日鉱日石金属株式会社 Refractory structure of cooling tower inner wall and operation method of cooling tower
KR101565761B1 (en) * 2014-11-24 2015-11-04 오홍근 Filtration system
WO2016085032A1 (en) * 2014-11-24 2016-06-02 오홍근 Dust collection system

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