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JPS6237715B2 - - Google Patents
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JPS6237715B2 - - Google Patents

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Publication number
JPS6237715B2
JPS6237715B2 JP54036990A JP3699079A JPS6237715B2 JP S6237715 B2 JPS6237715 B2 JP S6237715B2 JP 54036990 A JP54036990 A JP 54036990A JP 3699079 A JP3699079 A JP 3699079A JP S6237715 B2 JPS6237715 B2 JP S6237715B2
Authority
JP
Japan
Prior art keywords
ions
organic solvent
organic
phase
hcl
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
JP54036990A
Other languages
Japanese (ja)
Other versions
JPS55131184A (en
Inventor
Yamaji Nishimura
Michio Watanabe
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.)
NISHIMURA WATANABE CHUSHUTSU KENKYUSHO KK
Original Assignee
NISHIMURA WATANABE CHUSHUTSU KENKYUSHO KK
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 NISHIMURA WATANABE CHUSHUTSU KENKYUSHO KK filed Critical NISHIMURA WATANABE CHUSHUTSU KENKYUSHO KK
Priority to JP3699079A priority Critical patent/JPS55131184A/en
Priority to DE3012246A priority patent/DE3012246C2/en
Publication of JPS55131184A publication Critical patent/JPS55131184A/en
Publication of JPS6237715B2 publication Critical patent/JPS6237715B2/ja
Granted legal-status Critical Current

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Extraction Or Liquid Replacement (AREA)
  • Manufacture And Refinement Of Metals (AREA)
  • Manufacture Of Iron (AREA)
  • Cleaning And De-Greasing Of Metallic Materials By Chemical Methods (AREA)

Description

【発明の詳細な説明】[Detailed description of the invention]

本発明は、アルキル燐酸、燐酸エステル、オキ
シムあるいは第1級〜第4級アミンからなる群か
ら選択した1種または2種以上からなる油出剤
(以下単に抽出剤という)を石油系炭化水素で希
釈してなる有機溶媒に抽出されたFeイオン、Fe
塩化物錯体の剥離に関するものである。 従来有機相に抽出されたFeイオン、Fe塩化物
錯体の剥離には濃度の高いHClあるいは剥離液中
のFeイオン濃度を高めると云うことができず、
このため、有機相のFeを経済的に剥離できなか
つた。このために、Feを含む水溶液よりFeを抽
出分離する方法を溶媒抽出法によつて経済的にな
された事は、本発明人以外の発表はない。 本発明人は、これらの方法について特願昭50−
31550号、特願昭50−055048号、特願昭50−
089433号、特願昭50−144861号あるいは特願昭51
−118598号において開示しているが、いずれも2
種以上の有機溶媒を使用し、しかも多段にこれを
利用することによりそれぞれの特性を利用し、
Feを経済的に採取して酸を回収する方法を開示
しているが、工程が複雑となり従つて設備費が嵩
むと云う欠点があつた。 本発明者は種々研究の結果、有機溶媒中のFe
は、このような従来法の欠点を克服し、本発明を
完成するに至つた。すなわち本発明の要旨とする
ところは、アルキル燐酸、燐酸エステル、オキシ
ム、あるいは第1級アミン〜第4級アミン、これ
らの群よりからなる群から選択された1種または
2種以上が選択された抽出剤を石油系炭化水素で
希釈してなる有機溶媒に抽出されたFeイオンを
剥離するに当り、ガス状還元性物質単独または触
媒存在下のガス状還元性物質と該有機溶媒相とを
接触させることにより鉄の原子価を変化させ、剥
離を容易にした後、水または鉱酸または有機酸を
含む水溶液と接触させる事によりFeを剥離する
ことを特徴とする鉄イオンの剥離方法にある。抽
出剤としてはアルキル燐酸、燐酸エステル、オキ
シム、アミンの各品種中の1種またはそれ以上を
使用できることは勿論である。 本発明にて使用する、アルキル燐酸とは下記を
示す化合物である。
The present invention uses a petroleum-based hydrocarbon to extract an oil extractant (hereinafter simply referred to as an extractant) consisting of one or more selected from the group consisting of alkyl phosphoric acids, phosphoric esters, oximes, or primary to quaternary amines. Fe ions extracted into diluted organic solvent, Fe
It concerns the stripping of chloride complexes. Conventionally, it is not possible to remove Fe ions extracted into the organic phase and Fe chloride complexes by increasing the concentration of HCl or Fe ions in the stripping solution.
For this reason, Fe in the organic phase could not be economically peeled off. For this reason, no one other than the present inventor has reported that an economic method for extracting and separating Fe from an aqueous solution containing Fe by a solvent extraction method has been made. The inventor has filed a patent application for these methods in 1970-
No. 31550, Patent Application No. 1984-055048, Special Application No. 1973-
No. 089433, Patent Application No. 144861 or Patent Application No. 1973
−118598, but both are 2
By using more than one type of organic solvent and using them in multiple stages, we can take advantage of the characteristics of each.
Although this method discloses a method for economically extracting Fe and recovering acid, it has the disadvantage that the process becomes complicated and the equipment cost increases. As a result of various studies, the present inventor found that Fe in organic solvents
overcame these drawbacks of the conventional method and completed the present invention. That is, the gist of the present invention is that one or more selected from the group consisting of alkyl phosphoric acids, phosphoric esters, oximes, or primary amines to quaternary amines. When stripping Fe ions extracted into an organic solvent obtained by diluting an extractant with a petroleum-based hydrocarbon, the organic solvent phase is brought into contact with a gaseous reducing substance alone or in the presence of a catalyst. The iron ion stripping method is characterized by changing the valence of iron by changing the valence of iron to facilitate stripping, and then stripping the Fe by contacting it with water or an aqueous solution containing a mineral acid or an organic acid. Of course, one or more of alkyl phosphoric acids, phosphoric esters, oximes, and amines can be used as the extractant. The alkyl phosphoric acid used in the present invention is a compound shown below.

【式】【formula】

【式】【formula】

【式】【formula】

【式】または[expression] or

【式】Rはアルキル基を示す。 (但し上式中Rは一般に4〜14個の炭素原子を
含むアルキル基である)。 また燐酸エステルとは下記の式に示す化合物であ
る。
[Formula] R represents an alkyl group. (wherein R in the above formula is generally an alkyl group containing 4 to 14 carbon atoms). Further, the phosphoric acid ester is a compound represented by the following formula.

【式】【formula】 【式】【formula】

【式】又は[Formula] or

【式】 (但しRは4〜14個の炭素原子を含むアルキル
基である)。 第1級アミン〜第4級アミンを次に示し、テス
トに使用した1例を示すが、類似の高分子アミン
も当然使用できる。 第1級アミン:RNまたはR2NH2(但しRは4
〜18個の炭素原子を含むアルキル基である)で示
され、テストには次のものが使用された。 CH3C(CH32CH2C(CH32CH2C
(CH32CH2C(CH32CH2C(CH32NH2 第2級アミン:R2NまたはR2NH(但しRは4
〜18個の炭素原子のアルキル基である)で示さ
れ、テストには次のものが使用された。 第3級アミン:R3NまたはR3NH2(但しRは4
〜8個の炭素原子のアルキル基である)で示さ
れ、テストには次のものが使用された。 第4級アミン:
[Formula] (wherein R is an alkyl group containing 4 to 14 carbon atoms). Primary amines to quaternary amines are shown below, and one example used in the test is shown, but similar polymeric amines can of course also be used. Primary amine: RN or R 2 NH 2 (where R is 4
is an alkyl group containing ~18 carbon atoms), and the following were used for testing: CH 3 C (CH 3 ) 2 CH 2 C (CH 3 ) 2 CH 2 C
(CH 3 ) 2 CH 2 C (CH 3 ) 2 CH 2 C (CH 3 ) 2 NH 2 Secondary amine: R 2 N or R 2 NH (where R is 4
an alkyl group of ~18 carbon atoms), and the following were used for testing: Tertiary amine: R 3 N or R 3 NH 2 (where R is 4
(alkyl group of ~8 carbon atoms), and the following were used for testing: Quaternary amine:

【式】または[expression] or

【式】 (但しRは6〜18個の炭素原子のアルキル基で
ある) 本発明に使用されるオキシムの一例を次に示
す。 これと類似のオキシム、例えばゼネラルミルズ
化学の商品名LIX64,LIX65,LIX70,LIX34また
はLIX54等が使用される。 本発明で使用する石油系炭化水素希釈剤とは芳
香族系炭化水素、脂肪族系炭化水素あるいはケロ
シンの如き雑多な炭化水素混合品等も使用するこ
とができる。抽出剤の濃度は被処理液の性状、回
収する物質の濃度や品質等によつてその濃度が決
定される。 一般に抽出剤の濃度は2%〜95%(体積)であ
る。 次に本発明において使用するガス状還元性物質
はH2ガス、H2Sガス、COガス、SO2ガスであ
る。また還元を促進するために、触媒を使用する
こともできるが、本発明で使用する触媒はラネー
ニツケルと呼ばれる金属ニツケル、コバルト、
銅、鉄、銅−クロム酸化物、ニツケル酸化物、コ
バルト酸化物が含まれる。 以下、本発明を図面に基き詳細に説明する。 まず第1図のフロシートに示すように、Fe3+
含有HClまたはH2SO4溶液(A)を抽出剤の石油系炭
化水素希釈剤で希釈してなる有機溶媒で抽出(抽
出工程)し、得られた有機溶媒相は変換工程に送
られ、ここで装入されるガス状還元性物質(E)、例
えば水素ガスと接触して、有機溶媒相中のFeイ
オンをFe2+に変換して剥離を容易にした後、
Fe2+剥離工程で装入される剥離剤(B)すなわち
水、または鉱酸または有機酸を含有する水溶液と
接触させることによりFe2+を剥離し、有機溶媒
を再生して抽出工程へ再循環し、回収した水性相
中のFe2+はFe回収工程Cへ送られる。抽出工程
のFe3+イオン、Fe塩化物錯体を抽出した水性相
は少くとも一部をHCl,H2SO4による鉄含有材料
処理工程(D)へ再循環される。ガス状還元性物質(E)
としてH2,H2S,SO2,CO等を使用でき、必要
に応じ還元触媒を添加する。 第2図は、Fe3+含有HClまたはH2SO4溶液(A)か
らFe3+イオン、Fe塩化物錯体を抽出した、抽出
剤を石油系炭化水素で希釈した有機溶媒溶液を電
解槽陰極室に導入通過させ、陰極で発生する発生
機の水素により有機溶媒中のFe3+イオンをFe2+
イオン、錯体の原子価を変換させ同時に陰極室を
通過する剥離剤水溶液中に変換されたFeを剥離
し、有機溶媒を再生する他の実施態様のフローシ
ートを示す図である。 第3図は、アルキル燐酸を使用してFe3+イオ
ンとFe2+イオンの抽出率とPHの関係を示したも
ので、Fe2+イオンの剥離はPH3以下の水溶液で
可能である事を示す。 第4図は、アルキルアミンを使用して、Fe3+
イオンとFe2+イオンを錯体として抽出する、HCl
濃度と抽出率の関係を示す、水相のHCl濃度が低
いとこで抽出する事は、剥離液のFeやHCl濃度が
高くなると剥離が出来ない事を示す。 以下、実施例および比較例を挙げて本発明を具
体的に説明する。 実施例 1 抽出剤としてアルキル燐酸の品種群より選択し
たD2EHPAをn−パラフインで50%濃度に希釈し
た有機溶媒をテストに使用した。H2SO4380g/
、Fe3+42g/の水溶液を上記有機溶媒と接
触させ、18.6g/の濃度のFe3+イオンを含有す
る有機溶媒溶液を得た。以下のテスト(イ)〜(ニ)にお
いてはこれを使用した。 (イ) この有機溶媒溶液(有機相)を100g/
H2SO4(水性相)と有機相/水性相(体積)
(以下にO/Aと略記)=1で接触させたとこ
ろ、10分間震とう後、水性相に移行したFeイ
オンは0.01g/以下であつた(比較例)。 (ロ) 次に、150g/HClとO/A=1で接触さ
せ、10分間震とう後の水性相中のFeを測定し
たところFeイオンの濃11.2g/で1段で60.2
%の剥離率が得られた(比較例)。 (ハ) 次にFe2+ 100g/(FeSO4の形で)、 (NH42SO4 40g/を含み、且つH2SO450
g/を含有する水溶液に陰極を挿入し、隔膜
で仕切つた陽極との間に電流を流し、その水相
中を、Fe3+18.6g/の割合で含有する有機相
を滴径1.5〜2mmで通過させたところ、5分間
通過後の有機相にはFeイオン0.1g/以下で
あつた(実施例)。 実施例 2 アルキル燐酸の品種群よりD2EHPA、燐酸エス
テルの品種群よりトリブチルホスフエート
(TBP)をそれぞれ選択し、イソパラフインで希
釈し、それらの濃度をそれぞれ30%(体積)およ
び20%(体積)になるように希釈した有機溶媒溶
液(有機相)をテストに使用した。 この有機溶媒溶液をFe3+イオンを含むHCl溶液
と接触させ、有機相にFe3+とFe塩化物錯体との
両者を抽出し、21.4g/のFe濃度の有機溶媒
をテストに使用した。 (イ) この有機溶媒を水と接触させたところ、O/
A=1で10分間の震とう後水性相に移行した
Fe量を測定したところ6.9g/であつた(比
較例)。 (ロ) また150g/HCl溶液とO/A=1の比率
で接触したところ、水性相中に移行したFeの
量は8.4g/であつた(比較例)。 (ハ) また有機相にNi含有量50%のラネーニツケ
ル触媒を100g/の割合で懸濁させ、H2ガス
を10分間吹き込んだ後有機相をとり出し、50
g/H2SO4を含む水溶液とO/A=1の比率
で10分間接触させた後、水性相を分析したとこ
ろ、Fe濃度18.9g/であつた(実施例)。 (ホ) 電解槽(陰極室)内にFeCl2125g/、
NH4Cl60g/を含む水相内を滴径2〜3mmで
有機溶媒を5分間通過させた後の有機相のFe
を測定したところ、Feは0.42g/であつた
(実施例)。 実施例 3 オキシムの品種群よりLI×65、アルキル燐酸
の品種群よりD2EHPA、燐酸エステルの品種群よ
りTBP、高分子アミンの品種群よりTOAを選択
し、それぞれ芳香族炭化水素で希釈し、それぞれ
の濃度が5%、30%、10%、5%になるように調
合した。 Fe3+イオンを含むHCl溶液と接触させてFeを
抽出し、15.4g/の濃度のFeを含有する有機
溶媒をテストに使用した。 相機相へSO2ガスを5分間吹きこみ、次に50
g/H2SO4溶液と接触させた後の有機相のFe
量を分析したところ、2.1g/であつた。 これらの実施例の基礎をなす水溶液中のFe3+
イオン、Fe2+イオンの抽出率とPHとの関係を示
せば第3図に示す通りである。第4図はFe3+
Fe2+塩化物錯体の抽出率とHCl濃度との関係を示
す。図において横軸は水性相のHCl濃度(g/
)を示し、縦軸は抽出率を示す。 第5図にFe塩化物錯体の平衡図を示す。図に
おいて曲線aは還元性溶液によるFe塩化物錯体
の平衡図、曲線bは水によるFe塩化物錯体の平
衡図である。第6図はFe剥離平衡曲線を示し、
曲線cは還元性物質と接触後の有機相中のFeを
50g/H2SO4で剥離した時の平衡曲線、曲線d
は150g/HClによる剥離平衡曲線を示す。 また本発明を実施した場合次のような利点があ
る。 (1) 非鉄冶金界における湿式製錬工程において、
Feイオンの分離工程に溶媒抽出法が採用でき
るし、経済性もあるので、従来Feイオンの除
去と共に、共存する有価金属の損失が少くなる
ので経済性が高くなる、 (2) 有価金属の他に比較的Feを多量に含有する
浸出残さ、熔融滓、鉱あるいは珪酸鉱等の未利
用資源を、強酸を使用して浸出できることか
ら、固形の産業廃棄物を処理し、有価金属や電
解鉄を経済的に得ることが可能になる、 (3) 金属製品や金属材料の表面処理に使用された
廃酸(鉱酸あるいは有機酸)が経済的に回収で
きるので、クローズサーキツトが形成され、公
害防止と資源の回収が可能となる、 (4) 従来から採用されている加熱分解法による廃
HClの回収に比較してエネルギー使用量少な
く、経済性がある。また常温操業であるため耐
食性材料の選択が容易で、しかも、単純な装置
であるために、メンテナンス費用小さい装置を
製作できる、 (5) 大型から小型の装置まで製作が可能で、しか
も増設が自由であるために利用できる工場の範
囲が広いこと。 (6) 中和法に比較して、スラツジの発生が全くな
いことから、投棄処理費を必要とせず、しか
も、高純度電解鉄が回収されるので装置の立地
条件にスラツジ処理を考慮しなくてすむこと等
である。
[Formula] (wherein R is an alkyl group having 6 to 18 carbon atoms) An example of an oxime used in the present invention is shown below. Oximes similar to this are used, such as General Mills Chemical's trade names LIX64, LIX65, LIX70, LIX34 or LIX54. The petroleum hydrocarbon diluent used in the present invention may include aromatic hydrocarbons, aliphatic hydrocarbons, and miscellaneous hydrocarbon mixtures such as kerosene. The concentration of the extractant is determined by the properties of the liquid to be treated, the concentration and quality of the substance to be recovered, etc. Generally, the concentration of extractant is between 2% and 95% (by volume). Next, the gaseous reducing substances used in the present invention are H 2 gas, H 2 S gas, CO gas, and SO 2 gas. Catalysts can also be used to promote reduction, but the catalysts used in the present invention include metal nickel called Raney nickel, cobalt,
Includes copper, iron, copper-chromium oxide, nickel oxide, and cobalt oxide. Hereinafter, the present invention will be explained in detail based on the drawings. First, as shown in the flow sheet of Figure 1, Fe 3+
The HCl or H 2 SO 4 solution (A) is extracted with an organic solvent diluted with a petroleum hydrocarbon diluent as an extractant (extraction step), and the obtained organic solvent phase is sent to the conversion step, where it is After contacting with a gaseous reducing substance (E), e.g. hydrogen gas, which is charged at
Fe 2+ is stripped by contacting it with the stripping agent (B) charged in the Fe 2+ stripping process, i.e., water or an aqueous solution containing mineral acid or organic acid, and the organic solvent is regenerated and reused in the extraction process. Fe 2+ in the circulated and recovered aqueous phase is sent to Fe recovery step C. At least a portion of the aqueous phase from which Fe 3+ ions and Fe chloride complexes have been extracted in the extraction step is recycled to the iron-containing material treatment step (D) with HCl and H 2 SO 4 . Gaseous reducing substances (E)
H 2 , H 2 S, SO 2 , CO, etc. can be used as the catalyst, and a reduction catalyst may be added if necessary. Figure 2 shows the organic solvent solution in which Fe 3+ ions and Fe chloride complexes were extracted from Fe 3+ -containing HCl or H 2 SO 4 solution (A), and the extractant was diluted with petroleum-based hydrocarbons. The Fe 3+ ions in the organic solvent are converted into Fe 2+ by the generator hydrogen generated at the cathode.
FIG. 7 is a diagram showing a flow sheet of another embodiment in which the valences of ions and complexes are converted and at the same time Fe converted into an aqueous stripping agent solution passing through a cathode chamber is stripped to regenerate an organic solvent. Figure 3 shows the relationship between the extraction rate of Fe 3+ ions and Fe 2+ ions and pH using alkyl phosphoric acid, and shows that Fe 2+ ions can be removed using an aqueous solution with a pH of 3 or less. show. Figure 4 shows Fe 3+
HCl to extract ions and Fe 2+ ions as a complex
The relationship between concentration and extraction rate shows that extraction occurs when the HCl concentration in the aqueous phase is low, indicating that stripping cannot be performed when the Fe and HCl concentrations in the stripping solution are high. The present invention will be specifically described below with reference to Examples and Comparative Examples. Example 1 As an extractant, an organic solvent prepared by diluting D 2 EHPA selected from a group of alkyl phosphoric acid varieties with n-paraffin to a concentration of 50% was used in the test. H 2 SO 4 380g/
, Fe 3+ 42 g/aqueous solution was brought into contact with the above organic solvent to obtain an organic solvent solution containing Fe 3+ ions at a concentration of 18.6 g/a. This was used in the following tests (a) to (d). (b) 100g/100g of this organic solvent solution (organic phase)
H 2 SO 4 (aqueous phase) and organic phase/aqueous phase (volume)
(hereinafter abbreviated as O/A) = 1, and after shaking for 10 minutes, the amount of Fe ions transferred to the aqueous phase was 0.01 g/or less (comparative example). (b) Next, we brought it into contact with 150g/HCl at O/A=1, and after shaking for 10 minutes, we measured Fe in the aqueous phase.The Fe ion concentration was 11.2g/1 stage, and it was 60.2
% peeling rate was obtained (comparative example). (c) Then contains Fe 2+ 100g/(in the form of FeSO 4 ), (NH 4 ) 2 SO 4 40g/, and H 2 SO 4 50
A cathode is inserted into an aqueous solution containing Fe 3+ and a current is passed between it and an anode separated by a diaphragm, and an organic phase containing Fe 3+ at a rate of 18.6 g/ is formed into droplets with a diameter of 1.5 to 2 mm. When the organic phase was passed for 5 minutes, Fe ions were found to be 0.1 g/less or less (Example). Example 2 D 2 EHPA was selected from the alkyl phosphate variety group, and tributyl phosphate (TBP) was selected from the phosphate ester variety group, diluted with isoparaffin, and their concentrations were adjusted to 30% (by volume) and 20% (by volume), respectively. An organic solvent solution (organic phase) diluted to a volume of This organic solvent solution was contacted with an HCl solution containing Fe 3+ ions to extract both Fe 3+ and Fe chloride complexes into the organic phase, and an organic solvent with an Fe concentration of 21.4 g/L was used for the test. (b) When this organic solvent was brought into contact with water, O/
After shaking for 10 minutes at A=1, it transitioned to an aqueous phase.
When the amount of Fe was measured, it was 6.9 g/(comparative example). (b) When the sample was brought into contact with a 150 g/HCl solution at a ratio of O/A=1, the amount of Fe transferred into the aqueous phase was 8.4 g/(comparative example). (c) In addition, a Raney nickel catalyst with a Ni content of 50% was suspended in the organic phase at a rate of 100 g/ H2 gas was blown into the organic phase for 10 minutes, and then the organic phase was taken out.
After contacting with an aqueous solution containing g/H 2 SO 4 at a ratio of O/A=1 for 10 minutes, the aqueous phase was analyzed and found to have a Fe concentration of 18.9 g/(Example). (E) 125g of FeCl 2 / in the electrolytic cell (cathode chamber),
Fe in the organic phase after passing an organic solvent with a droplet size of 2 to 3 mm for 5 minutes through an aqueous phase containing 60 g of NH 4 Cl/
When measured, Fe was 0.42 g/(Example). Example 3 LI×65 was selected from the oxime variety group, D 2 EHPA was selected from the alkyl phosphate variety group, TBP was selected from the phosphate ester variety group, and TOA was selected from the polymer amine variety group, and each was diluted with an aromatic hydrocarbon. , and the respective concentrations were 5%, 30%, 10%, and 5%. Fe was extracted by contacting with an HCl solution containing Fe 3+ ions, and an organic solvent containing Fe at a concentration of 15.4 g/L was used for the test. Blow SO 2 gas into the phase machine for 5 minutes, then 50
g/Fe of the organic phase after contact with H 2 SO 4 solution
When the amount was analyzed, it was 2.1g/. Fe 3+ in the aqueous solution underlying these examples
The relationship between the extraction rate of ions and Fe 2+ ions and pH is shown in Figure 3. Figure 4 shows Fe 3+ ,
The relationship between the extraction rate of Fe 2+ chloride complex and HCl concentration is shown. In the figure, the horizontal axis is the HCl concentration (g/
), and the vertical axis shows the extraction rate. Figure 5 shows an equilibrium diagram of the Fe chloride complex. In the figure, curve a is an equilibrium diagram of the Fe chloride complex caused by a reducing solution, and curve b is an equilibrium diagram of the Fe chloride complex caused by water. Figure 6 shows the Fe peeling equilibrium curve,
Curve c represents Fe in the organic phase after contact with a reducing substance.
Equilibrium curve when peeled at 50g/H 2 SO 4 , curve d
shows the peel equilibrium curve with 150 g/HCl. Further, when the present invention is implemented, there are the following advantages. (1) In the hydrometallurgical process in the non-ferrous metallurgy industry,
Solvent extraction can be used in the separation process of Fe ions and is also economical, so in addition to removing conventional Fe ions, the loss of coexisting valuable metals is reduced, making it more economical. (2) In addition to valuable metals. Unused resources such as leaching residue, slag, ore, or silicate ore, which contain relatively large amounts of Fe, can be leached out using strong acids. (3) Since waste acids (mineral acids or organic acids) used for surface treatment of metal products and materials can be economically recovered, a closed circuit is formed and pollution is reduced. (4) Waste treatment using the conventional thermal decomposition method
Compared to HCl recovery, it uses less energy and is more economical. In addition, since it operates at room temperature, it is easy to select corrosion-resistant materials, and since it is a simple device, it is possible to manufacture devices with low maintenance costs. Because of this, there is a wide range of factories available. (6) Compared to the neutralization method, there is no sludge generation, so there is no need for disposal costs, and since high-purity electrolytic iron is recovered, sludge treatment does not need to be considered in the location conditions of the equipment. These include things like working on something.

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

第1図は本発明方法の一実施態様のフローシー
トを示す図、第2図はFeの原子価変換と剥離と
を電解槽陰極室内で同時に行う本発明の実施態様
のフローシートを示す図、第3図は水溶液中の
Fe3+イオン、Fe2+イオン抽出率とPHとの関係を
示す図、第4図はFe3+、Fe2+塩化物錯体の抽出
率とHCl濃度との関係を示す図、第5図はFe塩化
物錯体の剥離平衡曲線を示す図、第6図はFe剥
離平衡曲線を示す図である。
FIG. 1 is a diagram showing a flow sheet of an embodiment of the method of the present invention, FIG. 2 is a diagram showing a flow sheet of an embodiment of the present invention in which Fe valence conversion and stripping are performed simultaneously in the cathode chamber of an electrolytic cell, Figure 3 shows the
A diagram showing the relationship between Fe 3+ ion, Fe 2+ ion extraction rate and PH, Figure 4 is a diagram showing the relationship between Fe 3+ and Fe 2+ chloride complex extraction rate and HCl concentration, Figure 5 6 is a diagram showing a peeling equilibrium curve of Fe chloride complex, and FIG. 6 is a diagram showing a Fe peeling equilibrium curve.

Claims (1)

【特許請求の範囲】[Claims] 1 アルキル燐酸、燐酸エステル、オキシムある
いは第1級アミン〜第4級アミンからなる群から
選択された抽出剤を石油系炭化水素で希釈してな
る有機溶媒に抽出されたFeイオン、Fe塩化物錯
体を剥離するに当り、有機溶媒相中のFe3+を有
機相中で触媒の存在または不在下のガス状還元剤
と接触させることにより、Feの原子価を変化さ
せ、次に水または、鉱酸または有機酸を含有する
水溶液と接触させることによりFeを剥離するこ
とを特徴とする、鉄イオンの剥離方法。
1 Fe ions and Fe chloride complex extracted in an organic solvent prepared by diluting an extractant selected from the group consisting of alkyl phosphoric acid, phosphoric acid ester, oxime, or primary amine to quaternary amine with petroleum hydrocarbon. For stripping, the valence of Fe is changed by contacting the Fe 3+ in the organic solvent phase with a gaseous reducing agent in the presence or absence of a catalyst in the organic phase, and then with water or minerals. A method for removing iron ions, the method comprising removing Fe by contacting with an aqueous solution containing an acid or an organic acid.
JP3699079A 1979-03-30 1979-03-30 Peeling method for iron ion Granted JPS55131184A (en)

Priority Applications (2)

Application Number Priority Date Filing Date Title
JP3699079A JPS55131184A (en) 1979-03-30 1979-03-30 Peeling method for iron ion
DE3012246A DE3012246C2 (en) 1979-03-30 1980-03-28 Process for the recovery of iron compounds from organic solvent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP3699079A JPS55131184A (en) 1979-03-30 1979-03-30 Peeling method for iron ion

Publications (2)

Publication Number Publication Date
JPS55131184A JPS55131184A (en) 1980-10-11
JPS6237715B2 true JPS6237715B2 (en) 1987-08-13

Family

ID=12485174

Family Applications (1)

Application Number Title Priority Date Filing Date
JP3699079A Granted JPS55131184A (en) 1979-03-30 1979-03-30 Peeling method for iron ion

Country Status (1)

Country Link
JP (1) JPS55131184A (en)

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* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP5338186B2 (en) * 2008-08-07 2013-11-13 住友金属鉱山株式会社 Method for scrubbing amine-based extractant after back extraction

Also Published As

Publication number Publication date
JPS55131184A (en) 1980-10-11

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