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JP2687222B2 - Exhaust gas treatment method - Google Patents

Exhaust gas treatment method

Info

Publication number
JP2687222B2
JP2687222B2 JP63147956A JP14795688A JP2687222B2 JP 2687222 B2 JP2687222 B2 JP 2687222B2 JP 63147956 A JP63147956 A JP 63147956A JP 14795688 A JP14795688 A JP 14795688A JP 2687222 B2 JP2687222 B2 JP 2687222B2
Authority
JP
Japan
Prior art keywords
exhaust gas
iron
concentration
liquid
mol
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 - Lifetime
Application number
JP63147956A
Other languages
Japanese (ja)
Other versions
JPH01317528A (en
Inventor
邦裕 小倉
英次 豊田
健吾 安藤
満彦 浜井
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.)
Toyota Motor Corp
Original Assignee
Toyota Motor Corp
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 Toyota Motor Corp filed Critical Toyota Motor Corp
Priority to JP63147956A priority Critical patent/JP2687222B2/en
Priority to KR1019890000763A priority patent/KR910010242B1/en
Publication of JPH01317528A publication Critical patent/JPH01317528A/en
Application granted granted Critical
Publication of JP2687222B2 publication Critical patent/JP2687222B2/en
Anticipated expiration legal-status Critical
Expired - Lifetime legal-status Critical Current

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Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B22CASTING; POWDER METALLURGY
    • B22CFOUNDRY MOULDING
    • B22C9/00Moulds or cores; Moulding processes
    • B22C9/08Features with respect to supply of molten metal, e.g. ingates, circular gates, skim gates
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01DSEPARATION
    • B01D53/00Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
    • B01D53/34Chemical or biological purification of waste gases

Landscapes

  • Engineering & Computer Science (AREA)
  • Chemical & Material Sciences (AREA)
  • Health & Medical Sciences (AREA)
  • Biomedical Technology (AREA)
  • Environmental & Geological Engineering (AREA)
  • Analytical Chemistry (AREA)
  • General Chemical & Material Sciences (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Mechanical Engineering (AREA)
  • Treating Waste Gases (AREA)

Description

【発明の詳細な説明】 [産業上の利用分野] 本発明は、排ガス中のフェノールやホルムアルデヒド
等の還元性物質を過酸化水素と第1鉄イオンを含む吸収
液により洗浄除去すると共に、廃液中の鉄スラッジの処
理装置を不要とする排ガス処理方法に関するものであ
る。
DETAILED DESCRIPTION OF THE INVENTION [Industrial field of application] The present invention cleans and removes reducing substances such as phenol and formaldehyde in exhaust gas with an absorbent containing hydrogen peroxide and ferrous ions, The present invention relates to an exhaust gas treatment method that eliminates the need for the iron sludge treatment device.

[従来の技術] 一般に、鋳造工程等から排出される排ガス中には還元
性物質であるフェノールやホルムアルデヒド等の悪臭成
分が含まれている。そこで、この排ガスを大気中に放出
する前に、そのような悪臭成分を排ガス中から除去する
ことが必要となる。
[Prior Art] Generally, an exhaust gas discharged from a casting process or the like contains a malodorous component such as a reducing substance such as phenol or formaldehyde. Therefore, it is necessary to remove such malodorous components from the exhaust gas before releasing the exhaust gas into the atmosphere.

上記フェノールやホルムアルデヒド等の還元性物質は
水溶性であり、しかも水溶液上の平衡分圧が低い。従っ
て、これらの物質を洗浄除去する場合、吸収液中のこれ
らの物質の濃度が高くならないように、当該物質を適宜
酸化分解すればよい。
The reducing substances such as phenol and formaldehyde are water-soluble and have a low equilibrium partial pressure in an aqueous solution. Therefore, when these substances are washed and removed, the substances may be appropriately oxidatively decomposed so that the concentration of these substances in the absorption liquid does not become high.

吸収液中の当該物質を酸化分解するには、過酸化水素
と第1鉄イオン(通常、硫酸第1鉄を使用)の添加が効
果的であることが知られている。
It is known that the addition of hydrogen peroxide and ferrous ions (usually ferrous sulfate is used) is effective for oxidatively decomposing the substance in the absorbing solution.

この種の排ガス処理方法として、特公昭51−44898号
公報に開示されているように、吸収液を pH≦5 Fe2+/H2O2≧1/7 酸化還元電位≧(540−60×pH値)mV として使用する方法があった。
As an exhaust gas treatment method of this kind, as disclosed in Japanese Patent Publication No. 51-44898, the absorption liquid is treated with pH ≦ 5 Fe 2+ / H 2 O 2 ≧ 1/7 redox potential ≧ (540-60 × pH value) mV was used.

この排ガス処理においても、第1鉄イオンが必要であ
り、事実、硫酸第1鉄を添加している。
Also in this exhaust gas treatment, ferrous iron is necessary, and in fact ferrous sulfate is added.

しかるに、フェノール等の酸化分解の過程および気液
接触の過程で、上記第1鉄イオンは第2鉄イオンとな
る。
However, the ferrous ions become ferric ions in the process of oxidative decomposition of phenol or the like and the process of gas-liquid contact.

従って、第1鉄イオンを所定の濃度に保つために、硫
酸第1鉄を常時多量に添加し続けねばならず、また、そ
の結果、不要となった鉄分を系から適宜取り除いて二次
処理しなければならない。
Therefore, in order to keep the concentration of ferrous iron at a predetermined level, it is necessary to constantly add a large amount of ferrous sulfate, and as a result, unnecessary iron is appropriately removed from the system for secondary treatment. There must be.

さらに、上記在来技術を適用した実用装置の運転結果
を見ると、不要な鉄分がスラッジとなり、系内に堆積し
ている。
Furthermore, looking at the operation results of the practical device to which the above-mentioned conventional technique is applied, unnecessary iron components become sludge and are accumulated in the system.

結局、これまでの技術においては、“硫酸第1鉄の常
時多量供給”、“不要鉄分の廃棄ならびに二次処理”お
よび“系内に堆積した鉄スラッジの除去”が維持管理お
よび経済性の点で問題となっていた。
After all, in the conventional technology, "continuously supplying a large amount of ferrous sulfate", "disposal and secondary treatment of unnecessary iron content" and "removal of iron sludge accumulated in the system" are points of maintenance and economical efficiency. Was a problem.

これを解決するため、本発明者は特開昭62−237926号
公報に開示されているように、吸収液のpH、過酸化水素
濃度および第2鉄濃度を、それぞれ2〜4、0.8mg−mol
/以上および1mg−mol/以上の範囲に循環槽内で2分
間以上維持することにより、第1鉄イオンの再生を促進
して、第1鉄イオンの供給量を吸収液循環流量1m3/hr当
り30mg−mol/hr以下にすることにより、第1鉄イオンの
供給量を削減し、その結果、鉄スラッジ量を低減せし
め、系内で鉄スラッジの堆積を防ぐ技術を開発した。
In order to solve this, the present inventor, as disclosed in JP-A-62-237926, sets the pH, hydrogen peroxide concentration and ferric iron concentration of the absorbing solution to 2 to 4 mg and 0.8 mg to respectively. mol
By maintaining the above / above and above 1 mg-mol / above in the circulation tank for 2 minutes or more, the regeneration of ferrous iron is promoted and the supply amount of ferrous ion is adjusted to the absorption liquid circulation flow rate of 1 m 3 / hr. By reducing the amount of ferrous ions to 30 mg-mol / hr or less per unit time, we have developed a technique to reduce the amount of ferrous ions and consequently reduce the amount of iron sludge and prevent the accumulation of iron sludge in the system.

[発明が解決しようとする課題] しかしながら、上記従来方法では、鉄スラッジ量の低
減が不十分であるため、不要となった鉄分を系から適宜
取り除き廃棄するために、中和処理後、二次処理とし
て、生成した鉄スラッジ(水酸化第2鉄)を第2図に示
すように濃縮槽(シックナー)4に導き、上澄液18を終
末処理場へ放流すると共に、濃縮液19を固液分離装置
(フィルタープレス)5等で処理しなければならないと
いう問題点があった。
[Problems to be Solved by the Invention] However, in the above-mentioned conventional method, since reduction of the amount of iron sludge is insufficient, in order to appropriately remove unnecessary iron from the system and to discard it, after the neutralization treatment, the secondary As a treatment, the produced iron sludge (ferric hydroxide) was introduced into a concentrating tank (thickener) 4 as shown in FIG. 2, and the supernatant liquid 18 was discharged to the final treatment plant and the concentrated liquid 19 was solid-liquid. There is a problem that it must be processed by a separating device (filter press) 5 or the like.

本発明は、上記従来の問題点を解決するためになされ
たもので、その目的とするところは、第1鉄イオンの供
給量を更に大巾に削減し、その結果、鉄スラッジ量を大
巾に低減せしめ、二次処理装置(固液分離装置等)を不
要にすると共に、系内での鉄スラッジの堆積を防止し、
排ガス処理システムの維持管理をより容易とし、かつ経
済性をより高めることができる排ガス処理方法を提供す
ることにある。
The present invention has been made to solve the above-mentioned conventional problems, and an object thereof is to further drastically reduce the supply amount of ferrous iron ions, resulting in a large iron sludge amount. To eliminate the need for secondary treatment equipment (solid-liquid separation equipment, etc.) and prevent the accumulation of iron sludge in the system.
An object of the present invention is to provide an exhaust gas treatment method capable of facilitating maintenance and management of the exhaust gas treatment system and further improving economic efficiency.

[課題を解決するための手段・作用] ところで、フェノール等を吸収除去する場合、第1鉄
イオンの消費と再生については、次のように考えられ
る。
[Means and Actions for Solving the Problems] By the way, when phenol and the like are absorbed and removed, the consumption and regeneration of ferrous ions are considered as follows.

即ち、第1鉄イオンはフェノール等の酸化分解の過程
および気液接触の過程で第2鉄イオンになる。
That is, ferrous ions become ferric ions in the process of oxidative decomposition of phenol or the like and the process of gas-liquid contact.

一方、第2鉄イオンは、下記反応により、第1鉄イオ
ンに戻る。
On the other hand, ferric ions return to ferrous ions by the following reaction.

C6H4(OH)+2Fe3+→C6H4O2+2Fe2++2H+ ……(1) Fe3++H2O2→Fe2++HO2+H+ ……(2) ただし、C6H4(OH)はハイドロキノン或いはカテコ
ールを示し、いずれもフェノールの分解生成物である。
C 6 H 4 (OH) 2 + 2Fe 3+ → C 6 H 4 O 2 + 2Fe 2+ + 2H + …… (1) Fe 3+ + H 2 O 2 → Fe 2+ + HO 2 + H + …… (2) However, C 6 H 4 (OH) 2 represents hydroquinone or catechol, both of which are decomposition products of phenol.

以上の反応の内、(2)の反応は遅いので、(1)の
反応のみが第1鉄イオンの再生に寄与すると考えられ
る。
Among the above reactions, the reaction (2) is slow, so it is considered that only the reaction (1) contributes to the regeneration of ferrous ions.

本発明者は、鋭意研究の結果、吸収液の状態を下記の
ように設定することにより、上記(1)の反応を促進せ
しめ得ることを発見した。
As a result of earnest research, the present inventor has discovered that the reaction of the above (1) can be promoted by setting the state of the absorbing solution as follows.

更に、第1鉄イオンの濃度は下記吸収液条件のもとで
0.02mg−mol/以上であればフェノール等の酸化分解に
は十分であることを見出し、第1鉄イオンの供給量を従
来よりも大巾に少なくすることを可能ならしめた。
Furthermore, the concentration of ferrous ion is
It has been found that 0.02 mg-mol / or more is sufficient for oxidative decomposition of phenol and the like, and it has been possible to make the supply amount of ferrous ions much smaller than before.

その結果、廃液の二次処理装置が不要となった。 As a result, the waste liquid secondary treatment device is no longer required.

即ち、本発明は、吸収液のpH、過酸化水素濃度および
第2鉄濃度を、それぞれ2〜4、0.5mg−mol/以上お
よび0.5〜0.9mg−mol/の範囲に循環槽内で2分間以上
維持することにより、第1鉄イオンの再生を促進して、
第1鉄イオンの供給量を吸収液循環流量1m3/hr当り0.9
〜3.0mg−mol/hrの範囲にする。その結果、廃液中の鉄
スラッジ量を大巾に低減せしめ、固液分離装置等の二次
処理装置を不要とすることを特徴とするものである。
That is, in the present invention, the pH of the absorbing solution, the hydrogen peroxide concentration and the ferric iron concentration are respectively set to 2 to 4, 0.5 mg-mol / or more and 0.5 to 0.9 mg-mol / for 2 minutes in the circulation tank. By maintaining the above, it promotes the regeneration of ferrous ions,
The supply amount of ferrous ion is 0.9 per 1 m 3 / hr of absorption liquid circulation flow rate.
The range is to 3.0 mg-mol / hr. As a result, the amount of iron sludge in the waste liquid is greatly reduced, and a secondary treatment device such as a solid-liquid separation device is unnecessary.

[実施例] 以下、本発明方法を実施する排ガス処理システムにつ
いて図面を参照しながら詳述する。
[Examples] Hereinafter, an exhaust gas treatment system for carrying out the method of the present invention will be described in detail with reference to the drawings.

第1図は第1鉄イオンの供給量を吸収液循環流量1m3/
hr当り0.9〜3.0mg−mol/hrの範囲にする場合の排ガス処
理システムを示すものであって、1は吸収塔であり、例
えば鋳造工程から排出される未処理の排ガス7に吸収液
8を接触せしめて、該排ガス中のフェノール及びホルム
アルデヒド等の還元性物質を吸収液8に吸収せしめる。
Fig. 1 shows the amount of ferrous iron supplied as the absorption liquid circulation flow rate of 1 m 3 /
1 shows an exhaust gas treatment system in the case of setting it in a range of 0.9 to 3.0 mg-mol / hr per hr, 1 is an absorption tower, for example, an untreated exhaust gas 7 discharged from a casting process is treated with an absorption liquid 8 By bringing them into contact with each other, reducing substances such as phenol and formaldehyde in the exhaust gas are absorbed in the absorbing liquid 8.

2は循環槽であって、水9、苛性ソーダ10および硫酸
11が調節されながら供給され、吸収液の液量およびpH値
が所定値に維持される。
2 is a circulation tank, water 9, caustic soda 10 and sulfuric acid
11 is supplied while being adjusted, and the amount of absorption liquid and the pH value are maintained at predetermined values.

また、該循環槽2には、過酸化水素12および硫酸第1
鉄13も供給される。
Further, in the circulation tank 2, hydrogen peroxide 12 and sulfuric acid first
Iron 13 is also supplied.

本実施例の処理システムは、以上のように構成されて
いるので、まず、未処理排ガス7は吸収塔1内で吸収液
8により洗浄され、その中のフェノール及びホルムアル
デヒド等の還元性物質が該吸収液8に吸収・分解され
て、処理済み排ガス14として排出される。
Since the treatment system of the present embodiment is configured as described above, first, the untreated exhaust gas 7 is washed with the absorption liquid 8 in the absorption tower 1, and the reducing substances such as phenol and formaldehyde therein are removed. It is absorbed and decomposed by the absorbing liquid 8 and discharged as the treated exhaust gas 14.

排ガス洗浄前の吸収液8は、ポンプ(図示せず)によ
り上記循環槽2から吸収塔1に送られ、上述のようにフ
ェノール及びホルムアルデヒド等の還元性物質を吸収処
理した後、吸収液15として循環槽2に戻される。
The absorption liquid 8 before cleaning the exhaust gas is sent from the circulation tank 2 to the absorption tower 1 by a pump (not shown), and after absorbing the reducing substances such as phenol and formaldehyde as described above, the absorption liquid 15 is obtained. It is returned to the circulation tank 2.

また、吸収液8の一部は引抜き液16として吸収系から
分離され、中和槽3に入り、苛性ソーダ10もしくは硫酸
11で中和処理される。
Further, a part of the absorption liquid 8 is separated from the absorption system as the extraction liquid 16 and enters the neutralization tank 3, where caustic soda 10 or sulfuric acid is added.
It is neutralized at 11.

中和後の吸収液17は直接、終末処理場に送られ、他の
排水とともに処理される。
The neutralized absorption liquid 17 is directly sent to the terminal treatment plant and treated together with other wastewater.

尚、上記システムの運転条件および性能の実施例は下
記のごとくである。
Examples of operating conditions and performance of the above system are as follows.

実施例1 (i) 排ガス 処理前 処理後 流 量 m3/hr 90,000 温 度 ℃ 30 フェノール濃度 ppm 0.2 0.1未満 ホルムアルデヒド濃度ppm 0.21 〃 アンモニア濃度 ppm 5 〃 ダスト濃度 mg/m3N 1 − (ii) 吸収塔 形 式 :充填塔 充填物 :花型充填物(商品名:テラレット) 充填高さ m :2.0 ガス流速 m/sec :2.5 液ガス比 /m3 :2 (iii) 吸収液(循環槽) pH :3 過酸化水素濃度 mg−mol/ :1 第1鉄イオン濃度 〃 :0.02 第2鉄濃度 〃 :0.5 循環槽滞留時間 min :3 (iv) 硫酸第1鉄 吸収液循環量 1m3/hr当りmg−mol/hr :1.4 全供給量 g−mol/hr :0.25 (v) 排出液 排出液流量 m3/hr:0.5 (vi) 中和後の排出液 SS濃度 mg/:82 実施例2 (i) 排ガス 処理前 処理後 流 量 m3/hr 90,000 温 度 ℃ 30 フェノール濃度 ppm 0.11 0.1未満 ホルムアルデヒド濃度ppm 0.15 〃 アンモニア濃度 ppm 5 〃 ダスト濃度 mg/m3N 1 − (ii) 吸収塔 形 式 :充填塔 充填物 :花型充填物(商品名:テラレット) 充填高さ m :2.0 ガス流速 m/sec :2.5 液ガス比 /m3 :2 (iii) 吸収液(循環槽) pH :3 過酸化水素濃度 mg−mol/ :1.8 第1鉄イオン濃度 〃 :0.04 第2鉄濃度 〃 :0.7 循環槽滞留時間 min :3 (iv) 硫酸第1鉄 吸収液循環量 1m3/hr当りmg−mol/hr :2.0 全供給量 g−mol/hr :0.36 (v) 排出液 排出液流量 m3/hr:0.5 (vi) 中和後の排出液 SS濃度 mg/:104 [発明の効果] 吸収液中のpH、過酸化水素濃度および第2鉄濃度を、
それぞれ2〜4、0.5mg−mol/以上および0.5〜0.9mg
−mol/の範囲に循環槽内で2分間以上維持した後、該
吸収液を排ガスの洗浄に用いるので、その結果、硫酸第
1鉄の供給量を極めて少なくすることができ、廃液中の
鉄スラッジ量を大巾に低減し、固液分離装置等の二次処
理装置を不要とすることができる。
Example 1 (i) Exhaust gas pre-treatment and post-treatment flow rate m 3 / hr 90,000 Temperature ℃ 30 Phenol concentration ppm 0.2 0.1 Formaldehyde concentration ppm 0.21〃 Ammonia concentration ppm 5〃 Dust concentration mg / m 3 N 1- (ii) Absorption tower Type: Packing tower Packing: Flower packing (trade name: Terralet) Packing height m: 2.0 Gas flow rate m / sec: 2.5 Liquid gas ratio / m 3 : 2 (iii) Absorbing liquid (circulating tank) pH: 3 Hydrogen peroxide concentration mg-mol /: 1 Ferrous iron ion concentration 〃: 0.02 Ferric iron concentration 〃: 0.5 Circulation tank residence time min: 3 (iv) Ferrous sulfate absorption liquid circulation rate 1m 3 / hr Per mg-mol / hr: 1.4 Total supply amount g-mol / hr: 0.25 (v) Effluent Effluent flow rate m 3 / hr: 0.5 (vi) Effluent SS concentration after neutralization mg /: 82 Example 2 (i) flow amount after the exhaust gas treatment pretreatment m 3 / hr 90,000 temperature ° C. 30 phenol concentration ppm 0.11 0.1 less than the formaldehyde concentration ppm 0.15 〃 ammonia concentration ppm 5 〃 dust concentrated mg / m 3 N 1 - ( ii) the absorption column format: packed column packing: Flower-shaped packing (trade name: Tellerette) fill height m: 2.0 Gas flow rate m / sec: 2.5 solution gas ratio / m 3: 2 (iii) Absorption liquid (circulation tank) pH: 3 Hydrogen peroxide concentration mg-mol /: 1.8 Ferrous iron ion concentration 〃: 0.04 Ferric iron concentration 〃: 0.7 Circulation tank residence time min: 3 (iv) Sulfuric acid No. 1 Iron absorption liquid circulation rate 1 m 3 / hr mg-mol / hr: 2.0 Total supply amount g-mol / hr: 0.36 (v) Effluent flow rate m 3 / hr: 0.5 (vi) Emission after neutralization Liquid SS concentration mg /: 104 [Effect of the invention] pH, hydrogen peroxide concentration and ferric iron concentration in the absorption liquid
2 to 4, 0.5 mg-mol / min and 0.5 to 0.9 mg, respectively
Since the absorption liquid is used for cleaning the exhaust gas after being kept in the circulation tank in the range of −mol / for 2 minutes or more, as a result, the supply amount of ferrous sulfate can be extremely reduced, and the iron in the waste liquid can be reduced. The amount of sludge can be greatly reduced, and a secondary treatment device such as a solid-liquid separation device can be eliminated.

また、鉄分がスラッジとして系内に堆積する恐れもな
く、維持管理が容易で経済的である。
Further, there is no fear that iron content will be accumulated in the system as sludge, and maintenance is easy and economical.

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

第1図は本発明方法を実施する排ガス処理システムのブ
ロック図、第2図は従来の排ガス処理システムのブロッ
ク図である。 1……吸収塔、2……循環槽、3……中和槽、4……濃
縮槽、5……固液分離装置(フィルタープレス)、6…
…ホッパー、7……未処理排ガス、8……吸収液、9…
…水、10……苛性ソーダ、11……硫酸、12……過酸化水
素、13……硫酸第1鉄、14……処理済み排ガス、15……
吸収処理後の吸収液、16……引抜き液、17……中和後の
吸収液、18……上澄液、19……濃縮液、20……残渣、21
……ろ液。 なお、4,5,6は二次処理装置を示す。
FIG. 1 is a block diagram of an exhaust gas treatment system for carrying out the method of the present invention, and FIG. 2 is a block diagram of a conventional exhaust gas treatment system. 1 ... Absorption tower, 2 ... Circulation tank, 3 ... Neutralization tank, 4 ... Concentration tank, 5 ... Solid-liquid separation device (filter press), 6 ...
… Hopper, 7… Untreated exhaust gas, 8… Absorption liquid, 9…
… Water, 10 …… Caustic soda, 11 …… Sulfuric acid, 12 …… Hydrogen peroxide, 13 …… Ferrous sulfate, 14 …… Treated exhaust gas, 15 ……
Absorption liquid after absorption treatment, 16 ... Extraction liquid, 17 ... Absorption liquid after neutralization, 18 ... Supernatant liquid, 19 ... Concentrated liquid, 20 ... Residue, 21
... filtrate. Reference numerals 4, 5 and 6 denote secondary processing devices.

───────────────────────────────────────────────────── フロントページの続き (72)発明者 浜井 満彦 愛知県豊田市トヨタ町1番地 トヨタ自 動車株式会社内 (56)参考文献 特開 昭62−237926(JP,A) ─────────────────────────────────────────────────── ─── Continuation of front page (72) Inventor Mitsuhiko Hamai 1 Toyota-cho, Toyota-shi, Aichi Toyota Motor Co., Ltd. (56) Reference JP-A-62-237926 (JP, A)

Claims (1)

(57)【特許請求の範囲】(57) [Claims] 【請求項1】排ガス中のフェノールを含む還元性物質を
過酸化水素と第1鉄イオンを含む吸収液により洗浄除去
する方法において、該吸収液のpH、過酸化水素濃度およ
び第2鉄濃度を、それぞれ2〜4、0.5mg−mol/l以上お
よび0.5〜0.9mg−mol/lの範囲に循環槽内で2分間以上
に維持した後、該吸収液を排ガスの洗浄に用いることを
特徴とする排ガス処理方法。
1. A method of washing and removing a reducing substance containing phenol in exhaust gas with an absorption liquid containing hydrogen peroxide and ferrous ions, the pH, hydrogen peroxide concentration and ferric iron concentration of the absorption liquid being measured. , 2 to 4, 0.5 mg-mol / l or more and 0.5 to 0.9 mg-mol / l in the circulation tank for 2 minutes or more, respectively, and then the absorbent is used for cleaning exhaust gas. Exhaust gas treatment method.
JP63147956A 1988-06-17 1988-06-17 Exhaust gas treatment method Expired - Lifetime JP2687222B2 (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP63147956A JP2687222B2 (en) 1988-06-17 1988-06-17 Exhaust gas treatment method
KR1019890000763A KR910010242B1 (en) 1988-06-17 1989-01-25 Exhaust gas treatment method

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP63147956A JP2687222B2 (en) 1988-06-17 1988-06-17 Exhaust gas treatment method

Publications (2)

Publication Number Publication Date
JPH01317528A JPH01317528A (en) 1989-12-22
JP2687222B2 true JP2687222B2 (en) 1997-12-08

Family

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JP (1) JP2687222B2 (en)
KR (1) KR910010242B1 (en)

Cited By (1)

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CN108031268A (en) * 2017-12-22 2018-05-15 陈明秦 A kind of formaldehyde remover and preparation method thereof

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
AU2001245416A1 (en) * 2000-03-03 2001-09-17 Steen Research, Llc Method and apparatus for use of reacted hydrogen peroxide compounds in industrial process waters
CN100400108C (en) * 2006-08-11 2008-07-09 中北大学 Indoor air wet oxidation purification method
US10881756B2 (en) 2012-06-28 2021-01-05 Stephen R. Temple Methods and equipment for treatment of odorous gas streams from industrial plants
WO2018035165A1 (en) 2016-08-15 2018-02-22 Steen Research, Llc Processes for removing a nitrogen-based compound from a gas or liquid stream to produce a nitrogen-based product

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS62237926A (en) * 1986-04-10 1987-10-17 Gadelius Kk Exhaust gas treatment

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN108031268A (en) * 2017-12-22 2018-05-15 陈明秦 A kind of formaldehyde remover and preparation method thereof

Also Published As

Publication number Publication date
JPH01317528A (en) 1989-12-22
KR900000141A (en) 1990-01-30
KR910010242B1 (en) 1991-12-24

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