JPS585989B2 - Yukiyo Bio-Site FE - Google Patents
Yukiyo Bio-Site FEInfo
- Publication number
- JPS585989B2 JPS585989B2 JP50089433A JP8943375A JPS585989B2 JP S585989 B2 JPS585989 B2 JP S585989B2 JP 50089433 A JP50089433 A JP 50089433A JP 8943375 A JP8943375 A JP 8943375A JP S585989 B2 JPS585989 B2 JP S585989B2
- Authority
- JP
- Japan
- Prior art keywords
- ions
- acid
- organic solvent
- extracted
- organic phase
- 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
Links
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
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D11/00—Solvent extraction
- B01D11/04—Solvent extraction of solutions which are liquid
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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)
- Extraction Or Liquid Replacement (AREA)
- Cleaning And De-Greasing Of Metallic Materials By Chemical Methods (AREA)
- Processing Of Solid Wastes (AREA)
Description
【発明の詳細な説明】
金属製錬の過程、或いは金属製品の酸洗に使用された重
金属イオンを多量1こ含有する廃酸よりFeイオンを除
く方法としで、NaCaNH塩を尋加して、該越波のP
Hを調節し、水酸化物の形で重金属イオンを除く方法が
従来より採用されでおり、そしてこの方法lこおける中
和により生成するNa25o、、Ca5o4.(NH4
)2804等を副製品として販売或いは棄却しでいた。[Detailed Description of the Invention] As a method for removing Fe ions from waste acid containing a large amount of heavy metal ions used in the process of metal smelting or pickling of metal products, NaCaNH salt is added to the waste acid. P of the overtopping wave
Conventionally, a method has been adopted in which H is adjusted and heavy metal ions are removed in the form of hydroxide, and Na25o, Ca5o4. (NH4
)2804 etc. were sold as by-products or discarded.
しかるに、各方面で公害処理が進むにつれで上記した副
製品が多くなって、市場性がなくなり。However, as pollution treatment advances in various fields, the above-mentioned by-products increase and become unmarketable.
販売が困難になった。Sales became difficult.
又、棄却するにも費用が嵩むことや、二次公害の発生防
止面から著しく困難になった。In addition, it has become extremely difficult to reject the project due to the high cost and prevention of secondary pollution.
HNO3廃液の場合は、中和によってNO3イオンを除
くことができず、この廃水は富養化廃水として問題があ
り、特に瀬戸内海や湖に接する地域では、Nイオンに対
する規制が必要である。In the case of HNO3 waste liquid, NO3 ions cannot be removed by neutralization, and this wastewater poses a problem as enriched wastewater, and regulations regarding N ions are required, especially in areas bordering the Seto Inland Sea or lakes.
又、PH調節に使用する薬品が、エネルギーコストの上
昇や製法転換などから高騰し、費用が極めて嵩むという
欠点を有している。In addition, the cost of chemicals used for pH adjustment has skyrocketed due to rising energy costs and changes in manufacturing methods, resulting in extremely high costs.
又、該溶液を真空濃縮や冷却濃縮により、含有する金層
イオンを塩の形1例えばFeS。Further, the solution is concentrated in vacuum or concentrated by cooling to remove the gold layer ions contained in the salt form 1, for example, FeS.
7H20の如き結晶で増出すことにより、廃酸中の金」
オンを低下させる方法があるが、これら副生ずる結晶の
処理を経済的に行なうことができないという欠点を有し
、更に濃縮に要するエネルギーを多く要し、経済性に欠
けるものである。Gold in waste acid is increased by crystals such as 7H20.
Although there is a method of lowering the on, it has the drawback that the by-product crystals cannot be treated economically, and furthermore, it requires a lot of energy for concentration, making it uneconomical.
更に、溶媒抽出法として、特公昭47− 49995のものがある。Furthermore, as a solvent extraction method, There are 49,995 items.
この方法によると、有機溶媒としでケトン類或いはエー
テル類を使用してFe3+イオンを抽出する方法である
が、使用する溶媒の酸或いは水に対する溶解度が高く1
例えば、MIBKの場合、20.000PPM程度溶解
することから、経済性に乏しく、エーテルにいたつでは
、も早や工業的ではないという欠点を有している。According to this method, Fe3+ ions are extracted using ketones or ethers as an organic solvent.
For example, in the case of MIBK, it dissolves at about 20,000 PPM, so it is not economical, and when used in ether, it has the disadvantage that it is no longer suitable for industrial use.
更に又、廃酸を直接電解室へ導き、電解によりFeを金
属鉄として回収すると共に、ClS。Furthermore, the waste acid is directly led to an electrolytic chamber, and Fe is recovered as metallic iron by electrolysis, and ClS is recovered.
イオン等を隔膜にて仕切られた他室へ移動させて酸を回
収する方法としては、隔膜にイオン選択性膜(カチオン
或いはアニオン)や多種の微孔膜による方法が発表され
ているが、何れも、廃酸を直妾電解するために酸度が高
いこと、金属イオンが電解の進行に従い低下し、効率が
低下するこさ。Methods using ion-selective membranes (cation or anion) or various types of microporous membranes as diaphragms have been announced as methods for recovering acid by moving ions, etc. to another chamber separated by a diaphragm, but none of them are effective. Also, the acidity is high because the waste acid is directly electrolyzed, and the metal ions decrease as the electrolysis progresses, reducing efficiency.
電解に適した液条件1こできないこと、他の電解質の添
加ができないこと、Fe以外の金属イオンも電着して、
高純度の電解質が得られず、付加価イvが低下する等の
欠点を有している。Liquid conditions suitable for electrolysis cannot be achieved, other electrolytes cannot be added, metal ions other than Fe can also be electrodeposited,
It has drawbacks such as not being able to obtain a highly pure electrolyte and lowering the added value (iv).
なお、電解前に拡散透析膜を通過させることにより、遊
離酸の一部を電解前に他室へ移動させ。In addition, by passing through a diffusion dialysis membrane before electrolysis, a part of the free acid is moved to another chamber before electrolysis.
或いは電気透析により遊離酸を極力他室へ移動させるよ
うにして、前記した欠点を克服せんとしでいるが、電解
の進行により電解質が低下して動源が低下すること、或
いは金属イオンを余り低下しない範囲で酸回収を行なう
ために大容量の液を彷環しなければならないという欠点
がある。Alternatively, attempts have been made to overcome the above-mentioned drawbacks by moving the free acid to another chamber as much as possible by electrodialysis, but as the electrolysis progresses, the electrolyte decreases and the power source decreases, or the metal ions decrease too much. The drawback is that a large volume of liquid must be circulated in order to recover the acid to the extent that it does not.
しかして1本件出願の発明者に係る特開昭48−213
59.或いは特願昭50−31550のものにおいて、
アルキル燐酸等を含有する有機溶媒Aを使用しで、該溶
液中のFeイオンを抽出しその有機相よりの剥離にHC
lを使用し、その剥離液中のFeイオン濃度を高めるこ
とができず。However, Japanese Patent Application Laid-open No. 48-213 related to the inventor of the present application
59. Or in the patent application filed in 1983-31550,
Fe ions in the solution are extracted using organic solvent A containing alkyl phosphoric acid, etc., and HC is used to remove Fe ions from the organic phase.
It was not possible to increase the Fe ion concentration in the stripping solution.
このために、第1級〜第4級アミン或いは燐酸エステル
類を含有する有機溶媒Bを接触させることにより、濃厚
なFe含有塩化物溶液を得ることか可能となり、この溶
液を加熱分解してFe酸化物とHClを回収するために
要するエネルギーを軽減する方法がある。For this purpose, by bringing into contact organic solvent B containing primary to quaternary amines or phosphoric acid esters, it is possible to obtain a concentrated Fe-containing chloride solution, and this solution is thermally decomposed to release Fe. There are ways to reduce the energy required to recover oxides and HCl.
塩化物溶液の加熱分解法は。小容量の場合設備費が嵩む
ために実施が困難である。What is the thermal decomposition method of chloride solution? In the case of small capacity, it is difficult to implement due to high equipment costs.
又、高温部分に塩化物溶液を噴霧する方法であるために
、腐食しで、安定操業の長期継続は不可能であるという
欠点がある。Furthermore, since the method involves spraying a chloride solution onto high-temperature areas, there is a drawback in that it is corrosive and stable operation cannot be continued for a long period of time.
本発明は、これら従来法の欠点を克服するためになされ
たものである。The present invention has been made to overcome the drawbacks of these conventional methods.
しかして、その要旨とするところは、Fe”イオンを多
量に含有する廃酸に、アルキル燐酸を石油系炭化水素に
て稀釈された有機溶媒1例えばD2BHPA(ジー2−
エチルヘキシル燐酸)を含む有機溶媒を接触させること
により、該溶液中のFe3+イオンを有機相へ抽出する
ことにより酸を再生させる工程、一方、有機相に抽出さ
れたFeイオンは、Na25o3.NaH8o3.So
2.ヒドラジン化合物、Na2S、NaC1或いは還元
性物質(ガス状のもの)をバブリングする水溶液と接触
させることにより、有機相中のFe3+イオンを還元さ
せることによって、剥離を容易にした後。The gist of this is that organic solvent 1, such as D2BHPA (D2-2-
A step of regenerating the acid by extracting Fe3+ ions in the solution into an organic phase by contacting an organic solvent containing Na25o3. NaH8o3. So
2. After facilitating stripping by reducing Fe3+ ions in the organic phase by contacting with an aqueous solution bubbling a hydrazine compound, Na2S, NaCl or a reducing substance (in gaseous form).
HCl、H2SO4等の鉱酸と接触させることにより。By contacting with mineral acids such as HCl, H2SO4.
Feイオンを水相へ剥離することにある。The objective is to exfoliate Fe ions into the aqueous phase.
次に1本発明の詳細を添付図面をこ基すき説明する。Next, details of the present invention will be explained with reference to the accompanying drawings.
第1図はその実施方法の一例を示すものである。FIG. 1 shows an example of the implementation method.
Fe3+イオンを多量に含有する廃酸を、Fe抽出工程
に導き、アルキル燐酸を含有する有機溶媒と接触させる
と、水溶液中のFe3+イオンは次式に示すように、有
機相に抽出され、酸は回収される。When the waste acid containing a large amount of Fe3+ ions is introduced into the Fe extraction step and brought into contact with an organic solvent containing alkyl phosphoric acid, the Fe3+ ions in the aqueous solution are extracted into the organic phase as shown in the following equation, and the acid is It will be collected.
Fe”、、、+3R−H+:R3Fej3H+R−Hは
H型交換基を有する有機溶媒。Fe",,, +3R-H+: R3Fej3H+R-H is an organic solvent having an H-type exchange group.
強酸領域でFe3+イオンを抽出可能であることは、第
4図において1回の接触で、Fe3+イオンが有機相へ
抽出される割合とPHの関係を示すように、Fe2+イ
オンは抽出できないが。The fact that Fe3+ ions can be extracted in a strong acid region is shown in Figure 4, which shows the relationship between the ratio of Fe3+ ions being extracted into the organic phase and the pH in one contact, although Fe2+ ions cannot be extracted.
Fe”+イオンでは、よく抽出できることを示しでいる
。This shows that Fe''+ ions can be extracted well.
又、抽出剤にD2EHPA(ジー2−エチルヘキシル燐
酸)を使用して、Fe3+イオンを抽出した時の平衡曲
線を第2図に示す。FIG. 2 shows an equilibrium curve when Fe3+ ions are extracted using D2EHPA (di-2-ethylhexyl phosphoric acid) as an extractant.
次に、有機相に抽出されたFe3+イオンは。Next, the Fe3+ ions extracted into the organic phase.
抽出条件より更にHイオン濃度の高い鉱酸と接触させる
ことにより1次式に示すように、有機相より水相へ剥離
される。By contacting with a mineral acid having a higher H ion concentration than the extraction conditions, it is exfoliated from the organic phase to the aqueous phase as shown in the linear equation.
R3’Fe+3H(J’;3R−H+FeC#315%
HClによる剥離平衡曲線を第3図の〇−−〇線で示す
。R3'Fe+3H(J';3R-H+FeC#315%
The peeling equilibrium curve due to HCl is shown by the line ○--○ in FIG.
同図に示されるように、剥離液のFeイオン濃度を更に
高くするためには、剥離に使用する鉱酸は、更にH+イ
オン濃度の高いものが必要となり、経済性が失われる。As shown in the figure, in order to further increase the Fe ion concentration of the stripping solution, the mineral acid used for stripping must have an even higher H+ ion concentration, which results in loss of economic efficiency.
本発明は、有機相のFe3+イオンを剥離する前に、還
元性物質1例えば、ヒドラジン化合物。In the present invention, before stripping off Fe3+ ions in the organic phase, a reducing substance 1, for example, a hydrazine compound is added.
NaH8o3.Na25o3.NaNO2を含有する水
溶液、或いはSo2ガス等の還元ガスをバブリングする
水溶液を接触させることにより、有機相のFeイオンの
原子価を変換する。NaH8o3. Na25o3. By contacting with an aqueous solution containing NaNO2 or an aqueous solution bubbling a reducing gas such as So2 gas, the valence of Fe ions in the organic phase is changed.
次に、HCIやH2So4の鉱酸と接触させると容易に
水相へ剥離できるし、剥離液中のFeイオン濃度を高め
ることができる。Next, when brought into contact with a mineral acid such as HCI or H2So4, it can be easily stripped to the aqueous phase and the Fe ion concentration in the stripping solution can be increased.
第3図のX−X線で示される平衡曲線は還元性物質とし
てNa25o3を含有する水溶液と接触させた後、15
%H(J’と接触させた時のもので。The equilibrium curve shown by the X-X line in FIG.
%H (when in contact with J'.
同図の○−−0線に比較して、非常にFe濃度を高くす
ることが可能であることが理解される。It is understood that it is possible to make the Fe concentration extremely high compared to the ◯--0 line in the figure.
又、第4図の、PHと抽出率の関係で示されるように、
Fe2+イオンになると、PHが4以上の水溶液(H+
イオン濃度の低い水溶液)で抽出可能であることが判る
ように、逆に、PH4以下の水溶液では、有機相より水
相へ剥離できることを示すもので、有機相のFeイオン
を剥離するために、濃度の低い鉱酸で済み1本願方法は
従来法に比較しη経済性のあることが理解できるもので
ある。Also, as shown in the relationship between PH and extraction rate in Figure 4,
When Fe2+ ions become
As can be seen, it can be extracted with an aqueous solution with a low ion concentration (aqueous solution with a low ion concentration), and conversely, with an aqueous solution with a pH of 4 or less, it is possible to exfoliate from the organic phase to the aqueous phase.In order to exfoliate Fe ions in the organic phase, It can be seen that the method of the present invention is more economical than the conventional method since only a low concentration of mineral acid is required.
次に1本発明において使用される抽出剤は1次に示す群
から選択される。Next, the extractant used in the present invention is selected from the group shown below.
Rはアルキル基を示し、各群とも、一般にアルキル基の
炭素数が4〜18のものが使用される。R represents an alkyl group, and in each group, an alkyl group having 4 to 18 carbon atoms is generally used.
炭素数8のものとしで、D2EHPA(ジー2−エチル
ヘキシル燐酸)がある。One with 8 carbon atoms is D2EHPA (di-2-ethylhexyl phosphoric acid).
代表的なものとして、0PPA(オクチルピロ燐酸)が
ある。A typical example is 0PPA (octyl pyrophosphoric acid).
もよく知られる。is also well known.
又1本発明で使用される石油系炭化水素の稀釈剤は、芳
香族系炭化水素、或いは脂肪族系炭化水素が使用され、
もちろん、これらの混合品も使用でき、又、ケロシンの
如き雑多な石油系炭化水素の混合品も当然使用するもの
である。In addition, the petroleum hydrocarbon diluent used in the present invention is an aromatic hydrocarbon or an aliphatic hydrocarbon,
Of course, mixtures of these can also be used, and of course mixtures of miscellaneous petroleum hydrocarbons such as kerosene can also be used.
更に又、使用する有機溶媒の濃度は、対象廃酸中の物質
の濃度や、共存する他の酸の量によって決定されるが、
一般に2−75%(容積比)に調節する。Furthermore, the concentration of the organic solvent used is determined by the concentration of the substance in the target waste acid and the amount of other acids coexisting.
Generally, it is adjusted to 2-75% (volume ratio).
そし′て次に1本発明においで使用する還元性物質とし
では、N2H4をはじめとするヒドラジン化合物、Na
25o3.Na25o3.Na2S等で代表されるもの
であり、それらのガス状のもの(SO2等)が使用され
る。Next, the reducing substances used in the present invention include hydrazine compounds such as N2H4, Na
25o3. Na25o3. It is typified by Na2S and the like, and their gaseous forms (SO2, etc.) are used.
本発明を実施した場合1次のような利点がある。When the present invention is implemented, there are the following advantages.
(1)従来から経済的に処理困難とされCいた硫酸鉄を
処理し、金属鉄、酸化鉄と硫酸を経済的に回収すること
が可能となる。(1) It becomes possible to process iron sulfate, which has traditionally been considered economically difficult to process, and economically recover metallic iron, iron oxide, and sulfuric acid.
(2)従来から発表されCいる。(2) C has been announced for some time.
廃酸を直接電解して得る方法と異なり、C12ガス等の
二次公害を発生させることなく、純度の高い金属鉄や酸
化鉄と、Feイオンを全く含有しない回収酸を得ること
が可能となる。Unlike the method of obtaining waste acid by directly electrolyzing it, it is possible to obtain highly pure metallic iron and iron oxide and recovered acid that does not contain any Fe ions, without generating secondary pollution such as C12 gas. .
(3)大容量の設備はもちろん、小容量の廃酸を処理す
る装置も経済性が高いために、各所の酸洗個所でクロー
ズサーキットを形成することができる。(3) Not only large-capacity equipment but also equipment for treating small-volume waste acid is highly economical, so closed circuits can be formed at various pickling locations.
次に1本発明の実施例を挙げるが2本発明はこれに限定
されるものではない。Next, an example of the present invention will be described, but the present invention is not limited thereto.
実施例1 ステンレス鋼の酸洗に使用された。Example 1 Used for pickling stainless steel.
Feイオンを多量に含有する次に示す分析結果の廃酸を
実施試験に使用した。A waste acid containing a large amount of Fe ions and having the following analysis results was used in the practical test.
(単位9/13)アルキル燐酸1例えばD2EHPA(
前出)を含む有機溶媒と接触させることにより1次の式
で示すように、有機相へFe3+イオンを抽出する。(Unit 9/13) Alkyl phosphoric acid 1 e.g. D2EHPA (
As shown by the first-order equation, Fe3+ ions are extracted into the organic phase by contacting with an organic solvent containing (above).
金属イオンの大部分であるFe3+イオンを抽出すると
、酸は再生回収されることになる。When Fe3+ ions, which are the majority of metal ions, are extracted, the acid will be regenerated and recovered.
50%D2EHPA(前出)をケロシンで稀釈した有機
溶媒によるFe3+イオンの抽出平衡曲線を第2図に示
す。FIG. 2 shows an equilibrium curve for extracting Fe3+ ions using an organic solvent obtained by diluting 50% D2EHPA (described above) with kerosene.
有機相舎こ抽出されたFe3+イオンは、HCl又はH
2So4と接触させることにより1次式で示されるよう
に、有機相より剥離され、有機溶媒は再生される。The Fe3+ ions extracted from the organic phase filter are treated with HCl or H
By contacting with 2So4, it is stripped from the organic phase and the organic solvent is regenerated, as shown by the linear equation.
Fe3+イオンの剥離の前に有機相中のFeイオンを弱
還元させることにより、Feイオンの剥離が容易になる
ことを発見した。It has been discovered that the Fe ions can be easily stripped by weakly reducing the Fe ions in the organic phase before stripping the Fe3+ ions.
これは、第4図に示すように、Fe2+イオンはPHの
高い領域でないと抽出されないことからも証明されるも
のである。This is evidenced by the fact that Fe2+ ions are not extracted unless the pH is high, as shown in FIG.
還元性を有する溶液と剥離工程前に接触させることによ
り、その効果を得ることができる。This effect can be obtained by bringing it into contact with a reducing solution before the stripping step.
還元性溶液としでは、NaH803,ヒドラジン化合物
。Examples of reducing solutions include NaH803 and hydrazine compounds.
−Na2So4を添加したり、So2ガス等をバブリン
グすることにより1弱還元液をつくり、使用することが
できる。- By adding Na2So4 or bubbling So2 gas, etc., a weakly reduced solution can be made and used.
次Qこ、50%D2EHPA(前出)をケロシンで稀釈
した有機相に、23.94.!li!/1Fe3+イオ
ンを抽出させたものを使用し、150El/1Hclで
剥離する前に、各還元性溶液と接触させた。Next, add 50% D2EHPA (described above) to the organic phase diluted with kerosene at 23.94%. ! li! /1 Fe3+ ions were extracted and brought into contact with each reducing solution before stripping with 150 El/1 Hcl.
それを表(1)に示す。It is shown in Table (1).
実施例2
金属材料の酸洗に使用された廃硫酸の分析結果を実施試
験に使用した。Example 2 The analysis results of waste sulfuric acid used for pickling metal materials were used in practical tests.
上記した廃酸(1)、廃酸(2)に、Fe2+イオンの
酸化を目的とl、r、40%HNO3を0.11/1.
01廃酸の割合で添加して、Fe2+イオンをFe3+
イオンに変換した後、アルキル燐酸1例えばD2BHP
A(前出)を含む有機溶媒と接触させ。To the above-mentioned waste acids (1) and (2), l, r, 40% HNO3 was added in a ratio of 0.11/1 for the purpose of oxidizing Fe2+ ions.
01 waste acid to convert Fe2+ ion to Fe3+
After conversion into ions, alkyl phosphates 1 such as D2BHP
Contact with an organic solvent containing A (described above).
Fe3+イオンを抽出し、硫酸を再生した。Fe3+ ions were extracted and sulfuric acid was regenerated.
Fe3+イオンの連続抽出実施試験。Continuous extraction test of Fe3+ ions.
実施試験に使用したミキサーセトラー抽出装置は、巾1
00〜×長500XX高180%、ミキサーはポンプサ
クション型で1回転数を180〜310r−p−mの範
囲で1分相、界面高さを制御するために変化させた。The mixer-settler extractor used in the practical test has a width of 1
The mixer was a pump suction type mixer, and the number of revolutions was varied in the range of 180 to 310 rpm to control the phase separation and interface height.
水相、有機相は、定量ポンプを使用して一定量供給され
た。The aqueous phase and organic phase were supplied in fixed amounts using metering pumps.
装置名(1)(2)共、10段ミキサーセトラー。Equipment names (1) and (2) are both 10-stage mixer settlers.
ツ 備考−50%D2EHPA。tsu Notes - 50% D2EHPA.
註・・・入口水相のH2SO4濃度は、40%HNO3
の添加のために変化したもの。Note: H2SO4 concentration in the inlet aqueous phase is 40%HNO3
changed due to the addition of
洗浄液との接触実験は、水相1を1.5MNaCl+0
.1.MNa2So3溶液と接触さiた。In the contact experiment with the cleaning liquid, the aqueous phase 1 was mixed with 1.5M NaCl+0
.. 1. It was contacted with MNa2So3 solution.
水相2は指触させず。Do not touch water phase 2.
なお、洗浄液の管理は、PHと電位とによりなされる。Note that the cleaning liquid is managed by pH and potential.
連続実施試験では、0/A=1.0/1.0にて。In the continuous test, 0/A=1.0/1.0.
5段ミキサーセトラー抽出装置によつで有機相中のFe
の原子価を変化させた。Fe in the organic phase was removed by a five-stage mixer-settler extractor.
changed the valence of
連続剥離実施試験
実施試験に使用した装置は、連続抽出実施試験に使用し
たものと同一であるため省略する。Continuous Peeling Test The equipment used for the test is the same as the one used for the continuous extraction test, so it will be omitted.
上記した多くの特徴を有する本発明は、廃酸の排出個所
に、既設酸洗ライン等に容易に併設できて、しかも容量
に関係なく、経済的なりローズドサーキットを設けるこ
とを可能とした。The present invention, which has many of the features described above, makes it possible to provide an economical closed circuit at the waste acid discharge point, which can be easily installed alongside an existing pickling line, etc., regardless of the capacity.
有機溶媒を使用してFeイオンを含む酸の回収方法とし
て。As a method for recovering acids containing Fe ions using organic solvents.
きわめて工業的価値大なるものである。It has extremely great industrial value.
第1図は本発明の実施例を示す工程図、第2図は抽出剤
として50%D2EHPAをケロシンで稀釈した有機溶
媒によるFe3+イオン抽出平衡曲線を示し、第3図は
15%H(lによる逆抽出(剥離)をした場合の剥離平
衡曲線図(〇−〇)。
並びに還元性物質としでNa25o3又はNaClを使
用し、15%HC/とで逆抽出(剥離)を実施した場合
の剥離平衡曲線図(X−X)を示し。
第4図は有機相(30%D2EHPA、ケロシン稀釈、
硫酸酸性液)でのPHとFe3+イオンの抽出率の関係
(〇−9.−〇)、PHとFe2+4オンの抽出率の関
係(X−X)を示す曲線図表である。Figure 1 is a process diagram showing an example of the present invention, Figure 2 is an equilibrium curve for Fe3+ ion extraction using an organic solvent in which 50% D2EHPA is diluted with kerosene as an extractant, and Figure 3 is an equilibrium curve for Fe3+ ion extraction using 15% H (l). Peeling equilibrium curve diagram (〇-〇) when back extraction (peeling) is performed. Also, peeling equilibrium when back extraction (peeling) is performed using Na25O3 or NaCl as a reducing substance and 15% HC/. The curve diagram (X-X) is shown. Figure 4 shows the organic phase (30% D2EHPA, kerosene dilution,
It is a curve chart showing the relationship between PH and the extraction rate of Fe3+ ions (〇-9.-〇) and the relationship between PH and the extraction rate of Fe2+4 ions (X-X) in a sulfuric acid acidic solution.
Claims (1)
にFe3+イオンを抽出含有せしめ、該有機溶媒を、還
元性物質を含*子ろ水溶液、又は還元性物質をバブリン
グさせでいる溶液と接触させることにより、Feイオン
の剥離を容易に行ない得るようにした後、該有機溶媒を
鉱酸と接触させることにより、有機相のFeイオンを剥
離することを特徴とする有機溶媒を使用してFeイオン
を含む酸の回収方法。Fe3+ ions are extracted and contained in an organic solvent in which 1-alkyl phosphoric acid is diluted with a petroleum-based hydrocarbon, and the organic solvent is brought into contact with an aqueous solution containing a reducing substance or a solution in which the reducing substance is bubbled. By using an organic solvent, the Fe ions can be easily stripped off, and then the Fe ions in the organic phase can be stripped off by contacting the organic solvent with a mineral acid. A method for recovering acids containing
Priority Applications (26)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP50089433A JPS585989B2 (en) | 1975-07-21 | 1975-07-21 | Yukiyo Bio-Site FE |
| AU11214/76A AU501823B2 (en) | 1975-03-14 | 1976-02-18 | Removing heavy metals froman acid waste liquid |
| SE7602125A SE7602125L (en) | 1975-03-14 | 1976-02-23 | WAY TO TREAT AN ACID WASTE WASTE |
| CA247,168A CA1073566A (en) | 1975-03-14 | 1976-03-03 | Process for treating an acid waste liquid |
| IT21021/76A IT1059575B (en) | 1975-03-14 | 1976-03-10 | PROCEDURE FOR TREATING AN ACID WASTE LIQUID ESPECIALLY A LIQUID USED FOR PICKLING FOR RECOVERY PURPOSE |
| FR7607251A FR2303868A1 (en) | 1975-03-14 | 1976-03-12 | PROCESS FOR TREATING ACIDIC WASTE LIQUIDS |
| DE2610434A DE2610434C2 (en) | 1975-03-14 | 1976-03-12 | Process for the preparation of used, acidic treatment liquids containing iron ions for metal materials and pieces |
| GB10232/76A GB1539250A (en) | 1975-03-14 | 1976-03-15 | Process for treating acid waste liquids containing iron ions |
| US05/680,928 US4082832A (en) | 1975-05-06 | 1976-04-27 | Treatment of raw materials containing titanium |
| CA251,611A CA1079488A (en) | 1975-05-06 | 1976-04-30 | Treatment method of raw materials containing titanium |
| NO761531A NO761531L (en) | 1975-05-06 | 1976-05-04 | |
| IT22942/76A IT1071494B (en) | 1975-05-06 | 1976-05-04 | PROCEDURE FOR TREATING RAW MATERIALS CONTAINING TITANIUM IN THE PRODUCTION OF TITANIUM DIOXIDE |
| FR7613438A FR2310314A1 (en) | 1975-05-06 | 1976-05-05 | PROCESS FOR TREATMENT OF RAW MATERIALS CONTAINING TITANIUM AND TITANIUM BIOXIDE THUS OBTAINED |
| AU13637/76A AU505093B2 (en) | 1975-05-06 | 1976-05-05 | Production of titanium dioxide |
| FI761256A FI761256A7 (en) | 1975-05-06 | 1976-05-05 | |
| DE19762620065 DE2620065A1 (en) | 1975-05-06 | 1976-05-06 | PROCESS FOR MANUFACTURING TITANIUM DIOXIDE |
| NL7604855A NL7604855A (en) | 1975-05-06 | 1976-05-06 | By product recovery during prepn of titania - by fractional sepn of metallic ions with org solvents |
| GB18701/76A GB1552918A (en) | 1975-05-06 | 1976-05-06 | Production of titanium dioxide |
| ES447652A ES447652A1 (en) | 1975-05-06 | 1976-05-06 | Production of titanium dioxide |
| BE2055026A BE841820A (en) | 1975-07-21 | 1976-05-14 | PROCESS FOR TREATING AN ACID RESIDUAL LIQUID |
| NL7605401A NL7605401A (en) | 1975-07-21 | 1976-05-20 | PROCESS FOR TREATING ACID WASTE MATERIALS CONTAINING ACID IONS. |
| NO761943A NO761943L (en) | 1975-07-21 | 1976-06-08 | |
| BR7604337A BR7604337A (en) | 1975-07-21 | 1976-07-02 | PROCESS FOR TREATING AN ACID RESIDUAL LIQUID |
| FI761968A FI761968A7 (en) | 1975-07-21 | 1976-07-06 | |
| ES449985A ES449985A1 (en) | 1975-07-21 | 1976-07-21 | Recovery of acid containing fe ion by using organic solvent |
| US05/820,258 US4166098A (en) | 1975-03-14 | 1977-07-29 | Process for treating an acid waste liquid |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP50089433A JPS585989B2 (en) | 1975-07-21 | 1975-07-21 | Yukiyo Bio-Site FE |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS5217389A JPS5217389A (en) | 1977-02-09 |
| JPS585989B2 true JPS585989B2 (en) | 1983-02-02 |
Family
ID=13970523
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP50089433A Expired JPS585989B2 (en) | 1975-03-14 | 1975-07-21 | Yukiyo Bio-Site FE |
Country Status (7)
| Country | Link |
|---|---|
| JP (1) | JPS585989B2 (en) |
| BE (1) | BE841820A (en) |
| BR (1) | BR7604337A (en) |
| ES (1) | ES449985A1 (en) |
| FI (1) | FI761968A7 (en) |
| NL (1) | NL7605401A (en) |
| NO (1) | NO761943L (en) |
Families Citing this family (2)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPS5836677B2 (en) * | 1976-01-16 | 1983-08-10 | 日本ソレックス株式会社 | Method for recovering sulfuric acid and contained metals from iron sulfate solution |
| JPS5989732A (en) * | 1982-11-11 | 1984-05-24 | Hiroshi Mashima | Method for reducing and back-extracting fe (3) transferred to organic phase |
-
1975
- 1975-07-21 JP JP50089433A patent/JPS585989B2/en not_active Expired
-
1976
- 1976-05-14 BE BE2055026A patent/BE841820A/en not_active IP Right Cessation
- 1976-05-20 NL NL7605401A patent/NL7605401A/en not_active Application Discontinuation
- 1976-06-08 NO NO761943A patent/NO761943L/no unknown
- 1976-07-02 BR BR7604337A patent/BR7604337A/en unknown
- 1976-07-06 FI FI761968A patent/FI761968A7/fi not_active Application Discontinuation
- 1976-07-21 ES ES449985A patent/ES449985A1/en not_active Expired
Also Published As
| Publication number | Publication date |
|---|---|
| NO761943L (en) | 1977-01-24 |
| JPS5217389A (en) | 1977-02-09 |
| ES449985A1 (en) | 1977-08-16 |
| BE841820A (en) | 1976-09-01 |
| FI761968A7 (en) | 1977-01-22 |
| BR7604337A (en) | 1977-07-26 |
| NL7605401A (en) | 1977-01-25 |
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