JP2949545B2 - Treatment and recovery of metal surface treatment waste acid - Google Patents
Treatment and recovery of metal surface treatment waste acidInfo
- Publication number
- JP2949545B2 JP2949545B2 JP4325290A JP32529092A JP2949545B2 JP 2949545 B2 JP2949545 B2 JP 2949545B2 JP 4325290 A JP4325290 A JP 4325290A JP 32529092 A JP32529092 A JP 32529092A JP 2949545 B2 JP2949545 B2 JP 2949545B2
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- Japan
- Prior art keywords
- acid
- waste
- recovered
- treatment
- volatile
- Prior art date
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Classifications
-
- C—CHEMISTRY; METALLURGY
- C23—COATING 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
- C23G—CLEANING OR DE-GREASING OF METALLIC MATERIAL BY CHEMICAL METHODS OTHER THAN ELECTROLYSIS
- C23G1/00—Cleaning or pickling metallic material with solutions or molten salts
- C23G1/36—Regeneration of waste pickling liquors
Landscapes
- 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)
- ing And Chemical Polishing (AREA)
Description
【発明の詳細な説明】DETAILED DESCRIPTION OF THE INVENTION
【0001】[0001]
【産業上の利用分野】本発明は金属表面処理廃酸の処理
回収法に関する。BACKGROUND OF THE INVENTION 1. Field of the Invention The present invention relates to a method for treating and recovering metal surface treatment waste acid.
【0002】[0002]
【従来技術とその問題点】従来、普通鋼、ステンレス鋼
及びアルミニウム材の酸洗いやエッチングなどの表面処
理には、塩酸、硝酸などのような揮発性酸の単酸又は混
合酸が、必要に応じ少量の硫酸を添加して使用されてい
る。2. Description of the Related Art Conventionally, for a surface treatment such as pickling and etching of ordinary steel, stainless steel and aluminum materials, a single acid or a mixed acid of a volatile acid such as hydrochloric acid or nitric acid is required. It is used with a small amount of sulfuric acid added.
【0003】而して上記の金属表面処理工程から排出さ
れる廃酸中には、揮散性酸の遊離酸並びにその金属塩例
えば塩化鉄(塩化アルミニウム)、硝酸鉄(硝酸アルミ
ニウム)などが含まれている。[0003] The waste acid discharged from the above metal surface treatment step contains a free acid of a volatile acid and a metal salt thereof such as iron chloride (aluminum chloride) and iron nitrate (aluminum nitrate). ing.
【0004】このような廃酸の処理回収法として、蒸留
法の適用が考えられる。例えば塩酸系廃酸の場合には、
HClは比揮発度が大きいのでベーパーとして留出し易
く、特に廃酸中に含まれる金属塩の溶解度が高いこと
と、高濃度の金属塩溶液中ではHClの比揮発度はさら
に大きくなることから蒸留缶内に残留する母液内のHC
l濃度が非常に低くなり、大部分のHClを留出回収で
きる。また硝酸系廃酸の場合も、HNO3 はHCl程で
はないが、比揮発度はかなり大であり、また塩酸系と同
様、金属塩の溶解度も極めて大きいので、大部分のHN
O3 を留出回収できる。As a method for treating and recovering such waste acid, application of a distillation method can be considered. For example, in the case of hydrochloric acid waste acid,
HCl has a high specific volatility, so it is easy to distill out as a vapor.In particular, since the solubility of the metal salt contained in the waste acid is high, and in a highly concentrated metal salt solution, the specific volatility of HCl is further increased, the distillation is carried out. HC in mother liquor remaining in the can
1 concentration is very low, and most of the HCl can be distilled and recovered. Also, in the case of nitric acid waste acid, HNO 3 is not as high as HCl, but has a relatively high specific volatility, and the solubility of metal salts is extremely high as in the case of hydrochloric acid.
O 3 can be distilled and collected.
【0005】しかしながら、塩酸系及び硝酸系廃酸にお
いて、蒸留法で処理回収し得るのは、当然のことながら
遊離酸のみであり、金属塩として存在する揮散性酸分の
回収は困難である。However, in the case of hydrochloric acid and nitric acid waste acids, only the free acid can be treated and recovered by the distillation method, and it is difficult to recover the volatile acid component existing as a metal salt.
【0006】またこのような廃酸は、イオン交換膜によ
る透析処理、例えば陰イオン交換膜(以下AMと記す)
を用いた拡散透析装置(以下DD装置と記す)やAMと
陽イオン交換膜(以下CMと記す)とを用いた電気透析
装置(以下ED装置と記す)などを用いて回収処理する
ことができる。[0006] Such waste acid is subjected to a dialysis treatment using an ion exchange membrane, for example, an anion exchange membrane (hereinafter referred to as AM).
Recovery treatment can be carried out using a diffusion dialysis device (hereinafter, referred to as DD device) using an electrodialysis device (hereinafter, referred to as ED device) using AM and a cation exchange membrane (hereinafter, referred to as CM). .
【0007】例えば硝酸によるアルミニウム箔のエッチ
ング廃酸は、遊離のHNO3 及びAl(NO3 )3 を含
む水溶液であり、これをDD装置により処理すれば、廃
酸中の遊離のHNO3 はAMを透過するので回収できる
が、Al(NO3 )3 中のNO3 1-分はHNO3 として
回収されないで、逆にAl(NO3 )3 として回収酸中
に一部混入する。これはAl(NO3 )3 の透析係数は
HNO3 の透析係数に比し小さいとはいえ数十分の一の
オーダーであり、混入を完全に阻止することはできない
からである。For example, the waste acid for etching aluminum foil with nitric acid is an aqueous solution containing free HNO 3 and Al (NO 3 ) 3 , and if this is treated with a DD device, the free HNO 3 in the waste acid is reduced to AM. can be recovered because it transmits, but Al (nO 3) nO 3 1- min 3 without being recovered as HNO 3, mixed partially in the recovered acid to reverse as Al (nO 3) 3. This is because although the dialysis coefficient of Al (NO 3 ) 3 is smaller than that of HNO 3 , it is only on the order of several tenths, and the contamination cannot be completely prevented.
【0008】又ED装置に於いてもHNO3 は、In an ED device, HNO 3 is
【0009】[0009]
【数1】 (Equation 1)
【0010】と電離しているので、H1+は陰極側へ、N
O3 1-は陽極側へ移動し、交互に接合されたCMとAM
の間を通過する清水側に透過してHNO3 として回収さ
れる。然るにAl(NO3 )3 塩の方は理論的にはH 1+ is transferred to the cathode side and N 1
O 3 1- moves to the anode side and alternately joined CM and AM
Permeates to the fresh water side that passes through the gap and is recovered as HNO 3 . However, Al (NO 3 ) 3 salt is theoretically
【0011】[0011]
【数2】 (Equation 2)
【0012】の如く電離するが、弱電解質であり、電離
度が小さいので殆ど大部分がAl(NO3 )3 のまま存
在しており、従ってHNO3 として回収されるのは当初
から存在する遊離のHNO3 が大部分でありAl(NO
3 )3 からのNO3 1-はHNO3 として殆ど回収されな
い。[0012] Although the ionization as a weak electrolyte, since ionization degree is small and most largely exist remains Al (NO 3) 3, thus being recovered as HNO 3 is initially present free Most of the HNO 3 is Al (NO
3) NO from 3 3 1 it is hardly recovered as HNO 3.
【0013】これを要するに、上記廃酸をDD装置やE
D装置を適用して処理回収した場合も蒸留法同様回収し
得るのは遊離の揮発性酸のみであり、金属塩として存在
するものは回収できないのみならず回収酸中には金属イ
オンがかなり同伴されるので、回収酸の純度が再使用に
支障を及ぼすなどの問題点があり、透析処理の利用に限
界がある。[0013] In short, the waste acid is converted to a DD device or E
In the case of treatment and recovery using the D apparatus, only the free volatile acid can be recovered in the same manner as in the distillation method, and not only those that are present as metal salts cannot be recovered, but also metal ions are considerably entrained in the recovered acid. Therefore, there is a problem that the purity of the recovered acid hinders reuse, and the use of dialysis treatment is limited.
【0014】因みに、本出願人等が先に提案した塩酸廃
液の回収処理法(例えば特公昭50−8719号公報参
照)によれば、金属塩として存在する塩酸分も回収する
ことが可能になるが、上記回収処理法では、廃塩酸を直
接蒸留缶に供給しここで硫酸添加により廃酸中の金属塩
を複分解させる構成になっているので、多量の硫酸塩が
生成し、またこの硫酸塩は結晶となって析出するために
固液分離する必要が生ずる。例えば、析出する硫酸塩が
1水塩の場合、固液分離時の脱液率は、分離手段にもよ
るが、通常15〜30重量%程度であり、硫酸分のロス
が大きく、実用的でない。本発明はこのような従来の問
題点を一層することを目的としてなされたものである。 Incidentally, the hydrochloric acid waste previously proposed by the present applicants has been proposed.
Liquid recovery treatment method (for example, see Japanese Patent Publication No. 50-8719)
According to the reference, the hydrochloric acid present as a metal salt is also recovered.
However, in the above recovery method, waste hydrochloric acid is directly
Metal salts in waste acid by feeding sulfuric acid to distillation vessel where sulfuric acid is added
, So that a large amount of sulfate
Is formed, and this sulfate is deposited as crystals.
The need for solid-liquid separation arises. For example, the sulfate that precipitates
In the case of monohydrate, the liquid removal rate during solid-liquid separation depends on the separation means.
However, it is usually about 15 to 30% by weight,
Is large and impractical. The present invention has been made to further solve such a conventional problem.
【0015】[0015]
【問題点を解決するための手段】本発明は、塩酸、硝酸
などのような揮発性酸並びにその金属塩を含む金属表面
処理廃酸の処理回収法であって、上記廃酸中に溶存する
金属に対し、反応当量を超える量の硫酸を添加して廃酸
中に溶存する金属塩を複分解しつつイオン交換膜により
透析処理することにより、該廃酸中より揮発性酸を回収
する一方、透析廃液は硫酸塩主体の溶液として回収する
工程、上記工程よりの回収酸中に硫酸を添加し、硫酸濃
度を25〜60%に維持しつつ蒸留処理することによ
り、該回収酸中より揮発性酸を留出回収する工程、及び
硫酸濃度が25〜60%の蒸留缶缶出液を金属塩複分解
のために、イオン交換膜により透析処理される廃酸中に
供給する工程、とを含むことを特徴とする金属表面処理
廃酸の処理回収法に係る。SUMMARY OF THE INVENTION The present invention relates to a method for treating and recovering a volatile acid such as hydrochloric acid or nitric acid and a metal surface treatment waste acid containing a metal salt thereof, wherein the waste acid is dissolved in the waste acid. For the metal, by adding an amount of sulfuric acid in excess of the reaction equivalent and dialyzing the metal salt dissolved in the waste acid with an ion exchange membrane while performing double decomposition, the volatile acid is recovered from the waste acid, A step of recovering the dialysis waste liquid as a sulfate-based solution, adding sulfuric acid to the recovered acid from the above step, and performing distillation while maintaining the sulfuric acid concentration at 25 to 60%, so that the recovered acid is more volatile than the recovered acid. A step of distilling and recovering an acid, and a step of supplying a bottom of a distillation still having a sulfuric acid concentration of 25 to 60% into waste acid which is subjected to dialysis treatment with an ion exchange membrane for metal salt metathesis. Treatment and recovery method of metal surface treatment waste acid characterized by That.
【0016】本発明により処理回収される金属表面処理
廃酸は、先に述べたように遊離の揮発性酸と、その金属
塩とを含んでいる。廃酸の種類としては塩酸系廃酸、硝
酸系廃酸及び之等の混酸系廃酸を例示でき、また之等の
揮発性酸と塩を形成する金属としては、鉄又はアルミニ
ウムを例示できる。尚アルミニウムのエッチング処理に
は、之等の揮発性酸に少量の硫酸を添加して用いる場合
があるが、本発明では下記に述べるように廃酸中に硫酸
を加えて処理するので、廃酸中に少量の遊離硫酸やその
金属塩が含まれていても特に問題はない。また廃酸によ
っては、まれではあるが遊離の揮発性酸を高濃度例えば
10%以上含む場合があるが、このような場合は、本発
明法により処理回収する前に、イオン交換膜による透析
手段例えばDD装置を適用して、遊離の揮発性酸の一部
を前もって回収してもよい。The metal surface treatment waste acid to be treated and recovered according to the present invention contains a free volatile acid and its metal salt as described above. Examples of the kind of the waste acid include hydrochloric acid-based waste acid, nitric acid-based waste acid, and mixed acid-based waste acid such as these, and examples of the metal that forms a salt with the volatile acid such as these include iron or aluminum. In addition, a small amount of sulfuric acid may be added to these volatile acids for the aluminum etching treatment. However, in the present invention, sulfuric acid is added to the waste acid as described below. There is no particular problem even if a small amount of free sulfuric acid or its metal salt is contained therein. In addition, depending on the waste acid, a rare volatile acid may be contained in a high concentration, for example, 10% or more. In such a case, the dialysis means using an ion exchange membrane is required before the treatment and recovery by the method of the present invention. For example, a DD device may be applied to recover some of the free volatile acid in advance.
【0017】本発明法を適用して上記廃酸を処理回収す
るに際しては、先ず上記廃酸中に、該廃酸中に溶存する
金属に対して反応当量より少し過剰となるように硫酸が
添加される。In treating and recovering the waste acid by applying the method of the present invention, first, sulfuric acid is added to the waste acid so that the amount of the metal dissolved in the waste acid is slightly larger than the reaction equivalent. Is done.
【0018】過剰の硫酸を添加し乍ら透析処理すること
により、廃酸中に溶存している金属塩は実質的に全てが
複分解し、硫酸塩と揮発性酸とに移行するのでイオン交
換膜による透析処理、例えばDD装置及び/又はED装
置の適用により処理することにより、廃酸中にもともと
遊離状態に存在していた揮発性酸はもとより、金属塩と
して存在していた揮発性酸分をもうまく回収できる。By performing dialysis while adding excess sulfuric acid, substantially all of the metal salts dissolved in the waste acid are metathesized and converted into sulfates and volatile acids. Dialysis treatment, for example, by applying a DD device and / or an ED device, the volatile acid originally existing in a free state in the waste acid as well as the volatile acid existing as a metal salt can be removed. Can be collected well.
【0019】例えば硝酸のアルミニウム箔エッチング廃
酸には、HNO3 及びAl(NO3)3 を含む水溶液が
あり、これにAlの反応当量より過剰のH2 SO4 を添
加すると、For example, nitric acid aluminum foil etching waste acid includes an aqueous solution containing HNO 3 and Al (NO 3 ) 3. When an excess of H 2 SO 4 is added to the reaction equivalent of Al,
【0020】[0020]
【数3】 (Equation 3)
【0021】の如く複分解し、HNO3 が遊離される。
これをDD装置により処理すると、生成HNO3 が直ち
にAMを通して透過されるため、過剰のH2 SO4 の存
在と相俟って本反応は右向きの反応が支配的な不可逆反
応となりもともとの遊離HNO3 はもとよりAl(NO
3 )3 塩中のNO3 1-もまたHNO3 として回収され
る。この際Al2 (SO4 )3 のうちの一部が、従来法
として述べたAl(NO3)3 の場合と同様に回収酸中
に透析し不純物として混入する。As described above, HNO 3 is liberated.
When this is processed by a DD apparatus, the generated HNO 3 is immediately permeated through the AM, and this reaction, combined with the presence of excess H 2 SO 4 , leads to an irreversible reaction in which the rightward reaction is dominant, and the original free HNO 3 3 as well as Al (NO
3) 3 NO in the salt 3 1 is also recovered as HNO 3. At this time, a part of Al 2 (SO 4 ) 3 is dialyzed into the recovered acid and mixed as impurities as in the case of Al (NO 3 ) 3 described as the conventional method.
【0022】またED装置に於てもH2 SO4 の添加に
より生成したHNO3 は直ちにIn an ED device, HNO 3 generated by the addition of H 2 SO 4 is immediately
【0023】[0023]
【数4】 (Equation 4)
【0024】に電離し、もともと存在していた遊離のH
NO3 と同様に、それぞれAMとCMを透過してHNO
3 として回収される。これにより上記(1)式の反応
は、右向きの反応が支配的な不可逆反応となり、Al
(NO3 )3 中のNO3 1-もまたHNO3 として回収さ
れる。これに反して添加H2 SO4 の過剰分は一応、To the free H which originally existed
Like NO 3 , HNO passes through AM and CM respectively.
Recovered as 3 . As a result, the reaction of the above formula (1) becomes an irreversible reaction in which the rightward reaction is dominant, and
NO 3 1− in (NO 3 ) 3 is also recovered as HNO 3 . On the contrary, the excess amount of added H 2 SO 4 is temporarily
【0025】[0025]
【数5】 (Equation 5)
【0026】の如く電離するが、SO4 イオンは同じ陰
イオンであり、NO3 1-に比して透析係数は小さいが少
量透析混入する。[0026] Although the ionization as, SO 4 ion is the same anion, dialysis coefficient compared to NO 3 1-small but a small amount dialysis contamination.
【0027】上記置換反応に用いる硫酸は余り過剰にな
りすぎると未反応のH2 SO4 の、回収酸への混入量が
増えるので、廃酸中の金属分例えばAl分に対し、1.
05〜1.40特に1.1〜1.2当量程度が適当であ
る。If the amount of sulfuric acid used in the above substitution reaction is too large, the amount of unreacted H 2 SO 4 mixed into the recovered acid increases.
It is suitably from about 0.5 to 1.40, particularly about 1.1 to 1.2 equivalents.
【0028】このように廃酸に対し、廃酸中に溶存する
金属に対し当量以上、好ましくは1.1〜1.2当量の
硫酸を添加し乍らDD装置及び/又はED装置にて処理
することにより廃酸中にもともと遊離状態で存在してい
た揮発性酸はもとより、金属と結合し金属塩となってい
た揮発性酸分をも殆んど大部分、回収することができ
る。As described above, sulfuric acid is added to the waste acid in an amount equal to or more than the equivalent of the metal dissolved in the waste acid, preferably 1.1 to 1.2 equivalents, and the treatment is performed in the DD apparatus and / or the ED apparatus. By doing so, it is possible to recover almost all the volatile acid originally present in the waste acid in a free state, as well as most of the volatile acid which has been bonded to the metal to form a metal salt.
【0029】一方透析廃液は、僅かのH2 SO4 並びに
揮発性酸分を含むが、硫酸塩主体の溶液であるので、例
えばアルミニウム系酸の場合はこれをさらに濃縮し凝集
剤として有用な液体硫酸バンド〔Al2 (SO4 )3 〕
として利用出来る。又鉄系廃酸の場合は、冷却晶析によ
りFeSO4 ・7H2 Oを副生させることにより、有効
利用できる。On the other hand, the dialysis waste liquid contains a small amount of H 2 SO 4 and a volatile acid component, but is a solution mainly composed of a sulfate. For example, in the case of an aluminum-based acid, it is further concentrated to obtain a liquid useful as a flocculant. Sulfuric acid band [Al 2 (SO 4 ) 3 ]
Available as In the case of an iron-based waste acid, FeSO 4 .7H 2 O can be effectively used by by-producing FeSO 4 .7H 2 O by cooling crystallization.
【0030】尚イオン交換膜の透析処理により回収され
た回収酸中には、先に述べたように、揮発性酸に加え少
量のSO4 2-や金属分などが含まれるので、これをその
まま再使用するには純度的に適当でない。よって本発明
では上記回収酸を蒸留により精製する。As described above, in addition to the volatile acid, the recovered acid recovered by the dialysis treatment of the ion exchange membrane contains a small amount of SO 4 2− and a metal component. It is not suitable in terms of purity for reuse. Therefore, in the present invention, the recovered acid is purified by distillation.
【0031】本発明において、回収酸の蒸留は、蒸留缶
内の硫酸濃度を25〜60%に維持しながら行なわれ
る。In the present invention, distillation of the recovered acid is performed while maintaining the sulfuric acid concentration in the distillation still at 25 to 60%.
【0032】図1はH2 O、H2 SO4 及びHNO3 を
含む3成分系の気液平衡線図を、また図2はH2 O、H
2 SO4 及びHClを含む3成分系の気液平衡線図をそ
れぞれ示している。[0032] Figure 1 is H 2 O, the gas-liquid equilibrium diagram of a three-component system containing H 2 SO 4 and HNO 3, and FIG. 2 H 2 O, H
The vapor-liquid equilibrium diagrams of the ternary system containing 2 SO 4 and HCl are shown respectively.
【0033】図1及び図2から明らかなように蒸留缶内
の硫酸濃度を25〜60%、好ましくは40〜50%に
維持しつつ回収酸の蒸留を行なうことにより、蒸留缶内
に残留する揮発性酸濃度を低く抑える一方、留出回収酸
濃度を高めつつ、蒸留処理を行なうことが可能になる。
ちなみに蒸留缶内の硫酸濃度が25%に達しない場合は
蒸留缶内に残留する揮散性酸の割合が高くなりまた60
%を上回ると、蒸留缶内で硫酸塩が多量に析出する等の
問題があり、いずれも好ましくない。As is clear from FIGS. 1 and 2, the recovered acid is distilled while maintaining the sulfuric acid concentration in the distillation can at 25 to 60%, preferably 40 to 50%, so that it remains in the distillation can. The distillation treatment can be performed while the concentration of the volatile acid is kept low while the concentration of the distillate recovered acid is increased.
By the way, when the sulfuric acid concentration in the distillation still does not reach 25%, the ratio of volatile acid remaining in the distillation can becomes high, and 60%.
%, There is a problem that a large amount of sulfate precipitates in the distillation still, and neither is preferable.
【0034】このようにイオン交換膜による透析により
回収した回収酸を、蒸留缶内の硫酸濃度を25〜60%
に維持しつつ蒸留することにより、高純度、高濃度の揮
発性酸を留出回収できる。The recovered acid recovered by the dialysis with the ion exchange membrane is subjected to a sulfuric acid concentration of 25-60% in the distillation still.
By performing distillation while maintaining the pH, volatile acids having high purity and high concentration can be distilled and recovered.
【0035】蒸留缶内の母液は硫酸塩の外に多量の遊離
硫酸も含むので、その一部が、イオン交換膜による透析
処理を受ける前の廃酸中に供給され、該廃酸中の金属塩
を複分解するための硫酸として利用され、又これにより
蒸留缶内における硫酸塩の蓄積を防止する効果が得られ
る。尚添加硫酸は硫酸塩の生成に消費されるので、これ
に見合う当量以上の硫酸は新硫酸として補給することが
必要である。Since the mother liquor in the distillation still contains a large amount of free sulfuric acid in addition to the sulfate, a part of the mother liquor is supplied to the waste acid before being subjected to the dialysis treatment by the ion exchange membrane, and the metal in the waste acid is supplied. It is used as sulfuric acid for metathetically decomposing the salt, and this has the effect of preventing the accumulation of sulfate in the distillation still. Since the added sulfuric acid is consumed for the production of sulfate, it is necessary to supply sulfuric acid in an equivalent amount or more as fresh sulfuric acid.
【0036】本発明処理回収法において、硫酸は、蒸留
缶内を所定の硫酸濃度に維持し、高濃度の揮発性酸を留
出させるために利用された後、廃酸と共にイオン交換膜
透析装置中に送られ、該廃酸中の金属塩を複分解し、遊
離揮発性酸と、利用価値の高い硫酸塩を生成させるため
に利用される。In the treatment and recovery method of the present invention, sulfuric acid is used to maintain a predetermined concentration of sulfuric acid in the distillation vessel and to distill out a high concentration of volatile acid, and then, together with the waste acid, an ion exchange membrane dialysis apparatus. And is used to metathesize the metal salts in the waste acid to produce free volatile acids and valuable sulphates.
【0037】以下に実施例を掲げる。Examples will be described below.
【0038】[0038]
【実施例】図3に示すフロー図にもとづき、本発明法を
実施した。その結果を示すと、表1及び表2の通りであ
る。尚表1は塩酸系廃酸の場合を、また表2は硝酸系廃
酸の場合をそれぞれ示している。また図3中、各ライン
の要所に(1)〜(9)の符号が入れられ、各要所の液
量及び液組成は、表1及び表2の通りである。EXAMPLE The method of the present invention was carried out based on the flowchart shown in FIG. Tables 1 and 2 show the results. Table 1 shows the case of hydrochloric acid waste acid, and Table 2 shows the case of nitric acid waste acid. In FIG. 3, symbols (1) to (9) are assigned to key points of each line, and the liquid amount and liquid composition of each key point are as shown in Tables 1 and 2.
【0039】[0039]
【表1】 [Table 1]
【0040】[0040]
【表2】 [Table 2]
【0041】本発明処理回収法によれば、表1から明ら
かなように18%のT・HClを含む塩酸系廃酸1,2
00Kg/hから13.3%の高純度塩酸1524Kg/hを回
収できる。According to the treatment and recovery method of the present invention, as is apparent from Table 1, the hydrochloric acid-based waste acid 1 and 18 containing 18% of T.HCl was used.
1524 kg / h of high-purity hydrochloric acid of 13.3% from 00 kg / h can be recovered.
【0042】また表2から明らかなように、10.2%
のT・HNO3 を含む硝酸系廃酸931Kg/hから7.5
%の高純度硝酸1065.5Kg/hを回収できる。As apparent from Table 2, 10.2%
From 931 kg / h of nitric acid waste acid containing T.HNO 3 to 7.5
% High-purity nitric acid 1065.5 kg / h can be recovered.
【0043】[0043]
【発明の効果】本発明回収処理法によれば、金属表面処
理廃液中に含まれる揮発性酸を遊離のものはもとより、
金属と結合して金属塩になっている揮発性酸分を含めも
てその大部分を高純度揮発性酸とそして有効に回収でき
ると共に、廃酸中に溶存している金属、例えばAl,Fe
などは利用価値の高い硫酸塩の状態で回収することが可
能になる。更に、廃酸中に溶存する金属は、硫酸添加に
よる金属塩の複分解後に、透析処理により硫酸塩を主体
とする溶液(透析廃液)として別途に回収する構成にな
っているので、蒸留工程は実質的に硫酸塩を含まない状
態で行うことができ、硫酸塩を析出させることなしに、
従って固液分離工程の必要性なしに、金属表面処理廃液
から高純度揮発性酸を回収できる。 According to the present invention, the volatile acid contained in the metal surface treatment waste liquid is released,
Most of the metals, including volatile acids that are combined with metals to form metal salts, can be effectively recovered with high-purity volatile acids, and metals dissolved in waste acids, for example, Al, Fe
And the like can be recovered in the form of sulfate having high utility value. Furthermore, metals dissolved in waste acid can be added to sulfuric acid.
Sulphate mainly by dialysis treatment
Separately collected as a solution (dialysis waste liquid)
The distillation process is substantially free of sulfates
Can be carried out in a state, without depositing sulfate
Therefore, metal surface treatment wastewater is eliminated without the need for a solid-liquid separation process.
, High-purity volatile acid can be recovered.
【図1】HNO3 を含む3成分系の気液平衡線図であ
る。FIG. 1 is a vapor-liquid equilibrium diagram of a ternary system containing HNO 3 .
【図2】HClを含む3成分系の気液平衡線図である。FIG. 2 is a vapor-liquid equilibrium diagram of a ternary system containing HCl.
【図3】本発明の1実施状況を概略的に示すフロー図で
ある。FIG. 3 is a flowchart schematically showing one embodiment of the present invention.
───────────────────────────────────────────────────── フロントページの続き (72)発明者 壁谷 進自 大阪府門真市大字門真1006番地 松下電 器産業株式会社内 (72)発明者 神崎 信義 大阪府門真市大字門真1006番地 松下電 器産業株式会社内 (56)参考文献 特公 昭50−8719(JP,B1) (58)調査した分野(Int.Cl.6,DB名) C23G 1/36 C23F 1/16 C23F 1/46 C23G 1/02 ──────────────────────────────────────────────────の Continued on the front page (72) Inventor Susumu Kamiya, 1006 Kadoma Kadoma, Osaka Prefecture Inside Matsushita Electric Industrial Co., Ltd. (72) Inventor Nobuyoshi Kanzaki 1006 Odaka Kadoma, Kadoma City Osaka In-house (56) References JP 50-8719 (JP, B1) (58) Fields investigated (Int. Cl. 6 , DB name) C23G 1/36 C23F 1/16 C23F 1/46 C23G 1/02
Claims (1)
その金属塩を含む金属表面処理廃酸の処理回収法であっ
て、上記廃酸中に溶存する金属に対し、反応当量を超え
る量の硫酸を添加して廃酸中に溶存する金属塩を複分解
しつつイオン交換膜により透析処理することにより、該
廃酸中より揮発性酸を回収する一方、透析廃液は硫酸塩
主体の溶液として回収する工程、上記工程よりの回収酸
中に硫酸を添加し、硫酸濃度を25〜60%に維持しつ
つ蒸留処理することにより、該回収酸中より揮発性酸を
留出回収する工程、及び硫酸濃度が25〜60%の蒸留
缶缶出液を金属塩複分解のために、イオン交換膜により
透析処理される廃酸中に供給する工程、とを含むことを
特徴とする金属表面処理廃酸の処理回収法。1. A method for treating and recovering a volatile acid such as hydrochloric acid, nitric acid and the like and a metal surface treatment waste acid containing a metal salt thereof, wherein the amount of the metal exceeds the reaction equivalent with respect to the metal dissolved in the waste acid. The sulfuric acid is added and the metal salt dissolved in the waste acid is double-decomposed and dialyzed by an ion exchange membrane to recover the volatile acid from the waste acid. A recovering step, a step of distilling and recovering a volatile acid from the recovered acid by adding sulfuric acid to the recovered acid from the above step, and performing a distillation treatment while maintaining the sulfuric acid concentration at 25 to 60%; and Supplying the distillate bottoms having a sulfuric acid concentration of 25 to 60% into waste acid dialyzed by an ion exchange membrane for metal salt metathesis. Treatment collection method.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4325290A JP2949545B2 (en) | 1992-12-04 | 1992-12-04 | Treatment and recovery of metal surface treatment waste acid |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP4325290A JP2949545B2 (en) | 1992-12-04 | 1992-12-04 | Treatment and recovery of metal surface treatment waste acid |
Publications (2)
Publication Number | Publication Date |
---|---|
JPH06173048A JPH06173048A (en) | 1994-06-21 |
JP2949545B2 true JP2949545B2 (en) | 1999-09-13 |
Family
ID=18175167
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Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP4325290A Expired - Lifetime JP2949545B2 (en) | 1992-12-04 | 1992-12-04 | Treatment and recovery of metal surface treatment waste acid |
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JP (1) | JP2949545B2 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102409343A (en) * | 2010-09-24 | 2012-04-11 | 比亚迪股份有限公司 | Regeneration method of waste acid in polysilicon texturing process and waste acid regeneration system |
Families Citing this family (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
KR100613257B1 (en) * | 2001-12-22 | 2006-09-25 | 재단법인 포항산업과학연구원 | Recycling method of waste acid etching solution |
KR101009026B1 (en) * | 2005-12-26 | 2011-01-17 | 대일개발 주식회사 | Method for recovering acid from mixed waste acid occupied in preparing process of liquid crystal display |
KR101382646B1 (en) * | 2008-01-29 | 2014-04-10 | 재단법인 포항산업과학연구원 | Method for recovering acid from mixed waste acid by using solvent extraction method and vacuum evaporation |
CN102828192A (en) * | 2012-08-29 | 2012-12-19 | 南京化工职业技术学院 | Resourceful treatment method for pickling waste liquor in steel industry |
-
1992
- 1992-12-04 JP JP4325290A patent/JP2949545B2/en not_active Expired - Lifetime
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN102409343A (en) * | 2010-09-24 | 2012-04-11 | 比亚迪股份有限公司 | Regeneration method of waste acid in polysilicon texturing process and waste acid regeneration system |
CN102409343B (en) * | 2010-09-24 | 2013-08-21 | 比亚迪股份有限公司 | Regeneration method of waste acid in polysilicon texturing process and waste acid regeneration system |
Also Published As
Publication number | Publication date |
---|---|
JPH06173048A (en) | 1994-06-21 |
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