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JPS6035995B2 - Concentration control method for nitric acid pickling bath - Google Patents
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JPS6035995B2 - Concentration control method for nitric acid pickling bath - Google Patents

Concentration control method for nitric acid pickling bath

Info

Publication number
JPS6035995B2
JPS6035995B2 JP12043478A JP12043478A JPS6035995B2 JP S6035995 B2 JPS6035995 B2 JP S6035995B2 JP 12043478 A JP12043478 A JP 12043478A JP 12043478 A JP12043478 A JP 12043478A JP S6035995 B2 JPS6035995 B2 JP S6035995B2
Authority
JP
Japan
Prior art keywords
acid
pickling
concentration
nitric acid
tank
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
JP12043478A
Other languages
Japanese (ja)
Other versions
JPS5547387A (en
Inventor
正剛 小坂
友夫 高張
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 Steel Corp
Original Assignee
Nippon Steel 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 Nippon Steel Corp filed Critical Nippon Steel Corp
Priority to JP12043478A priority Critical patent/JPS6035995B2/en
Publication of JPS5547387A publication Critical patent/JPS5547387A/en
Publication of JPS6035995B2 publication Critical patent/JPS6035995B2/en
Expired legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C23COATING METALLIC MATERIAL; COATING MATERIAL WITH METALLIC MATERIAL; CHEMICAL SURFACE TREATMENT; DIFFUSION TREATMENT OF METALLIC MATERIAL; COATING BY VACUUM EVAPORATION, BY SPUTTERING, BY ION IMPLANTATION OR BY CHEMICAL VAPOUR DEPOSITION, IN GENERAL; INHIBITING CORROSION OF METALLIC MATERIAL OR INCRUSTATION IN GENERAL
    • C23GCLEANING OR DE-GREASING OF METALLIC MATERIAL BY CHEMICAL METHODS OTHER THAN ELECTROLYSIS
    • C23G1/00Cleaning or pickling metallic material with solutions or molten salts
    • C23G1/36Regeneration of waste pickling liquors

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  • Chemical & Material Sciences (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • General Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Mechanical Engineering (AREA)
  • Metallurgy (AREA)
  • Organic Chemistry (AREA)
  • Cleaning And De-Greasing Of Metallic Materials By Chemical Methods (AREA)

Description

【発明の詳細な説明】 本発明は高合金鋼等の酸洗に使用する硝酸とふつ化水素
酸の露酸(以下硝ふつ酸と記す)の濃度管理法に関する
ものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for controlling the concentration of nitric acid and hydrofluoric acid (hereinafter referred to as nitric acid) used for pickling high alloy steel and the like.

鋼材を熱間加工、あるいは熱処理して生成した酸化スケ
ールを除去する場合、ステンレス鋼等安定なスケールを
有する鋼材の酸洗には通常硝ふっ酸が用いられている。
When removing oxidized scale generated by hot working or heat treating steel materials, nitric hydrofluoric acid is usually used to pickle steel materials with stable scale, such as stainless steel.

酸洗液の酸濃度は酸洗に適した範囲内にある必要があり
、通常適宜硝酸およびふつ化水素酸を補充して濃度調整
を行なっている。また、酸洗液が汚れたり、液中にスケ
ールが堆積した場合には液を排出し新液を補充して使用
している。硝酸、ふつ化水素酸を補充して濃度調整しつ
つ酸洗処理を継続すると酸洗液中にスケールでない沈殿
物が生成して槽内に堆積することがある。
The acid concentration of the pickling solution must be within a range suitable for pickling, and the concentration is usually adjusted by supplementing nitric acid and hydrofluoric acid as appropriate. Additionally, if the pickling solution becomes dirty or scale is deposited in the solution, the solution is drained and refilled with new solution. If the pickling process is continued while adjusting the concentration by replenishing nitric acid or hydrofluoric acid, non-scale precipitates may be formed in the pickling solution and deposited in the tank.

このような沈殿物が堆積するとそれを糟外へ取出すのに
多大の労力を必要とすると共に酸による薬湯が懸念され
る。とくにスプレー酸洗の場合は/ズル閉塞や配管の閉
塞を生じ正常な酸洗処理が行なえなくなる。また、この
ように沈殿物が生成したり、スケ−ル堆積量が増した場
合等に排出した酸洗液中には劣化した酸といえどもかな
りの童の硝酸、ふっ化水素酸が含まれているため、その
まま廃棄することはできず、カーバィド蓬、消石灰等を
加えて中和処理をしなければならない。本発明は、硝ふ
つ酸を用いてステンレス鋼等の鋼材を酸洗するに際し、
前記のごとく堅く堆積する沈殿物の生成を抑制し、かつ
排出した酸洗液から硝酸およびふつ化水素酸を回収する
と共に鉄イオンを除去して効果的な酸洗を行なうための
酸の濃度管理を行なうことを目的とする。
When such precipitates accumulate, it requires a great deal of effort to remove them from the pot, and there is a concern that the bath will be medicated by acid. Particularly in the case of spray pickling, the pickling process may not be carried out normally due to clogging of drains or piping. In addition, even if the acid is degraded, the pickling solution discharged when precipitates are formed or the amount of scale buildup increases contains a considerable amount of nitric acid and hydrofluoric acid. Therefore, it cannot be disposed of as is, and must be neutralized by adding carbide mosaic, slaked lime, etc. In the present invention, when pickling steel materials such as stainless steel using nitric acid,
Acid concentration control to suppress the formation of hard deposits as described above, recover nitric acid and hydrofluoric acid from the discharged pickling solution, and remove iron ions for effective pickling. The purpose is to carry out.

本発明の方法は、酸洗に使用中の硝ふつ酸中の鉄イオン
濃度、およびふつ素イオン濃度がふつ化鉄沈殿物を生成
しない限界内に維持されるように監視し、設定濃度以上
となったとき酸洗液を適宜排出し、イオン交換膜を用い
て酸洗液から硝酸およびふつ化水素酸を回収し、この回
収酸を再利用して酸洗に適した濃度に調整すると共に使
用中の酸洗液中の硝酸およびふつ化水素酸濃度を監視す
ることを特徴とする。
The method of the present invention monitors the iron ion concentration and fluorine ion concentration in the nitric acid used for pickling to ensure that it is maintained within limits that do not produce iron fluoride precipitates, and prevents the concentration from exceeding a set concentration. When this happens, drain the pickling solution appropriately, recover nitric acid and hydrofluoric acid from the pickling solution using an ion exchange membrane, and reuse the recovered acid to adjust the concentration to the appropriate concentration for pickling. It is characterized by monitoring the nitric acid and hydrofluoric acid concentrations in the pickling solution.

従来イオン交換膜は硝酸に弱いものとされ、こ‐のよう
な方式での酸回収はできないとされていたが、近年硝酸
に耐えるものが市販されるようになった結果、本発明が
可能となった。
Conventionally, ion exchange membranes were thought to be weak against nitric acid, and it was thought that acid recovery using this method was impossible, but in recent years, membranes that can withstand nitric acid have become commercially available, making the present invention possible. became.

硝ふっ酸により鉄鋼材料を酸洗するとまず‘11式によ
り鉄が溶解する。
When a steel material is pickled with nitric and hydrofluoric acid, the iron first dissolves according to the '11 formula.

ついで、‘2},【3}式により、この溶解した鉄イオ
ンがふつ化水素酸と反応して鉄ふつ素錯体が生成し、つ
いには【41式によりふつ化鉄となって沈殿する。がe
+母H+→がe3十3日2↑ ‘1
’Fe3十十HF→FeF2十H+
‘21FeF2十HF→FeF2十十日十
‘3’FeF2十十HF→FeF3
↓十日十 {41本発明者らは各種
酸濃度、鉄イオン濃度の液についての実験、および酸洗
槽内に堆積したものを分折することにより、上記FeF
3は水和反応によりがeF3・虫LOとなっていること
を明らかにした。
Then, according to equations '2} and [3}, the dissolved iron ions react with hydrofluoric acid to form an iron fluoride complex, which finally becomes iron fluoride and precipitates according to equation [41]. is e
+ Mother H + → is e3 13th day 2↑ '1
'Fe310HF→FeF20H+
'21FeF20HF→FeF210days10
'3'FeF210HF→FeF3
↓10 days ago {41 The present inventors conducted experiments with liquids with various acid concentrations and iron ion concentrations, and by dissecting the deposits in the pickling tank, the above FeF
3 revealed that eF3/insect LO was formed through a hydration reaction.

また沈殿物の生成は硝酸濃度にはほとんど影響されず、
鉄イオン(F3十)と総ふつ素イオン(T−F‐)濃度
に関係し、これらのイオン濃度が第1図の曲線A以下の
範囲内であれば沈殿を生じないことを確認した。この範
囲内で酸洗効力の大きい範囲として第1図斜線範囲を濃
度管理限界として設定した。すなわち、鉄イオン濃度3
0タノク以下、ふつ素イオン濃度5〜60夕/そであれ
ば酸洗効力も大きく、ふつ化鉄沈殿物も生成しない。ふ
つ化鉄は第1図の曲線B,Cとなるに従い、その生成量
が多くなり、曲線Bでは10夕/そ、曲線Cでは100
夕/そも沈殿する。前記‘1}〜{4)式のうち酸洗に
有効な反応は【1’式のみである。
In addition, the formation of precipitates is hardly affected by nitric acid concentration;
It was confirmed that precipitation does not occur as long as the concentration of iron ions (F30) and total fluorine ions (T-F-) is within the range below curve A in FIG. 1. Within this range, the diagonally shaded range in Figure 1 was set as the concentration control limit as the range where the pickling effect was large. That is, iron ion concentration 3
If the fluorine ion concentration is below 0 Tanok and the fluorine ion concentration is 5 to 60, the pickling effect will be high and no iron fluoride precipitate will be formed. The amount of iron fluoride produced increases as curves B and C appear in Figure 1, with curve B at 10 t/s and curve C at 100 t/s.
Evening/precipitation. Among the above formulas '1} to {4), only formula [1'] is effective for pickling.

また硝酸も鉄を溶解して酸洗に有効である。しかし鉄イ
オンが含まれている状態、で、単に酸を補充したのでは
【21【3}‘41式の反応によってふつ化水素酸が鉄
イオン反応しふつ化鉄沈殿物の生成に消費され、追加分
だけの効果は望めなくなる。したがって、酸洗液中の鉄
イオン濃度、および総ふつ素イオン濃度を管理して、ふ
つ化鉄沈殿物の生成およびふつ化水素酸の無駄な添加を
防止しなければならない。鉄イオン濃度および総ふつ素
イオン濃度が第1図の曲線A以下であればふつ化鉄沈殿
物は生成しない。しかし【2’,‘3}式により鉄・ふ
つ化錆体が生成し、添加するふっ化水素酸が浪費される
。生成する鍔体は第1図の曲線Dを境として右下の領域
ではFeF2十、左上の領域ではFeFまであった。し
たがってふつ化鉄が沈殿しない領域であっても鉄イオン
濃度はできるだけ低いことが望ましい。また総ふつ素イ
オン濃度も同様にできるだけ低いことが望ましいが、酸
洗処理のために最水限は必要である。このような葛馬点
から鉄イオン濃度、総ふつ素イオン濃度を第1図斜線内
に維持することが望ましい。すなわち酸洗液中の鉄イオ
ン濃度および総ふつ素イオン濃度を測定し、各濃度が第
1図の斜線範囲を超えないように排液して硝酸およびふ
つ化水素酸を補充し、酸濃度を酸洗に適した範囲内に調
整する。
Nitric acid also dissolves iron and is effective for pickling. However, in a state where iron ions are contained, if acid is simply replenished, hydrofluoric acid reacts with iron ions and is consumed to form iron fluoride precipitates through the reaction of formula 21 [3}'41. You won't be able to expect the effect of the additional amount. Therefore, the iron ion concentration and total fluorine ion concentration in the pickling solution must be controlled to prevent the formation of iron fluoride precipitates and the wasteful addition of hydrofluoric acid. If the iron ion concentration and total fluorine ion concentration are below curve A in FIG. 1, no iron fluoride precipitate will be formed. However, due to the formula [2', '3}, iron and fluorinated rust are produced, and the added hydrofluoric acid is wasted. The produced flanges were as high as 20 FeF in the lower right region of the curve D in FIG. 1 and up to FeF in the upper left region. Therefore, it is desirable that the iron ion concentration be as low as possible even in a region where iron fluoride does not precipitate. It is also desirable that the total fluorine ion concentration be as low as possible, but a maximum water limit is required for pickling treatment. It is desirable to maintain the iron ion concentration and total fluorine ion concentration within the diagonal lines in FIG. 1 from such a point. In other words, the iron ion concentration and total fluorine ion concentration in the pickling solution were measured, and the acid concentration was adjusted by draining the solution and replenishing it with nitric acid and hydrofluoric acid so that each concentration did not exceed the shaded range in Figure 1. Adjust to a range suitable for pickling.

硝酸およびふつ化水素酸の濃度は鋼種、スケールの状態
によって異なるが、例えば熱間圧延競錨後のステンレス
鋼の場合HN03は20〜100夕/ど、HFは5〜5
0夕/夕が適している。補充する硝酸およびふつ化水素
酸は、排液からイオン交換膜によって回収したものを用
い、不足分を新酸で補う。以下、本発明の方法を第2図
に従って説明する。
The concentration of nitric acid and hydrofluoric acid varies depending on the steel type and scale condition, but for example, in the case of hot-rolled stainless steel, HN03 is 20 to 100 m/d, HF is 5 to 5
0 evening/evening is suitable. The nitric acid and hydrofluoric acid to be replenished are those recovered from the wastewater using an ion exchange membrane, and the shortage is supplemented with new acid. The method of the present invention will be explained below with reference to FIG.

硝ふつ酸酸洗槽1は、糟内に鉄鋼材料を浸糟するか、糟
中の液を鉄鋼材料にスプレーして循環し酸洗処理を行う
ものである。酸洗槽1中の鉄イオン、総ふつ素イオンを
分折装置5で分析しモニターする。鉄イオン、総ふつ素
イオンが、第1図斜線で示した範囲内を常に維持するよ
うにFe3十が30夕/そ、F‐が60タノクを超えた
とき槽内の一部或は全部の酸洗液を排出し、廃酸貯溜槽
2に導入し、回収酸貯溜槽4および必要に応じて新酸タ
ンク6および水8を加えて酸洗に適した酸濃度に調整す
る。廃酸貯溜槽2内の廃酸は、拡散透折槽3に導入し、
陰イオン交換膜によってふつ化水素酸および硝酸を回収
する。拡散透折槽3内においては、第3図に示すごとく
陰イオン交換膜7を隔てて廃酸Sと水Wを向流させる。
得られた回収酸Rは回収酸貯溜槽4に導入し、Fe3十
を王とする金属イオンを主成分とする透折液Fは廃酸処
理設備に導く。透折液中には、少量ではあるが未回収の
硝酸ふつ化水素酸が含まれているため中和処理が必要で
ある。回収酸貯溜槽4中の回収酸は、分折装置5によっ
て硝酸濃度およびふつ化水素酸濃度を測定し、酸洗槽1
への導入に備える。酸洗槽1からの酸の排出は、酸洗処
理を間歌的に行う場合等には一時に全量排出することが
できるが、ストリップの連続酸洗等連続的に酸洗処理を
行っている間は、酸洗処理に支障ない程度に一部を排出
し、回収酸および必要に応じて新酸を導入する。又、硝
ふつ酸酸洗槽1からの酸の排出および回収酸、新酸の導
入を連続して行い、酸洗液の‐ 量、ふつ化鉄沈殿物を
生じないFe3十、F−濃度および酸洗処理に適したH
N03、HF濃度を維持するよう、分折装置5の測定結
果によって排出および導入量を調整するのが望ましい。
なお、回収酸貯溜槽4および廃酸貯溜槽2は連続して処
理する場合には省略しても良い。
The nitric acid pickling tank 1 performs pickling treatment by soaking the steel material in a casing or by spraying a liquid in the casing onto the steel material and circulating it. Iron ions and total fluorine ions in the pickling tank 1 are analyzed and monitored using a spectrometer 5. In order to always maintain iron ions and total fluorine ions within the range shown by the diagonal lines in Figure 1, when Fe30 exceeds 30 T/so, when F- exceeds 60 T, some or all of the inside of the tank is The pickling solution is discharged and introduced into the waste acid storage tank 2, and the recovered acid storage tank 4 and, if necessary, a new acid tank 6 and water 8 are added to adjust the acid concentration to a suitable level for pickling. The waste acid in the waste acid storage tank 2 is introduced into the diffusion filtration tank 3,
Hydrofluoric acid and nitric acid are recovered by an anion exchange membrane. In the diffusion filtration tank 3, the waste acid S and water W are caused to flow in countercurrents across the anion exchange membrane 7, as shown in FIG.
The obtained recovered acid R is introduced into a recovered acid storage tank 4, and the filtered liquid F, which is mainly composed of metal ions mainly composed of Fe30, is introduced to a waste acid treatment facility. The filtered liquid contains a small amount of unrecovered nitric acid and hydrofluoric acid, so neutralization treatment is necessary. The recovered acid in the recovered acid storage tank 4 is subjected to measurement of nitric acid concentration and hydrofluoric acid concentration by a spectrometer 5, and then transferred to the pickling tank 1.
Prepare for the introduction of The acid can be discharged from the pickling tank 1 in its entirety at once when the pickling process is carried out intermittently, but in cases where the pickling process is carried out continuously, such as continuous pickling of strips. During this time, a portion of the acid is discharged to the extent that it does not interfere with the pickling process, and recovered acid and new acid are introduced as necessary. In addition, by continuously discharging the acid from the nitric acid pickling tank 1 and introducing the recovered acid and new acid, the amount of the pickling solution, Fe30, F-concentration, and H suitable for pickling treatment
In order to maintain the N03 and HF concentrations, it is desirable to adjust the amounts of discharge and introduction based on the measurement results of the spectrometer 5.
Note that the recovered acid storage tank 4 and the waste acid storage tank 2 may be omitted when processing is performed continuously.

次に本発明の実施例を示す。Next, examples of the present invention will be shown.

実施例 分折計でモニターして鉄イオン濃度が279/夕、総ふ
っ素イオン濃度が23.6夕/そとなった酸洗液下記■
10従を酸洗槽から引き抜き、417〆/日の割合し、
で拡散透折装置へ導入した。
Example A pickling solution with an iron ion concentration of 279/unit and a total fluorine ion concentration of 23.6/unit as monitored with a spectrometer.
10 pieces were pulled out from the pickling tank and processed at a rate of 417〆/day,
It was introduced into a diffuser spectroscopy device.

上水を512〆/Hrの割合で流入して酸回収を行なっ
たところ下記濃度■の回収酸が410ぞ/日の割合で得
られた。このときの硝酸およびふつ酸の回収率は各々7
1%及び57%であった。この回収酸に62%硝酸およ
び56%のふつ酸を分折計の指示をみながら補充し、硝
酸25.5多/そふつ酸14.4夕/そとした。このと
きの補充量は硝酸3.6夕/日、ふつ酸4.0ぞ/日で
あった。この調製した酸洗液を酸洗槽に戻し酸洗を行な
ったところ効果的に酸洗することができた。酸洗するこ
とによりステンレス鋼帯の地金およびスケールが溶出す
ることにより酸洗液中の鉄イオン濃度は増加し、酸洗に
有効なふつ酸および硝酸は減少するが、分折計で硝酸お
よびふつ酸濃度を監視し、常に硝酸255夕/夕、ふつ
酸14.4夕/夕となるように酸を追加して酸洗した。
これにより効果的に酸洗を継続することができた。また
分折計で鉄イオン濃度を連続して測定し、それが30夕
/Z‘こ近ずくごとに上記操作を操返えすことにより、
沈殿を生じることないこ連続して酸洗することが可能と
なった。■ 酸洗液組成 ■ 回収酸組成 HN0325.5 9/2 HN03 18.9
9/多HF 14・4 9/多 HF 8
‐4 9/多Fe 27 g/多 Fe
l.4 9/多以上述べたごとく、本発明によれば硝ふ
つ酸酸洗液中にふつ化鉄三沈殿物が発生するこをがない
ので、特にスプレー酸洗時のトラブルがなく、また堅い
沈殿堆積物の除去作業が不要となる。
When the acid was recovered by flowing clean water at a rate of 512 〆/hr, recovered acid with the following concentration (■) was obtained at a rate of 410 〆/day. The recovery rates of nitric acid and hydrofluoric acid at this time were 7 each.
1% and 57%. The recovered acid was replenished with 62% nitric acid and 56% fluoric acid while checking the instructions on the spectrometer to give 25.5% nitric acid/14.4% sulfuric acid. The amount of replenishment at this time was 3.6 evenings/day of nitric acid and 4.0 nights/day of hydrofluoric acid. When the prepared pickling solution was returned to the pickling tank and pickling was performed, effective pickling was achieved. Pickling causes the base metal and scale of the stainless steel strip to elute, increasing the concentration of iron ions in the pickling solution and reducing the amount of fluoric acid and nitric acid, which are effective for pickling. The acid concentration was monitored and acid was added so that the concentration of nitric acid was 255 t/night and the concentration of nitric acid was 14.4 t/d.
This allowed the pickling to continue effectively. In addition, by continuously measuring the iron ion concentration with a spectrometer and repeating the above operation every 30 days/Z',
It became possible to carry out continuous pickling without causing precipitation. ■ Pickling liquid composition ■ Recovered acid composition HN0325.5 9/2 HN03 18.9
9/multi HF 14・4 9/multi HF 8
-4 9/Poly Fe 27 g/Poly Fe
l. 4 9/ As stated above, according to the present invention, there is no occurrence of iron fluoride tri-precipitates in the nitrate pickling solution, so there is no particular trouble during spray pickling, and there is no hard precipitate build-up. There is no need to remove objects.

さらに従来廃棄していた廃酸から硝酸およびふつ化水素
酸を回収して循環使用するので酸洗コストが低減する。
又廃棄酸は酸濃度が従来に比し大中に低減するので中和
剤の減少等廃酸処理におけるメリットも大きい。
Furthermore, pickling costs are reduced because nitric acid and hydrofluoric acid are recovered and recycled from waste acid that was conventionally discarded.
In addition, since the acid concentration of waste acid is reduced compared to conventional methods, there are great advantages in waste acid treatment, such as a reduction in the amount of neutralizing agent.

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

第1図はふっ化鉄沈殿物を発生しない濃度範囲を示す図
、第2図は本発明法を行うための系統図、第3図は第2
図中の拡散透折槽3内の詳細を示す図である。 第3図 第1図 第2図
Figure 1 is a diagram showing the concentration range that does not generate iron fluoride precipitates, Figure 2 is a system diagram for carrying out the method of the present invention, and Figure 3 is a diagram showing the concentration range in which iron fluoride precipitates are not generated.
It is a figure which shows the detail inside the diffusion-transmission tank 3 in a figure. Figure 3 Figure 1 Figure 2

Claims (1)

【特許請求の範囲】 1 酸洗槽内の酸洗液を連続的又は間歇的に酸洗槽外に
導き、イオン交換膜により硝酸およびふつ化水素酸を回
収し、この回収した酸を(必要に応じて新酸を補充する
)酸洗槽に導入することにより、酸洗槽内の鉄イオン濃
度および総ふつ素イオン濃度をふつ化鉄沈殿物が生成す
る限界濃度内に維持し、かつ酸洗槽内の酸濃度を酸洗に
適した濃度に調整することを特徴とする硝ふつ酸酸洗浴
の濃度管理法。 2 酸洗槽内の鉄イオン濃度および総ふつ素イオン濃度
がふっ化鉄沈殿物を生成する限界内の一定濃度を超えた
ときに、槽内の一部または全部の酸洗液を酸洗槽外に導
き、イオン交換膜により硝酸およびふつ化水素酸を回収
し、この回収した酸(必要に応じて新酸を補充する)を
酸洗槽に導入して、酸洗槽内の酸濃度を酸洗に適した濃
度に調整することを特徴とする硝ふつ酸酸洗浴の濃度管
理法。
[Claims] 1. The pickling solution in the pickling tank is continuously or intermittently led out of the pickling tank, nitric acid and hydrofluoric acid are recovered by an ion exchange membrane, and the recovered acid is By introducing new acid into the pickling tank, the iron ion concentration and total fluorine ion concentration in the pickling tank can be maintained within the critical concentration at which iron fluoride precipitates are formed, and the acid A concentration control method for a nitric acid pickling bath characterized by adjusting the acid concentration in the washing tank to a concentration suitable for pickling. 2. When the iron ion concentration and total fluorine ion concentration in the pickling tank exceed a certain concentration within the limit for producing iron fluoride precipitates, some or all of the pickling solution in the tank is removed from the pickling tank. Nitric acid and hydrofluoric acid are recovered using an ion exchange membrane, and the recovered acid (replenishing new acid as necessary) is introduced into the pickling tank to reduce the acid concentration in the pickling tank. A method for controlling the concentration of a nitric acid pickling bath, which is characterized by adjusting the concentration to a concentration suitable for pickling.
JP12043478A 1978-10-02 1978-10-02 Concentration control method for nitric acid pickling bath Expired JPS6035995B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP12043478A JPS6035995B2 (en) 1978-10-02 1978-10-02 Concentration control method for nitric acid pickling bath

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP12043478A JPS6035995B2 (en) 1978-10-02 1978-10-02 Concentration control method for nitric acid pickling bath

Publications (2)

Publication Number Publication Date
JPS5547387A JPS5547387A (en) 1980-04-03
JPS6035995B2 true JPS6035995B2 (en) 1985-08-17

Family

ID=14786107

Family Applications (1)

Application Number Title Priority Date Filing Date
JP12043478A Expired JPS6035995B2 (en) 1978-10-02 1978-10-02 Concentration control method for nitric acid pickling bath

Country Status (1)

Country Link
JP (1) JPS6035995B2 (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPS6054394B2 (en) * 1982-05-21 1985-11-29 株式会社トクヤマ How to prepare pickling solution
AT374508B (en) * 1982-07-01 1984-05-10 Ruthner Industrieanlagen Ag METHOD FOR PROCESSING USED BEIZER OR CORROSIVE SOLUTIONS BASED ON SALPETER FLUORIC ACID
CN106048626A (en) * 2016-07-06 2016-10-26 浙江久德不锈钢型材有限公司 Acid pickling process of stainless steel resistant to salt fog

Also Published As

Publication number Publication date
JPS5547387A (en) 1980-04-03

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