JP3018018B2 - Metal chloride treatment method - Google Patents
Metal chloride treatment methodInfo
- Publication number
- JP3018018B2 JP3018018B2 JP3207475A JP20747591A JP3018018B2 JP 3018018 B2 JP3018018 B2 JP 3018018B2 JP 3207475 A JP3207475 A JP 3207475A JP 20747591 A JP20747591 A JP 20747591A JP 3018018 B2 JP3018018 B2 JP 3018018B2
- Authority
- JP
- Japan
- Prior art keywords
- fuel
- metal chloride
- roasting furnace
- chlorine
- furnace
- 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 - Fee Related
Links
Landscapes
- Gasification And Melting Of Waste (AREA)
- Crucibles And Fluidized-Bed Furnaces (AREA)
- ing And Chemical Polishing (AREA)
Description
【0001】[0001]
【産業上の利用分野】本発明は、エッチング廃液処理過
程で発生する金属塩化物から塩素分を分離し、分離物を
独立に回収する方法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for separating chlorine from metal chlorides generated in a process of treating an etching waste liquid and independently recovering the separated substances.
【0002】[0002]
【従来の技術】一般に、エッチング廃液はこのエッチン
グ廃液中に塩化物として含有されたニッケル、クロム、
銅、鉄等を除去してエッチング用液として再生される。
この処理過程で生成する金属塩化物はこの金属塩化物を
10〜100倍の水で希釈攪拌し、その後、ろ過を行い
低塩素澱物とすることにより処理されている。また、前
記の湿式処理に対して、特開昭50−38967号公報
のように、塩分含有量の高い廃棄物を流動床内で流動化
ガスの吹き込み速度を3m/secとして供給して流動
床内の燃焼温度を廃棄物の融点以上に保持し、塩分の主
たる部分を排ガスとともに排出する焼却方法等が提案さ
れている。2. Description of the Related Art Generally, an etching waste liquid contains nickel, chromium,
It is regenerated as an etching solution by removing copper, iron and the like.
The metal chloride produced in this process is treated by diluting and stirring the metal chloride with 10 to 100 times the amount of water, followed by filtration to obtain a low chlorine precipitate. Further, in contrast to the above wet treatment, as disclosed in JP-A-50-38967, waste having a high salt content is supplied in a fluidized bed at a blowing speed of a fluidizing gas of 3 m / sec, and the fluidized bed is supplied. An incineration method and the like have been proposed in which the combustion temperature in the inside is maintained at a temperature equal to or higher than the melting point of the waste, and the main part of the salt is discharged together with the exhaust gas.
【0003】[0003]
【発明が解決しようとする課題】しかしながら、エッチ
ング廃液から分離されたニッケル澱物を例に述べると、
前記の希釈攪拌ろ過ではニッケル澱物付着物から、不溶
解性塩化鉄塩が生成し塩素の除去が完全でない。また、
大量のFeCl2 含有排水が発生するとともに、この排
水を処理する際にろ過性の悪い水酸化鉄澱物が生成す
る。しかも、この水酸化鉄澱物を搬送、廃棄する必要が
あり、処理を含めた総合コストが極めて高い。一方、塩
分含有量の高い廃棄物を流動床内で流動化ガスの吹き込
み速度を3m/secで供給して流動床内の燃焼温度を
廃棄物の融点以上に保持し、塩分の主たる部分を排ガス
とともに排出する方法は流動床内の燃焼温度を廃棄物の
融点以上に保持するため工業用化石燃料の消費が極めて
高く、高温であるために流動処理自体も容易でない。更
に、この流動床内の燃焼温度を低くした際は低温となる
ために、不溶解性塩化鉄塩の分解が出来ないため商品中
の塩素含有率が高く商品価値が低い。しかも、この低温
処理方法では同一の水分のニッケル澱物処理でも燃料原
単位が高く、発生する排ガス量も極めて多い等の欠点が
ある。本発明はこれ等従来法の欠点である塩化物の除去
を確実に行うとともに、この塩化物を低いエネルギー消
費で除去し、しかも、発生する排ガスが少なく処理コス
トの安価な塩化物の脱塩素処理を可能とする金属塩化物
の処理方法の提供にある。However, the nickel deposit separated from the etching waste liquid is taken as an example.
In the above-mentioned dilution stirring filtration, insoluble iron chloride salts are formed from the deposits of nickel deposits, and chlorine is not completely removed. Also,
A large amount of wastewater containing FeCl 2 is generated, and when the wastewater is treated, an iron hydroxide precipitate having poor filterability is generated. In addition, it is necessary to transport and discard the iron hydroxide deposit, and the total cost including the treatment is extremely high. On the other hand, waste having a high salt content is supplied in the fluidized bed at a blowing speed of the fluidizing gas of 3 m / sec to maintain the combustion temperature in the fluidized bed above the melting point of the waste, and the main part of the salt is discharged into the exhaust gas. In the method of discharging together with the waste, the combustion temperature in the fluidized bed is kept above the melting point of the waste, so that the consumption of industrial fossil fuel is extremely high, and the fluidization itself is not easy due to the high temperature. Further, when the combustion temperature in the fluidized bed is lowered, the temperature becomes low, and the insoluble iron chloride salt cannot be decomposed, so that the chlorine content in the product is high and the commercial value is low. In addition, this low-temperature processing method has disadvantages such as a high fuel consumption rate and an extremely large amount of exhaust gas even when the nickel deposit is treated with the same moisture. The present invention reliably removes chloride, which is a drawback of these conventional methods, and removes this chloride with low energy consumption, and furthermore, generates less exhaust gas and has a low processing cost. It is an object of the present invention to provide a method for treating a metal chloride which enables the following.
【0004】[0004]
【課題を解決するための手段】本発明に係る金属塩化物
の処理方法は、エッチング廃液処理過程で澱物として生
成する金属塩化物の塩素分除去方法であって、湿粉状態
の前記澱物を含水素燃料またはアルカン系気体燃料を燃
料とする流動焙焼炉にて500〜700℃、過剰酸素濃
度0.5〜5%、炉内滞在時間20分以上にて焙焼処理
し、該流動焙焼炉のオーバーフロー分と、ダストチャン
バーで回収された低塩化鉄粉を製品として回収すると共
に、該流動焙焼炉からのガスを冷却し、シックナーで沈
澱処理した後該シックナーから塩素分含有液を回収する
ようにして構成されている。ここで、含水素燃料とは水
素ガスが混入している気体燃料をいい、アルカン系気体
燃料とは、例えば、プロパン、ブタン等をいう。According to the present invention, there is provided a method for treating a metal chloride, which comprises removing chlorine from a metal chloride produced as a precipitate in a process of treating an etching waste liquid. Is roasted in a fluidized roasting furnace using a hydrogen-containing fuel or an alkane-based gaseous fuel as a fuel at 500 to 700 ° C., an excess oxygen concentration of 0.5 to 5%, and a residence time in the furnace of 20 minutes or more. The overflow from the roasting furnace and the low iron chloride powder collected in the dust chamber are collected as products, and the gas from the fluidized roasting furnace is cooled and subjected to precipitation treatment with a thickener. Is configured to be collected. Here, the hydrogen-containing fuel refers to a gaseous fuel mixed with hydrogen gas, and the alkane-based gaseous fuel refers to, for example, propane, butane and the like.
【0005】[0005]
【作用】本発明に係る金属塩化物の処理方法において
は、エッチング廃液処理過程で発生する湿粉状態の澱物
を流動焙焼炉にて、含水素燃料またはアルカン系気体燃
料を燃料として、500〜700℃、過剰酸素濃度0.
5〜5%、炉内滞在時間20分以上の条件で焙焼処理し
ている。従って、湿粉状態の澱物から供給される水分及
び含水素燃料またはアルカン系気体燃料の燃焼によって
生じる水分が、金属塩化物に作用してHClを生じさ
せ、これによって金属塩化物から塩素分が除去される。
そして、燃焼温度が500〜700℃となっているの
で、燃料コスト、焙焼設備の高騰を招くことなく、過剰
酸素濃度も適性な範囲にあるので、燃料の不燃化を生じ
ることなく、更には過剰酸素によって金属の酸化を進め
ることがない。In the method for treating metal chlorides according to the present invention, the wet powdery sediment generated in the etching waste liquid treatment process is processed in a fluidized roasting furnace using a hydrogen-containing fuel or an alkane-based gaseous fuel as a fuel. ~ 700 ° C, excess oxygen concentration 0.
The roasting process is performed under the conditions of 5 to 5% and the residence time in the furnace is 20 minutes or more. Therefore, the water supplied from the wet powdered sediment and the water generated by the combustion of the hydrogen-containing fuel or the alkane-based gaseous fuel act on the metal chloride to generate HCl, whereby chlorine is separated from the metal chloride. Removed.
Since the combustion temperature is 500 to 700 ° C., the fuel cost and the roasting equipment are not soared, and the excess oxygen concentration is in an appropriate range. Excess oxygen does not promote metal oxidation.
【0006】[0006]
【実施例】続いて、添付した図面を参照しつつ、本発明
を具体化した実施例につき説明し、本発明の理解に供す
る。図1には本発明の一実施例に係る金属塩化物の処理
方法のフロー図を示すが、図に示すように、原料である
エッチング廃液処理で発生する澱物10の成分を表1に
示す。DESCRIPTION OF THE PREFERRED EMBODIMENTS Embodiments embodying the present invention will now be described with reference to the accompanying drawings to provide an understanding of the present invention. FIG. 1 shows a flow chart of a method for treating a metal chloride according to one embodiment of the present invention. As shown in the figure, Table 1 shows the components of the precipitate 10 generated in the treatment of the etching waste liquid as a raw material. .
【0007】[0007]
【表1】 [Table 1]
【0008】表1に示すように、澱物10にはNi粉、
鉄粉の他、相当量の塩化第1鉄の粉末を含んでいる。該
澱物10をテーブルフィーダー11を介して流動焙焼炉
12に入れる。この流動焙焼炉12は燃料としてアルカ
ン系気体燃料の一例であるプロパンを燃料とし、コンプ
レッサーによってエアを供給している。前記プロパンの
供給量は0.209Nm3 であり、空気の供給量は5.
97Nm3 として過剰酸素とし、ガス燃料を直接流動層
に噴射させるようにする。そして、空塔速度を30〜2
00cm/sec として、該澱物10が500〜700℃の
温度で20〜120分間焙焼できるようにする。これに
よって、発生する水分と塩化鉄とが反応して塩化水素が
発生すると共に、金属鉄が生成される。該流動焙焼炉1
2のオーバーフロー分と、ダストチャンバー13によっ
て回収されたダストは乾燥金属粉14からなり、この乾
燥金属粉14の成分を表2に示すが、塩素分が極めて少
ないことが分かる。As shown in Table 1, the precipitate 10 contains Ni powder,
It contains a considerable amount of ferrous chloride powder in addition to iron powder. The sediment 10 is put into a fluidized roasting furnace 12 via a table feeder 11. The fluidized roasting furnace 12 uses propane, which is an example of an alkane-based gaseous fuel, as fuel, and supplies air by a compressor. The propane supply was 0.209 Nm 3 and the air supply was 5.
Excess oxygen is set as 97 Nm 3 , and gas fuel is directly injected into the fluidized bed. And the superficial tower speed is 30-2
At a rate of 00 cm / sec, the precipitate 10 can be roasted at a temperature of 500 to 700 ° C. for 20 to 120 minutes. As a result, the generated moisture and iron chloride react with each other to generate hydrogen chloride and also generate metallic iron. The fluidized roasting furnace 1
2 and the dust collected by the dust chamber 13 consist of dry metal powder 14. The components of the dry metal powder 14 are shown in Table 2, and it can be seen that the chlorine content is extremely small.
【0009】[0009]
【表2】 [Table 2]
【0010】前記ダストチャンバー13からの気流を冷
却塔15及び洗浄塔16によって冷却、洗浄して、その
冷却液及び洗浄液と、次工程の電気集塵機17によって
回収された粉塵とをシックナー18に入れて、その上澄
液と澱物とを分離する。この上澄液には約15%の塩酸
を含むのでこれを資源として回収する。なお、この塩酸
を含む水をFeCl2 から高濃度のFeCl3 を製造す
る塩鉄処理工程の補給源として使用することもでき、こ
れによって更に資源を有効に利用できる。前記電気集塵
機17から発生する気体には、未回収の塩酸が含有して
おり、そのまま大気中に拡散すると公害となるので、除
害塔19によって苛性ソーダー水溶液(または水酸化カ
ルシウム溶液)に塩酸を吸収させて食塩化し、無害化し
た気体をブロワー20によって吸引させて大気中に放出
する。なお、21は循環ポンプを示す。従って、大気中
には完全に塩素分の除去された空気が排出されることに
なる。The air flow from the dust chamber 13 is cooled and washed by a cooling tower 15 and a washing tower 16, and the cooling liquid and the washing liquid and the dust collected by an electric dust collector 17 in the next step are put into a thickener 18. The supernatant and the sediment are separated. Since the supernatant contains about 15% hydrochloric acid, this is recovered as a resource. The water containing hydrochloric acid can also be used as a replenishing source in the ferrous salt treatment process for producing high-concentration FeCl 3 from FeCl 2 , whereby resources can be used more effectively. The gas generated from the electrostatic precipitator 17 contains unrecovered hydrochloric acid. If the gas is diffused into the atmosphere as it is, it will cause pollution. Therefore, the hydrochloric acid is added to the caustic soda aqueous solution (or calcium hydroxide solution) by the detoxification tower 19. The gas that has been absorbed and converted into salt and made harmless is sucked by the blower 20 and released into the atmosphere. Reference numeral 21 denotes a circulation pump. Accordingly, air from which chlorine content has been completely removed is discharged into the atmosphere.
【0011】[0011]
【発明の効果】本発明に係る金属塩化物の処理方法は以
上の説明からも明らかなように、塩化物の除去が略完全
に行われているので、金属資源としての利用価値が大き
いと共に、塩素分も塩酸として回収しているので、資源
の有効利用を図ることができる。そして、その処理温度
が500〜700℃と比較的低いので、燃料コスト及び
焙焼炉及びその付帯設備の低廉化を招くことができる。As is clear from the above description, the method for treating metal chlorides according to the present invention has almost complete removal of chlorides, so that the method has a great value as a metal resource. Since chlorine is also recovered as hydrochloric acid, resources can be effectively used. Since the processing temperature is relatively low at 500 to 700 ° C., the fuel cost and the cost of the roasting furnace and its accompanying equipment can be reduced.
【図1】本発明の一実施例に係る金属塩化物の処理方法
のフロー図である。FIG. 1 is a flowchart of a method for treating a metal chloride according to one embodiment of the present invention.
10 澱物 11 テーブルフィーダー 12 流動焙焼炉 13 ダストチャンバー 14 乾燥金属粉 15 冷却塔 16 洗浄塔 17 電気集塵機 18 シックナー 19 除害塔 20 ブロワー 21 循環ポンプ DESCRIPTION OF SYMBOLS 10 Deposit 11 Table feeder 12 Fluid roasting furnace 13 Dust chamber 14 Dry metal powder 15 Cooling tower 16 Washing tower 17 Electric dust collector 18 Thickener 19 Detoxification tower 20 Blower 21 Circulation pump
───────────────────────────────────────────────────── フロントページの続き (72)発明者 栗栖 誠一 福岡県北九州市戸畑区飛幡町1番1号 新日本製鐵株式会社 八幡製鐵所内 (72)発明者 笹原 英義 福岡県北九州市戸畑区飛幡町1番1号 新日本製鐵株式会社 八幡製鐵所内 (56)参考文献 特開 昭50−38967(JP,A) (58)調査した分野(Int.Cl.7,DB名) C23F 1/46 F23G 7/00 F27B 15/00 ──────────────────────────────────────────────────続 き Continued on the front page (72) Inventor Seiichi Kurisu 1-1, Tobata-cho, Tobata-ku, Kitakyushu-shi, Fukuoka Nippon Steel Corporation Inside Yawata Works (72) Inventor Hideyoshi Sasahara Toba-ku, Tobata-ku, Kitakyushu-shi, Fukuoka No. 1-1, Nippon Steel Corporation Yawata Works (56) References JP-A-50-38967 (JP, A) (58) Fields investigated (Int. Cl. 7 , DB name) C23F 1 / 46 F23G 7/00 F27B 15/00
Claims (1)
成する金属塩化物の塩素分除去方法であって、前記澱物
を含水素燃料またはアルカン系気体燃料を燃料とする流
動焙焼炉にて500〜700℃、過剰酸素濃度0.5〜
5%、炉内滞在時間20分以上にて焙焼処理し、該流動
焙焼炉のオーバーフロー分と、ダストチャンバーで回収
された低塩化鉄粉を製品として回収すると共に、該流動
焙焼炉からのガスを冷却し、シックナーで沈澱処理した
後該シックナーから塩素分含有液を回収することを特徴
とする金属塩化物の処理方法。1. A method for removing chlorine from a metal chloride produced as a deposit in a process of treating an etching waste liquid, wherein the deposit is subjected to a fluid roasting furnace using a hydrogen-containing fuel or an alkane-based gas fuel as a fuel. ~ 700 ° C, excess oxygen concentration 0.5 ~
5%, a roasting treatment at a furnace stay time of 20 minutes or more, the overflow portion of the fluidized roasting furnace and the low iron chloride powder collected in the dust chamber are recovered as products, and the fluidized roasting furnace is recovered. Cooling the gas and precipitating with a thickener and recovering a chlorine-containing liquid from the thickener.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3207475A JP3018018B2 (en) | 1991-07-23 | 1991-07-23 | Metal chloride treatment method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP3207475A JP3018018B2 (en) | 1991-07-23 | 1991-07-23 | Metal chloride treatment method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPH0525663A JPH0525663A (en) | 1993-02-02 |
| JP3018018B2 true JP3018018B2 (en) | 2000-03-13 |
Family
ID=16540371
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP3207475A Expired - Fee Related JP3018018B2 (en) | 1991-07-23 | 1991-07-23 | Metal chloride treatment method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JP3018018B2 (en) |
Families Citing this family (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| AT399516B (en) * | 1993-07-21 | 1995-05-26 | Andritz Patentverwaltung | METHOD FOR REGENERATING Hydrochloric Acid From Pickling Plants |
-
1991
- 1991-07-23 JP JP3207475A patent/JP3018018B2/en not_active Expired - Fee Related
Also Published As
| Publication number | Publication date |
|---|---|
| JPH0525663A (en) | 1993-02-02 |
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Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| LAPS | Cancellation because of no payment of annual fees |