JPS632149Y2 - - Google Patents

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Publication number
JPS632149Y2
JPS632149Y2 JP1983196908U JP19690883U JPS632149Y2 JP S632149 Y2 JPS632149 Y2 JP S632149Y2 JP 1983196908 U JP1983196908 U JP 1983196908U JP 19690883 U JP19690883 U JP 19690883U JP S632149 Y2 JPS632149 Y2 JP S632149Y2
Authority
JP
Japan
Prior art keywords
tank
wastewater
thermal decomposition
sulfuric acid
acid
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
JP1983196908U
Other languages
Japanese (ja)
Other versions
JPS60104291U (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 JP19690883U priority Critical patent/JPS60104291U/en
Publication of JPS60104291U publication Critical patent/JPS60104291U/en
Application granted granted Critical
Publication of JPS632149Y2 publication Critical patent/JPS632149Y2/ja
Granted legal-status Critical Current

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  • Treating Waste Gases (AREA)
  • Removal Of Specific Substances (AREA)
  • Treatment Of Water By Oxidation Or Reduction (AREA)

Description

【考案の詳細な説明】 〔考案の属する分野〕 この考案は、湿式排ガス脱硫装置のブローダウ
ン水およびそのイオン交換処理の際に発生する再
生濃厚廃水などジチオン酸含有廃水の処理装置に
係り、特にジチオン酸を主成分とするCOD成分
を含む廃水に硫酸を加えて加熱分解する処理装置
に関する。
[Detailed description of the invention] [Field to which the invention pertains] This invention relates to a treatment device for dithionic acid-containing wastewater such as blowdown water of a wet exhaust gas desulfurization equipment and regenerated concentrated wastewater generated during its ion exchange treatment. This invention relates to a treatment device that adds sulfuric acid to wastewater containing COD components mainly composed of dithionic acid and decomposes it by heating.

〔従来技術〕[Prior art]

従来特開昭52−146962,特公昭56−50637など
湿式排ガス脱硫装置から排出されるブローダウン
水およびそのイオン交換処理の際に発生するイオ
ン交換樹脂の再生濃厚廃水などのジチオン酸を主
成分とするCOD成分を含む廃水に硫酸を加えPH
を1.5以下とし、かつ60〜100℃の温度で加熱して
COD成分を分解し、生成した亜硫酸ガスをアル
カリ剤によつて吸収除去する処理方法が開示され
ている。
Conventional JP-A-52-146962, JP-A-56-50637, etc., which mainly contain dithionic acid from blowdown water discharged from wet exhaust gas desulfurization equipment and recycled concentrated wastewater of ion exchange resin generated during ion exchange treatment. Add sulfuric acid to wastewater containing COD components to
1.5 or less, and heated at a temperature of 60 to 100℃.
A treatment method is disclosed in which COD components are decomposed and the generated sulfur dioxide gas is absorbed and removed using an alkaline agent.

従来の加熱分解槽は温度100℃以下で加熱分解
するために大気開放形槽としているので分解率が
約65〜90%程度であり、分解反応時に発生する亜
硫酸ガスSO2を主成分とする排ガスを処理する必
要があつた。
Conventional thermal decomposition tanks are open to the atmosphere in order to perform thermal decomposition at temperatures below 100°C, so the decomposition rate is approximately 65-90%, and the exhaust gas mainly composed of sulfur dioxide gas SO 2 generated during the decomposition reaction. It was necessary to process.

排ガスの処理方法としては、排ガスを送風機に
よつて湿式排ガス脱硫装置へ返送して再処理する
方法があるが、耐蝕性の長距離ダクトを必要と
し、また湿式排ガス脱硫装置の運転時間に制約さ
れる欠点があつた。
One method for treating exhaust gas is to send it back to the wet flue gas desulfurization equipment using a blower for reprocessing, but this method requires a long, corrosion-resistant duct and is limited by the operating time of the wet flue gas desulfurization equipment. There were some shortcomings.

〔考案の目的〕[Purpose of invention]

この考案の目的は、前記従来技術の欠点を解消
し、ジチオン酸イオンの分解率を向上させ、且排
ガスの処理を不要とするジチオン酸含有廃水の処
理装置を提供するにある。
The purpose of this invention is to provide a treatment device for dithionate-containing wastewater that eliminates the drawbacks of the prior art, improves the decomposition rate of dithionate ions, and eliminates the need for exhaust gas treatment.

〔考案の要点〕[Key points of the idea]

この考案は、ジチオン酸イオンを含有する廃水
に硫酸を添加して100℃以上の温度でかつ1.15〜
1.20Kg/cm2の圧力で加熱分解する密閉形加熱分解
槽と、生成した亜硫酸ガスSO2をアルカリ剤によ
つて吸収する中和吸収槽と、生成した亜硫酸イオ
ンSO3 2-を酸化剤によつて酸化して安定した硫酸
イオンSO4 2-にする酸化槽とにより構成したもの
である。
This idea was developed by adding sulfuric acid to wastewater containing dithionate ions at a temperature of 100℃ or higher and at a temperature of 1.15 to 1.15℃.
A closed thermal decomposition tank that thermally decomposes at a pressure of 1.20Kg/cm 2 , a neutralization absorption tank that absorbs the generated sulfite gas SO 2 with an alkaline agent, and an oxidizing agent that uses the generated sulfite ion SO 3 2- . The sulfuric acid ion is thus oxidized into a stable sulfate ion SO 4 2- , and an oxidation tank.

〔考案の実施例〕[Example of idea]

第1図は、この考案に係るジチオン酸含有廃水
の処理装置の1実施例の断面図を示す。
FIG. 1 shows a sectional view of one embodiment of the dithionic acid-containing wastewater treatment apparatus according to this invention.

密閉形加熱分解槽1の下部に廃水供給管2を接
続し、廃水供給管2には、加熱用のスチーム供給
管3及び硫酸供給管4を接続する。加熱分解槽1
の内部にはじやま板5を数枚設ける。加熱分解槽
1の上部には、処理水排出管6を接続し、途中に
圧力調整弁7を付設して中和吸収槽8に接続す
る。中和吸収槽8にはアルカリ剤供給管9、PH制
御器10、アルカリ剤の供給ポンプ11、アルカ
リ剤槽12から構成されるアルカリ剤の供給設備
を設ける。中和吸収槽8と酸化槽14は吸収処理
水管14を介して連結され、酸化槽14には空気
供給管15が接続している。
A wastewater supply pipe 2 is connected to the lower part of the closed type thermal decomposition tank 1, and a steam supply pipe 3 and a sulfuric acid supply pipe 4 for heating are connected to the wastewater supply pipe 2. Thermal decomposition tank 1
Several cutting boards 5 are provided inside. A treated water discharge pipe 6 is connected to the upper part of the thermal decomposition tank 1, and a pressure regulating valve 7 is provided in the middle to connect it to a neutralization absorption tank 8. The neutralization absorption tank 8 is provided with an alkali agent supply facility consisting of an alkali agent supply pipe 9, a PH controller 10, an alkali agent supply pump 11, and an alkali agent tank 12. The neutralization absorption tank 8 and the oxidation tank 14 are connected via an absorption treatment water pipe 14, and the oxidation tank 14 is connected to an air supply pipe 15.

次にこの作用を説明する。 Next, this effect will be explained.

ジチオン酸(S2O6 2-)を含む廃水は、廃水供
給管2より加熱分解槽1の下部に導入されるが、
導入経路においてスチーム供給管3及び硫酸供給
管4より、スチーム及び硫酸が添加される。廃水
は点線で示す流れで、加熱分解槽1内を上昇す
る。この際、廃水の流れはマクロ的には上向流で
流れ、この流れはスチームにより加熱されている
ので比重の違いから自然に上昇する。加熱分解槽
1内のジチオン酸(S2O6 2-)の分解反応は S2O6 2-→SO4 2-+SO2↑ −(1) で示され、この反応は、硫酸添加量,温度,圧力
が大きいほど速やかに進行する。本実施例では硫
酸添加量3.5v/v%、温度105℃、圧力1.15〜1.20
Kg/cm2とした。
Wastewater containing dithionic acid (S 2 O 6 2- ) is introduced into the lower part of the thermal decomposition tank 1 from the wastewater supply pipe 2.
Steam and sulfuric acid are added through the steam supply pipe 3 and the sulfuric acid supply pipe 4 in the introduction path. The wastewater rises in the thermal decomposition tank 1 in a flow indicated by a dotted line. At this time, the flow of wastewater flows upward from a macroscopic perspective, and since this flow is heated by steam, it naturally rises due to the difference in specific gravity. The decomposition reaction of dithionic acid (S 2 O 6 2- ) in the thermal decomposition tank 1 is shown as S 2 O 6 2- →SO 4 2- +SO 2 ↑ −(1), and this reaction depends on the amount of sulfuric acid added, The higher the temperature and pressure, the faster the process progresses. In this example, the amount of sulfuric acid added was 3.5v/v%, the temperature was 105°C, and the pressure was 1.15 to 1.20.
Kg/ cm2 .

ジチオン酸が分解され、硫酸イオンSO4 2-及び
亜硫酸ガスSO2を含んだ廃水は、加熱分解槽1の
上部から処理水排出管6より排出され、圧力調整
弁7により減圧され、大気圧となり中和吸収槽8
に供給される。中和吸収槽8は、PH制御器10に
より槽内のPHを検出しPHが7〜10に保持されるよ
うに、供給ポンプ11を作動させ、アルカリ剤槽
12から、アルカリ液をアルカリ供給管9を通し
て、中和吸収槽8に供給する。中和吸収槽8にお
いて亜硫酸ガスSO2を含んだ廃水はアルカリ剤と
の反応によつて、次式の示す通り SO2+2OH-→SO3 2-+H2O −(2) となり、亜硫酸ガスSO2は亜硫酸イオンSO3 2-
なり液中に固定される。
The dithionic acid is decomposed, and the wastewater containing sulfuric acid ions SO 4 2- and sulfur dioxide gas SO 2 is discharged from the upper part of the thermal decomposition tank 1 through the treated water discharge pipe 6, and the pressure is reduced by the pressure regulating valve 7 to atmospheric pressure. Neutralization absorption tank 8
supplied to In the neutralization absorption tank 8, the PH in the tank is detected by the PH controller 10, and the supply pump 11 is operated so that the PH is maintained at 7 to 10. 9 and is supplied to the neutralization absorption tank 8. In the neutralization absorption tank 8, the wastewater containing sulfur dioxide gas SO 2 reacts with an alkaline agent to become SO 2 +2OH - →SO 3 2- +H 2 O -(2) as shown in the following equation, and sulfur dioxide gas SO 2 becomes sulfite ion SO 3 2- and is fixed in the liquid.

亜硫酸イオンSO3 2-を含んだ処理水は、吸収処
理水管13を経て酸化槽14に導入される。酸化
剤として、本実施では空気を用いたので、その供
給方法は、空気供給管15より散気ノズルを経て
気泡を液中に分散させた。亜硫酸イオンSO3 2-
空気との反応は、 SO3 2-+1/2O2→SO4 2- −(3) となり、亜硫酸イオンSO3 2-は酸化を受けない安
定した硫酸イオンSO4 2-に変化する。
The treated water containing sulfite ions SO 3 2- is introduced into the oxidation tank 14 through the absorption treatment water pipe 13 . Since air was used as the oxidizing agent in this embodiment, air bubbles were dispersed in the liquid through an air supply pipe 15 and an aeration nozzle. The reaction between sulfite ion SO 3 2- and air is SO 3 2- + 1/2O 2 →SO 4 2- −(3), and sulfite ion SO 3 2- becomes a stable sulfate ion SO 4 2 that does not undergo oxidation. -Changes to .

本実施例において、ジチオン酸S2O6濃度30000
mg/の廃水を最終的には、処理水のCODMn50
mg/以下として、分解率99.8%を得て安定に処
理することができた。
In this example, dithionic acid S 2 O 6 concentration 30000
CODMn50 of the treated water
mg/ or less, the decomposition rate was 99.8% and stable processing was possible.

〔考案の変形例,応用例〕[Variations and application examples of the idea]

本実施例では、廃水の加熱源としてスチームを
用い、廃水供給管2に直接供給したが、加熱分解
槽1の下部に供給してもよい。又、加熱源として
スチーム以外の方法として例えばヒータを加熱分
解槽1の外周に巻いても良く、加熱方法は限定さ
れない。さらに酸化槽14で用いる酸化剤は、空
気に限定されず、過酸化水素,オゾンなどを用い
ることもできる。
In this embodiment, steam was used as a heating source for wastewater and was supplied directly to the wastewater supply pipe 2, but it may also be supplied to the lower part of the thermal decomposition tank 1. Further, as a heating source other than steam, for example, a heater may be wound around the outer periphery of the thermal decomposition tank 1, and the heating method is not limited. Further, the oxidizing agent used in the oxidizing tank 14 is not limited to air, and hydrogen peroxide, ozone, etc. can also be used.

〔考案の効果〕[Effect of idea]

この考案に係るジチオン酸含有廃水の処理装置
は、加熱分解槽を密閉形としたので、加熱温度を
100℃以上として分解率を向上させ、反応時間を
短縮して加熱分解槽の容量を小さくし、硫酸消費
量を少くし、且亜硫酸ガスを放散せず排ガス処理
装置を不要とすることができる。
The dithionic acid-containing wastewater treatment device according to this invention has a closed thermal decomposition tank, so the heating temperature can be controlled.
At 100°C or higher, the decomposition rate can be improved, the reaction time can be shortened, the capacity of the thermal decomposition tank can be reduced, the amount of sulfuric acid consumed can be reduced, and sulfur dioxide gas is not released, making it possible to eliminate the need for an exhaust gas treatment device.

また中和吸収槽と酸化槽とを設置しているので
安定した硫酸イオンとすることができる。
Furthermore, since a neutralization absorption tank and an oxidation tank are installed, stable sulfate ions can be produced.

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

第1図はこの考案に係るジチオン酸含有廃水の
1実施例の断面図を示す。 1……加熱分解槽、2……廃水供給管、3……
スチーム供給管、4……硫酸供給管、5……じや
ま板、6……処理水排出管、7……圧力調整弁、
8……中和吸収槽、9……アルカリ剤供給管、1
0……PH制御器、11……供給ポンプ、12……
アルカリ剤槽、13……吸収処理水管、14……
酸化槽、15……空気供給管。
FIG. 1 shows a cross-sectional view of one embodiment of the dithionic acid-containing wastewater according to this invention. 1... Thermal decomposition tank, 2... Waste water supply pipe, 3...
Steam supply pipe, 4... Sulfuric acid supply pipe, 5... Stainless steel board, 6... Treated water discharge pipe, 7... Pressure adjustment valve,
8... Neutralization absorption tank, 9... Alkali agent supply pipe, 1
0...PH controller, 11...Supply pump, 12...
Alkaline agent tank, 13... Absorption treatment water pipe, 14...
Oxidation tank, 15...Air supply pipe.

Claims (1)

【実用新案登録請求の範囲】[Scope of utility model registration request] ジチオン酸含有廃水に硫酸を添加して加熱分解
するジチオン酸含有廃水の処理装置において、廃
水に硫酸を添加して温度100℃以上でかつ圧力
1.15〜1.20Kg/cm2を保持する密閉形加熱分解槽
と、この密閉形加熱分解槽の出口に付設した圧力
調整弁と、前記密閉形加熱分解槽に接続してアル
カリ剤供給装置を付設した中和吸収槽と、この中
和吸収槽に接続して酸化剤注入装置を付設した酸
化槽とを備えたことを特徴とするジチオン酸含有
廃水の処理装置。
In a treatment device for dithionic acid-containing wastewater that adds sulfuric acid to dithionic acid-containing wastewater and thermally decomposes it, sulfuric acid is added to the wastewater and the temperature is 100°C or higher and the pressure is
A closed thermal decomposition tank that maintains 1.15 to 1.20 Kg/ cm2 , a pressure regulating valve attached to the outlet of this closed thermal decomposition tank, and an alkali agent supply device connected to the closed thermal decomposition tank were attached. A treatment device for wastewater containing dithionic acid, comprising a neutralization absorption tank and an oxidation tank connected to the neutralization absorption tank and equipped with an oxidizing agent injection device.
JP19690883U 1983-12-21 1983-12-21 Treatment equipment for wastewater containing dithionic acid Granted JPS60104291U (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP19690883U JPS60104291U (en) 1983-12-21 1983-12-21 Treatment equipment for wastewater containing dithionic acid

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP19690883U JPS60104291U (en) 1983-12-21 1983-12-21 Treatment equipment for wastewater containing dithionic acid

Publications (2)

Publication Number Publication Date
JPS60104291U JPS60104291U (en) 1985-07-16
JPS632149Y2 true JPS632149Y2 (en) 1988-01-20

Family

ID=30422168

Family Applications (1)

Application Number Title Priority Date Filing Date
JP19690883U Granted JPS60104291U (en) 1983-12-21 1983-12-21 Treatment equipment for wastewater containing dithionic acid

Country Status (1)

Country Link
JP (1) JPS60104291U (en)

Family Cites Families (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS5834196B2 (en) * 1975-04-18 1983-07-25 荏原インフイルコ株式会社 Hiendatsuriyuuhaisuinoshiyorihouhou
JPS537967A (en) * 1976-07-09 1978-01-24 Babcock Hitachi Kk Method for treating drain water

Also Published As

Publication number Publication date
JPS60104291U (en) 1985-07-16

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