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JPS609550B2 - Method for recovering waste heat from coke oven gas - Google Patents
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JPS609550B2 - Method for recovering waste heat from coke oven gas - Google Patents

Method for recovering waste heat from coke oven gas

Info

Publication number
JPS609550B2
JPS609550B2 JP52123799A JP12379977A JPS609550B2 JP S609550 B2 JPS609550 B2 JP S609550B2 JP 52123799 A JP52123799 A JP 52123799A JP 12379977 A JP12379977 A JP 12379977A JP S609550 B2 JPS609550 B2 JP S609550B2
Authority
JP
Japan
Prior art keywords
coke oven
oven gas
liquid
gas
tower
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
JP52123799A
Other languages
Japanese (ja)
Other versions
JPS5456607A (en
Inventor
正治郎 井上
宏紀 安西
孝志 亀田
孝 小山田
一夫 多木
▲ただし▼ 中込
有佐 岡崎
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.)
Mitsui Mining Co Ltd
Kawasaki Motors Ltd
Original Assignee
Mitsui Mining Co Ltd
Kawasaki Jukogyo KK
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 Mitsui Mining Co Ltd, Kawasaki Jukogyo KK filed Critical Mitsui Mining Co Ltd
Priority to JP52123799A priority Critical patent/JPS609550B2/en
Priority to DE19782844607 priority patent/DE2844607A1/en
Publication of JPS5456607A publication Critical patent/JPS5456607A/en
Publication of JPS609550B2 publication Critical patent/JPS609550B2/en
Expired legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10KPURIFYING OR MODIFYING THE CHEMICAL COMPOSITION OF COMBUSTIBLE GASES CONTAINING CARBON MONOXIDE
    • C10K1/00Purifying combustible gases containing carbon monoxide
    • C10K1/08Purifying combustible gases containing carbon monoxide by washing with liquids; Reviving the used wash liquors
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00Technologies relating to chemical industry
    • Y02P20/10Process efficiency
    • Y02P20/129Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Combustion & Propulsion (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Organic Chemistry (AREA)
  • Industrial Gases (AREA)
  • Physical Water Treatments (AREA)

Description

【発明の詳細な説明】 本発明は現在廃棄されているコークス炉ガスからの低温
の廃熱をコークス炉ガスの冷却設備を大幅に変更するこ
となく、有効に回収する方法に関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for effectively recovering low-temperature waste heat from currently discarded coke oven gas without significantly changing coke oven gas cooling equipment.

従来、第1図のフローシートに示す如くコークス炉1か
ら発生する約100ぴ○のコークス炉ガスは0ドライメ
ーン3で散布されるガス液4によって約80qoまで冷
却される。
Conventionally, as shown in the flow sheet of FIG. 1, about 100 qo of coke oven gas generated from a coke oven 1 is cooled down to about 80 qo by gas liquid 4 sprayed in a 0 dry main 3.

ついで間接ガス冷却器6及び/又は直接ガス冷却器7で
約35q0まで冷却される。直接ガス冷却器7では希安
水冷却器8で海水又夕は冷水塔循環水9によって冷却さ
れた希安水10が循環使用されている。
It is then cooled down to about 35q0 by an indirect gas cooler 6 and/or a direct gas cooler 7. In the direct gas cooler 7, diluted diluted water 10 cooled by seawater in diluted diluted water cooler 8 or cooled by circulating water 9 from a cooling tower is circulated.

かくの如くコークス炉ガス2の保有熱はガス液4、海水
9又は冷水塔循環水9に移行し、ついで大気中に放熱、
温海水お放流によって系外に放出されている。0 上記
の如く、コークス炉ガスの保有する莫大な熱が全く利用
されずに貴重なエネルギー資源の浪費となっているばか
りでなく、冷煤として海水を使用すれば多量の温海水の
排出に伴ない、赤潮発生などの公害の原因となる場合が
ある。
In this way, the heat retained in the coke oven gas 2 is transferred to the gas liquid 4, seawater 9, or cooling water tower circulating water 9, and then radiated into the atmosphere.
It is being released outside the system by releasing warm seawater. 0 As mentioned above, not only is the huge amount of heat possessed by coke oven gas not used at all, resulting in a waste of valuable energy resources, but if seawater is used as cold soot, a large amount of warm seawater will be discharged. It may cause pollution such as red tide.

ここにコークス炉ガスの保有熱の1例として例えばコー
クス炉ガス135 00州m3/時間(H)を発生させ
る場合の熱バランスを示すと次の通りである。
Here, as an example of the retained heat of coke oven gas, the heat balance in the case where coke oven gas is generated at 13,500 m3/hour (H) is as follows.

(i) ドライメーンで、 コークス炉ガス→大気放熱 8000,000KCal/日 (ii} ガス循環ラインで、 コークス炉ガス→ガス液→大気放熱 15000,000 〃 側 聞懐及び直接ガス冷却器で、 コークス炉ガス→海水→温海水放熱 ー 〆 74000,000 〃 希安水 合 計 97000,000 〃 冷煤として30午○の海水を使用すると約53℃の温海
水が32皿h3/日も排出されることになる。
(i) In the dry main, coke oven gas → atmospheric heat radiation 8,000,000 KCal/day (ii) In the gas circulation line, coke oven gas → gas liquid → atmospheric heat radiation 15,000,000 〃 Side In the pipe and direct gas cooler, coke Furnace gas → seawater → warm seawater heat radiation - 〆 74,000,000 〃 Diluted ammonium water total 97,000,000 〃 If 30 pm seawater is used as cold soot, 32 plates of warm seawater at about 53℃ will be discharged per day. become.

一方コークス工場ではコークス炉ガスに含有される硫化
水素、シアン化水素、アンモニヤ「軽油などの有害物質
除去用又は有害物質回収用に吸収塔、放散塔などからな
る各種ガス精製設備や廃液処理設備など多量の熱を必要
とする設備が共存しているのでコークス炉ガス保有熱の
有効利用が望まれている。本発明はこの要望に応えてコ
ークス炉ガスの冷却設備を現状から大幅に変更すること
なくコークス炉ガスの保有熱を有効に利用することを目
的とするコークス炉ガスの廃熱を回収する方法に関する
もので、コークス炉ガス精製設備の放散塔からの有害物
質又は有用物質が除去された貧吸収液をコークス炉ガス
の冷却用に使用し、該熱交換された貧吸収液を該放散塔
に戻し、コークス炉ガス精製設備の吸収塔からの有害物
質又は有用物質を含有した富吸収液を加熱して上記放散
塔に供V給することによって、該放散塔で有害物質又は
有用物質を分離せしめ、貧吸収液として、コークス炉ガ
ス冷却用並びに吸収※に循環して使用して上記本発明の
目的を達成することができた。
On the other hand, in coke factories, a large amount of gas purification equipment including absorption towers, stripping towers, etc. and waste liquid treatment equipment are used to remove or recover harmful substances such as hydrogen sulfide, hydrogen cyanide, and ammonia contained in coke oven gas. Since equipment that requires heat coexists, it is desired to make effective use of the heat retained in coke oven gas.In response to this demand, the present invention has been developed to efficiently utilize coke oven gas cooling equipment without significantly changing the current coke oven gas cooling equipment. This relates to a method for recovering waste heat from coke oven gas, which aims to effectively utilize the heat retained in the oven gas, and is a method for recovering waste heat from coke oven gas, which is a poor absorption method from which harmful or useful substances have been removed from the dispersion tower of coke oven gas purification equipment. The liquid is used for cooling coke oven gas, the heat-exchanged poor absorption liquid is returned to the stripping tower, and the rich absorption liquid containing harmful or useful substances from the absorption tower of the coke oven gas purification equipment is heated. By supplying V to the stripping tower, harmful substances or useful substances are separated in the stripping tower, and as a poor absorption liquid, the liquid is circulated for coke oven gas cooling and absorption*, and is used in the above-mentioned method of the present invention. I was able to achieve my goal.

この場合、コークス炉ガス精製設備に真空、低温下での
放散操作を伴うプロセス例えば硫化水素除去におけるバ
キウムカーボネート法等を導入するか又は真空蒸発など
低温による濃縮操作を伴なう排液処理プロセスを導入す
ることによって間接ガス冷却器をリボィラーおよび/又
は加熱器として使用し、更にはドライメーンを循環する
熱いガス液を熱源とするりボイラー及び/又は放熱器を
設置して低温の廃熱を利用する。さらに必要に応じてガ
ス液の循環配管に保温を施行することにより、熱の利用
率を向上せしめることが可能である。
In this case, a process that involves a dissipation operation in a vacuum and at low temperatures is introduced into the coke oven gas purification equipment, such as the vacium carbonate method for hydrogen sulfide removal, or a waste liquid treatment process that involves concentration operations at low temperatures such as vacuum evaporation. The indirect gas cooler can be used as a reboiler and/or heater by introducing a boiler and/or a radiator to use the hot gas liquid circulating in the dry main as a heat source. Make use of it. Furthermore, by insulating the gas liquid circulation piping as necessary, it is possible to improve the heat utilization efficiency.

次に本発明を実施例によって詳細説明する。Next, the present invention will be explained in detail by way of examples.

実施例 1(本発明を硫化水素除去設備に使用した場合
)第2図にその実施の1例を示す如く、コークス炉1か
らのコークス炉ガス2は第1図の場合と同様にドライメ
ーン3で散布されるガス液4によって約80qoまで冷
却され、ついで間接ガス冷却器6及び直接ガス冷却器7
で約35q0に冷却される。間接ガス冷却器6は従来の
海水又は冷水塔循環水の代りに有害物質放散繋12のボ
トムよりの貧吸収液15を通じ、リボィラーとして使用
される。熱量が不足する場合にはドライメーン3からの
熱いガス液を熱源とするりボイラー17を設置する。か
くて間接ガス冷却器6を出た貧吸収液15は有害物質放
散塔12の加熱用に送給され、有害物質放散塔12を出
た加熱水の1部は再び間接ガス冷却器6及びリボイラー
17に送給されて上記の様に使用される。残部は熱交換
器14、吸収液冷却器13を経て吸収塔111こ送給さ
れてコークス炉ガスの有害物質吸収用に供する。有害物
質を吸収した富吸収液16は有害物質放散塔12に送給
されも間接冷却器6よりの貧吸収液の加熱循環水によっ
て加熱されて有害物質、例えばこの場合には硫化水素1
8が放散される。この場合必要に応じてガス液循環配管
に保温を施工する。硫化水素を6.16夕/Nm3を含
むコークス炉ガス13500州m3/日の処理に上記の
如く本発明を使用したところコークス炉ガスはドライメ
ーンで散布される200仇h3/日のガス液で81qo
まで冷却された。
Embodiment 1 (When the present invention is used in hydrogen sulfide removal equipment) As shown in FIG. 2, an example of its implementation, the coke oven gas 2 from the coke oven 1 is transferred to the dry main 3 as in the case of FIG. It is cooled to about 80 qo by the gas liquid 4 sprayed at
It is cooled to about 35q0. The indirect gas cooler 6 is used as a reboiler by passing the poor absorption liquid 15 from the bottom of the harmful substance dissipation link 12 instead of the conventional seawater or cooling tower circulating water. If the amount of heat is insufficient, a boiler 17 is installed using hot gas liquid from the dry main 3 as a heat source. In this way, the poor absorption liquid 15 that has exited the indirect gas cooler 6 is sent to the harmful substance dispersion tower 12 for heating, and a portion of the heated water that has exited the harmful substance dispersion tower 12 is returned to the indirect gas cooler 6 and the reboiler. 17 and used as described above. The remainder is sent to the absorption tower 111 via the heat exchanger 14 and the absorption liquid cooler 13, and is used for absorbing harmful substances from the coke oven gas. The rich absorption liquid 16 that has absorbed harmful substances is sent to the harmful substance dispersion tower 12 and is heated by the heated circulation water of the poor absorption liquid from the indirect cooler 6 to remove harmful substances, such as hydrogen sulfide 1 in this case.
8 is dissipated. In this case, install heat insulation on the gas liquid circulation piping as necessary. When the present invention was used as described above to treat 13,500 m3/day of coke oven gas containing hydrogen sulfide at 6.16 m3/day, the coke oven gas was a gas liquid dispersed in the dry main at 200 m3/day. 81qo
cooled to.

コークス炉ガスから熱を奪ったガス液は大気中に放熱し
て約75午0になった。常時運転される5基の間接ガス
冷却器のうち2基をリボィラーとして使用した。
The gas liquid, which took heat from the coke oven gas, radiated heat into the atmosphere and the temperature reached approximately 75:00. Two of the five indirect gas coolers in constant operation were used as reboilers.

この結果放散塔ボトムの貧吸収液1734m3/日は5
3qoから6が0まで加熱され、一方コークス炉ガスは
81qoから6roまで冷却された。
As a result, the poor absorption liquid at the bottom of the stripping tower is 1734 m3/day.
3qo to 6 was heated to 0, while coke oven gas was cooled from 81qo to 6ro.

(他の3基は通常の間接ガス冷却器として運転使用した
。)又有害物質放散塔の不足熱を補うため及び熱を調節
するためにガス液を熱源とするボイラーを設備し、75
qoのガス液100皿3/日を通じ、有害物質放散塔ボ
トムの貧吸収液417m3/日を5チ0から65タ℃ま
で加熱した。加熱された貧吸収液は約100トル(To
m)の真空で操作される有害物質放散塔ボトムに戻り減
圧されてスチームを発生させ、有害物質放散塔頂部から
供V給される富吸収液から硫化水素を放散せしめた。
Z間接ガス冷却器から出たガスは
直接ガス冷却器にて循環される希安水で3FCまで冷却
された。この結果コークス炉ガスからは80〜90%の
硫化水素が除去され、40〜6畔容量パーセントの濃厚
硫化水素ガスが回収された。有害物質放散繁でのスZチ
ーム消費は皆無であった。本発明を使用しない通常の場
合は約38トン/時のスチームが必要であった。
(The other three units were operated as ordinary indirect gas coolers.) In addition, a boiler using gas liquid as a heat source was installed to compensate for the lack of heat in the hazardous substance diffusion tower and to adjust the heat.
417 m3/day of the poor absorption liquid at the bottom of the harmful substance dispersion tower was heated from 0 to 65 degrees Celsius through 100 plates of gas liquid of 3/day. The heated poor absorbent liquid has a temperature of about 100 Torr (To
The mixture was returned to the bottom of the hazardous substance stripping tower operated in a vacuum and the pressure was reduced to generate steam, thereby dissipating hydrogen sulfide from the V-rich absorption liquid supplied from the top of the hazardous substance stripping column.
The gas coming out of the Z indirect gas cooler was cooled to 3FC with diluted water circulated in the direct gas cooler. As a result, 80-90% of hydrogen sulfide was removed from the coke oven gas, and concentrated hydrogen sulfide gas of 40-6% by volume was recovered. There was no consumption of steam due to the high release of harmful substances. In the normal case without the use of the present invention, approximately 38 tons/hour of steam was required.

又コークス炉ガス冷却用の海水は100仇h3/時減少
させることができた。
2実施例 2(本発明のコークス炉ガスの廃熱を
活性汚泥処理廃水の濃縮処理設備に使用した場合)第3
図にその実施の1例を示す如く、コークス炉1からのコ
ークス炉ガス2は第1図の場合と同2様にドライメーン
3で散布されるガス液4によって約80℃に冷却され、
ついで間援ガス冷却器6に通じて冷却される。
In addition, the amount of seawater used to cool coke oven gas could be reduced by 100 h3/hour.
2 Example 2 (When the waste heat of coke oven gas of the present invention is used in a concentration treatment facility for activated sludge treatment wastewater) Third
As an example of its implementation is shown in the figure, the coke oven gas 2 from the coke oven 1 is cooled to about 80°C by the gas liquid 4 sprayed by the dry main 3, as in the case of Fig. 1.
The gas is then passed through an intervening gas cooler 6 to be cooled.

間接ガス冷却器6は海水又は冷水塔循環水の代りに冷水
塔又は真空蒸発器21を出た活性汚泥処理廃水20を通
じ、加熱器として使用する。間接ガス冷却器6を出た加
熱された活性汚泥処理廃水20は冷水塔又は真空蒸発器
21に送給して活性汚泥処理廃水19の蒸発用に循環使
用する。この場合間接ガス冷却器6の伝熱管は廃水の腐
食性に対応して材質を変更する。冷水塔又は真空蒸発器
21での濃縮用熱量が不足する場合はドライメーン3か
らの熱いガス液4を熱源とする廃液加熱器22を設置し
て、活性汚泥処理廃水20の1部を循環する。加熱され
た活性汚泥処理廃水20‘ま冷却塔又は真空蒸発器21
で水分の蒸発により濃縮、冷却され再び間接ガス冷却器
6、廃液加熱器22に循環される。
The indirect gas cooler 6 is used as a heater by passing activated sludge treated wastewater 20 from the cooling tower or vacuum evaporator 21 instead of seawater or circulating water from the cooling tower. The heated activated sludge treated wastewater 20 exiting the indirect gas cooler 6 is fed to a cooling tower or a vacuum evaporator 21 and recycled for evaporation of the activated sludge treated wastewater 19. In this case, the material of the heat exchanger tubes of the indirect gas cooler 6 is changed depending on the corrosivity of the wastewater. If the amount of heat for concentration in the cooling tower or vacuum evaporator 21 is insufficient, a waste liquid heater 22 using the hot gas liquid 4 from the dry main 3 as a heat source is installed to circulate a part of the activated sludge treated waste water 20. . Heated activated sludge treated wastewater 20' cooling tower or vacuum evaporator 21
The water is concentrated and cooled by evaporation of moisture, and is again circulated to the indirect gas cooler 6 and the waste liquid heater 22.

濃縮された廃水は系外に抜き出され焼却又は結晶分離な
ど(図示せず)で最終的な処理を受ける。コークス炉ガ
ス135 00帆m3/日を発生するコークス工場に於
いて発生する余剰安水を活性汚泥処理した廃水61.8
h3/日を本発明で処理した。
The concentrated wastewater is extracted from the system and undergoes final treatment such as incineration or crystal separation (not shown). Wastewater 61.8% is treated with activated sludge from surplus ammonium water generated in a coke factory that generates 135,000 m3/day of coke oven gas.
h3/day were treated with the invention.

活性汚泥処理廃水の性状を濃縮廃水と共に第1表に示し
た。常時運転される5基の間接ガス冷却器のうち3基を
廃液加熱器として使用し、390の廃水を間接ガス冷却
器に16胸h3/日通して54qOまで加熱した。
The properties of the activated sludge treated wastewater are shown in Table 1 together with the concentrated wastewater. Three of the five indirect gas coolers in continuous operation were used as waste liquid heaters, and 390 ml of wastewater was heated to 54 qO by passing through the indirect gas coolers for 16 h3/day.

コークス炉ガスは81℃から520まで冷却された。他
の2基は通常の間接ガス冷却器として使用した。54℃
まで加熱された廃水は自然通風式冷水塔21に導ぴき空
気中に水分を蒸発させることによって35℃まで冷却、
濃縮され再び間接ガス冷却器6に循環した。
The coke oven gas was cooled from 81°C to 520°C. The other two were used as conventional indirect gas coolers. 54℃
The wastewater that has been heated to 35°C is led to a natural draft cooling tower 21 where it is cooled to 35°C by evaporating moisture into the air.
It was concentrated and circulated to the indirect gas cooler 6 again.

この結果、自然通風式冷却水塔21に於て弘.2トン/
時の水分が蒸発し第1表に示す性状の濃縮廃水が7.3
h3/日抜き出された。
As a result, in the natural draft cooling water tower 21. 2 tons/
When the water content evaporates, the concentrated wastewater with the properties shown in Table 1 becomes 7.3
Extracted h3/day.

この濃縮廃水は通常の液中燃焼法又は廃液燃焼法によっ
て簡単に焼却することができ廃水を完全になくすことが
できた。
This concentrated wastewater could be easily incinerated by the usual submerged combustion method or waste liquid combustion method, and the wastewater could be completely eliminated.

本実施例に於ては廃水の濃縮に必要な熱はすべてコーク
ス炉ガスの保有熱によってまかなわれた。
In this example, all the heat necessary for concentrating the wastewater was provided by the retained heat of the coke oven gas.

スチームを使用すれば約58トン/日必要である。If steam is used, approximately 58 tons/day is required.

又コークス炉ガス冷却用の海水は160肌3/H減少さ
せることができた。第1表 (実施例2,3における廃水の性状) 本実施例と従来法の比較を以下に述べる。
In addition, the amount of seawater used to cool coke oven gas could be reduced by 160 skin 3/H. Table 1 (Properties of wastewater in Examples 2 and 3) A comparison between this example and the conventional method will be described below.

活性汚泥処理後の廃水を再処理する方法としては、‘1
’コークスの消火用水として使用する方法ト【2)活性
炭の使用により吸着処理する方法、{31濃縮処理後焼
却する方法等が知られているが、いづれも種々の欠点を
有している。例えば、コークスの消火用水として使用す
る方法ではコークスの着臭、腐食性蒸気が多量に発生す
ることなど、活性炭による吸着処理法では、高価な活性
炭の使用により設備費、運転経費が高いことなど、濃縮
処理後焼却する方法では、廃水の濃縮にスチーム等の熱
エネルギーを多量に必要とすること、設備費が高価であ
ることなどが挙げられる。一方、本実施例による方法で
は、従釆の濃縮処理法の欠点を解決した極めて有利な方
法である。
'1 is a method for reprocessing wastewater after activated sludge treatment.
Methods for using coke as fire extinguishing water (2) A method of adsorption treatment using activated carbon, a method of incineration after concentration treatment, etc. are known, but each method has various drawbacks. For example, the method of using coke as fire extinguishing water causes the coke to smell and generates a large amount of corrosive vapor, while the adsorption treatment method using activated carbon requires high equipment and operating costs due to the use of expensive activated carbon. The method of incineration after concentration treatment requires a large amount of thermal energy such as steam to concentrate the wastewater, and the equipment cost is high. On the other hand, the method according to this embodiment is an extremely advantageous method that solves the drawbacks of the secondary concentration method.

即ち廃水の濃縮に必要とされる多量の熱エネルギーを、
コークス炉ガスの廃熱を回収することによりまかない、
スチーム等の新たな熱エネルギーを不要とするばかりで
なく、通常コークス炉ガスの精製に必要とされる設備を
相互に利用することによって廃水の濃縮を達成するため
、新たに追加すべき設備並びに敷地が殆んど不要となり
、著しく経済性を発揮することができ、更に本方法を通
常の液中燃焼法又は廃水燃焼法と組合せることによって
、廃水を完全になくすことができる。以上実施例によっ
て説明した如く、本発明によってコークス炉ガス冷却設
備において従来使用されている間接ガス冷却器をそのま
ま或は一部材質を変更すること及びガス液循環系に保温
ならびに3熱交換器を設置することによりコークス炉ガ
スの保有熱をコークス炉ガスの精製や廃液濃縮処理など
の熱源として有効に利用し、コークス工場でのスチーム
などの熱エネルギー消費量を減少させると共に、袷蝶と
しての海水消費量を減少させることにより温海水の排出
量を減少させることができる。更に廃水を従来の液中燃
焼又は廃液燃焼設備で経済的に処理される濃度にまで濃
縮できるのでこれらの設備との組合せによってコークス
工場からの廃水を完全に無くすることができる。
In other words, the large amount of thermal energy required for concentrating wastewater is
This is covered by recovering waste heat from coke oven gas.
In order to not only eliminate the need for new thermal energy such as steam, but also to achieve wastewater concentration by mutually using the equipment normally required for refining coke oven gas, new equipment and sites need to be added. is almost unnecessary, making it extremely economical. Furthermore, by combining this method with a normal submerged combustion method or wastewater combustion method, wastewater can be completely eliminated. As explained above with reference to the embodiments, the present invention allows the indirect gas cooler conventionally used in coke oven gas cooling equipment to be used as it is or to partially change the material, and to add heat insulation and three heat exchangers to the gas-liquid circulation system. By installing this system, the retained heat of coke oven gas can be effectively used as a heat source for refining coke oven gas and concentrating waste liquid, reducing thermal energy consumption such as steam in coke factories, and reducing the amount of seawater used as a butterfly. By reducing consumption, the amount of warm seawater discharged can be reduced. Furthermore, since wastewater can be concentrated to a concentration that can be economically processed with conventional submerged combustion or wastewater combustion equipment, in combination with these equipments, wastewater from coke plants can be completely eliminated.

又、コークス工場で通常用いられている設備を使用する
ので廃水濃縮のための追加設備は殆んど不要、又は若干
の機器の追加のみで良く、著しく経済的である。
In addition, since the equipment normally used in coke factories is used, there is almost no need for additional equipment for concentrating wastewater, or only a few additions of equipment are required, making it extremely economical.

更に廃水処理用敷地が殆.んど不要の利点がある。Furthermore, most of the sites are for wastewater treatment. It has the advantage of not being necessary.

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

第1図はコ−クス炉ガスの冷却設備のフローシート、第
2図は本発明を有害物質放散塔に使用した一実施例のフ
ローシート、第3図は本発明を活性汚泥処理廃水の濃縮
処理設備に使用した−実施例のフローシートを示す。 1…・・・コークス炉、2・・・…コークス炉ガス、3
……ドライメーン、4……ガス液、5・・・…タールデ
カンター、6・・・・・・間接ガス冷却器、7・・・・
・・直接ガス冷却器、8…・・・希安水冷却器、9・・
・・・・海水又は冷水塔循環水、10・・・・・・希安
水、11・…・・吸収塔、12・・・・・・有害物質放
散塔、13・・・・・・吸収液冷却器、14・…・・吸
収液熱交換器、15・・・・・・貧吸収液、16・…・
・富吸収液、17・・・・・・リボィラー、18・・・
・・・硫化水素、19・・・・・・活性汚泥処理廃液、
20…・・・三農縞廃水、2 1…・・・冷水塔又は真
空蒸発器、22・・・・・・廃液加熱器。 第1図 第2図 第3図
Fig. 1 is a flow sheet of coke oven gas cooling equipment, Fig. 2 is a flow sheet of an example in which the present invention is used in a hazardous substance dispersion tower, and Fig. 3 is a flow sheet of an embodiment in which the present invention is used for concentration of activated sludge treated wastewater. A flow sheet of an example used in a processing facility is shown. 1...Coke oven, 2...Coke oven gas, 3
...Dry main, 4...Gas liquid, 5...Tar decanter, 6...Indirect gas cooler, 7...
... Direct gas cooler, 8... Diluted water cooler, 9...
... Sea water or cooling water tower circulating water, 10 ... Diluted water, 11 ... Absorption tower, 12 ... Harmful substance dispersion tower, 13 ... Absorption Liquid cooler, 14... Absorption liquid heat exchanger, 15... Poor absorption liquid, 16...
- Rich absorption liquid, 17... Reboiler, 18...
...Hydrogen sulfide, 19...Activated sludge treatment waste liquid,
20... Sannojima wastewater, 2 1... Cold water tower or vacuum evaporator, 22... Waste liquid heater. Figure 1 Figure 2 Figure 3

Claims (1)

【特許請求の範囲】 1 コークス炉ガス精製設備の放散塔からの有害物質又
は有用物質が除去された貧吸収液をコークス炉ガスの冷
却用に使用し、該熱交換された貧吸収液を該放散塔に戻
し、コークス炉ガス精製設備の吸収塔からの有害物質又
は有用物質を含有した富吸収液を加熱して上記の放散塔
に供給することによって、該放散塔で有害物質又は有用
物質を分離せしめ、貧吸収液として、コークス炉ガスの
冷却用並びに吸収塔に循環して使用することを特徴とす
るコークス炉ガスの廃熱を回収する方法。 2 ドライメーン3から出たガス液4と間接ガス吸収器
6から出た貧吸収液15とを共に放散塔12に供給して
吸収塔11からの富吸収液から硫化水素を除去する加熱
用に使用される特許請求の範囲第1項記載のコークス炉
ガスの廃熱を回収する方法。 3 活性汚泥処理廃液19の濃度廃液をコークス炉ガス
の冷却用としてドライメーン3に散布するガス液4及び
間接冷却器6の冷却用として使用し、熱交換された該濃
縮廃液20を該活性汚泥処理廃液の廃液濃縮用として廃
液の濃縮処理設備21に循環使用する特許請求の範囲第
1項記載のコークス炉ガスの廃熱を回収する方法。
[Claims] 1. A poor absorption liquid from which harmful or useful substances have been removed from a dispersion tower of coke oven gas purification equipment is used for cooling coke oven gas, and the heat-exchanged poor absorption liquid is used to cool coke oven gas. By returning the rich absorption liquid containing harmful or useful substances from the absorption tower of the coke oven gas purification equipment to the stripping tower and heating it and supplying it to the stripping tower, the harmful or useful substances are removed in the stripping tower. A method for recovering waste heat from coke oven gas, characterized in that it is separated and used as a poor absorption liquid for cooling coke oven gas and by circulating it in an absorption tower. 2 Gas liquid 4 from the dry main 3 and poor absorption liquid 15 from the indirect gas absorber 6 are both supplied to the stripping tower 12 for heating to remove hydrogen sulfide from the rich absorption liquid from the absorption tower 11. A method for recovering coke oven gas waste heat according to claim 1. 3. The concentrated waste liquid 19 of the activated sludge treatment waste liquid is used for cooling the coke oven gas and the gas liquid 4 sprayed on the dry main 3 and for cooling the indirect cooler 6, and the heat-exchanged concentrated waste liquid 20 is used as the activated sludge. A method for recovering coke oven gas waste heat according to claim 1, wherein the waste heat is recycled to a waste liquid concentration treatment facility 21 for concentrating treated waste liquid.
JP52123799A 1977-10-14 1977-10-14 Method for recovering waste heat from coke oven gas Expired JPS609550B2 (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP52123799A JPS609550B2 (en) 1977-10-14 1977-10-14 Method for recovering waste heat from coke oven gas
DE19782844607 DE2844607A1 (en) 1977-10-14 1978-10-13 Heat recovery from coke-oven gas - using liq. obtained from scrubbing as coolant for the gas

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP52123799A JPS609550B2 (en) 1977-10-14 1977-10-14 Method for recovering waste heat from coke oven gas

Publications (2)

Publication Number Publication Date
JPS5456607A JPS5456607A (en) 1979-05-07
JPS609550B2 true JPS609550B2 (en) 1985-03-11

Family

ID=14869593

Family Applications (1)

Application Number Title Priority Date Filing Date
JP52123799A Expired JPS609550B2 (en) 1977-10-14 1977-10-14 Method for recovering waste heat from coke oven gas

Country Status (2)

Country Link
JP (1) JPS609550B2 (en)
DE (1) DE2844607A1 (en)

Families Citing this family (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN102168888B (en) * 2011-02-25 2013-02-27 清华大学 Contact-type advanced recycling system for waste heat of low-temperature flue gas
CN104629816B (en) * 2015-01-30 2016-09-28 济南冶金化工设备有限公司 From the preliminary chiller of refrigeration mode coal oven dithio-gas

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
DE1032465B (en) * 1955-11-24 1958-06-19 Still Fa Carl Process for the extraction of tar, ammonia and ammonia water from gases of dry distillation
JPS52148505A (en) * 1976-06-05 1977-12-09 Kawasaki Heavy Ind Ltd Recovering of sensible heat of coke oven gas and power generation thereby

Also Published As

Publication number Publication date
DE2844607A1 (en) 1979-05-03
JPS5456607A (en) 1979-05-07

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