JPH0643620B2 - Solvent extraction method - Google Patents
Solvent extraction methodInfo
- Publication number
- JPH0643620B2 JPH0643620B2 JP61181447A JP18144786A JPH0643620B2 JP H0643620 B2 JPH0643620 B2 JP H0643620B2 JP 61181447 A JP61181447 A JP 61181447A JP 18144786 A JP18144786 A JP 18144786A JP H0643620 B2 JPH0643620 B2 JP H0643620B2
- Authority
- JP
- Japan
- Prior art keywords
- extraction
- organic
- amine
- solvent
- concentration
- 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 - Lifetime
Links
- 238000000034 method Methods 0.000 title claims description 29
- 238000000638 solvent extraction Methods 0.000 title claims description 19
- 239000012074 organic phase Substances 0.000 claims description 33
- 230000002378 acidificating effect Effects 0.000 claims description 30
- 150000001412 amines Chemical class 0.000 claims description 28
- 229910021645 metal ion Inorganic materials 0.000 claims description 26
- 239000007864 aqueous solution Substances 0.000 claims description 22
- -1 amine salt Chemical class 0.000 claims description 17
- 239000003513 alkali Substances 0.000 claims description 16
- 239000002904 solvent Substances 0.000 claims description 15
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 10
- 239000003085 diluting agent Substances 0.000 claims description 9
- 150000001875 compounds Chemical class 0.000 claims description 8
- 150000003014 phosphoric acid esters Chemical class 0.000 claims description 2
- 150000001732 carboxylic acid derivatives Chemical class 0.000 claims 1
- 230000001172 regenerating effect Effects 0.000 claims 1
- 238000000605 extraction Methods 0.000 description 40
- 239000011550 stock solution Substances 0.000 description 21
- 238000000926 separation method Methods 0.000 description 20
- 239000008346 aqueous phase Substances 0.000 description 19
- 238000006243 chemical reaction Methods 0.000 description 15
- 229910052751 metal Inorganic materials 0.000 description 13
- 239000002184 metal Substances 0.000 description 13
- 239000002253 acid Substances 0.000 description 12
- 239000003960 organic solvent Substances 0.000 description 9
- 239000012071 phase Substances 0.000 description 9
- 229910052761 rare earth metal Inorganic materials 0.000 description 8
- 239000000243 solution Substances 0.000 description 8
- 238000010586 diagram Methods 0.000 description 6
- GRYLNZFGIOXLOG-UHFFFAOYSA-N Nitric acid Chemical compound O[N+]([O-])=O GRYLNZFGIOXLOG-UHFFFAOYSA-N 0.000 description 5
- 230000015572 biosynthetic process Effects 0.000 description 5
- 150000002739 metals Chemical class 0.000 description 5
- 229910017604 nitric acid Inorganic materials 0.000 description 5
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 4
- 235000011114 ammonium hydroxide Nutrition 0.000 description 4
- 230000000694 effects Effects 0.000 description 4
- 229910052739 hydrogen Inorganic materials 0.000 description 4
- 239000001257 hydrogen Substances 0.000 description 4
- 239000007788 liquid Substances 0.000 description 4
- 229910052759 nickel Inorganic materials 0.000 description 4
- 230000008929 regeneration Effects 0.000 description 4
- 238000011069 regeneration method Methods 0.000 description 4
- 229910002651 NO3 Inorganic materials 0.000 description 3
- 229910052779 Neodymium Inorganic materials 0.000 description 3
- NHNBFGGVMKEFGY-UHFFFAOYSA-N Nitrate Chemical compound [O-][N+]([O-])=O NHNBFGGVMKEFGY-UHFFFAOYSA-N 0.000 description 3
- 229910052772 Samarium Inorganic materials 0.000 description 3
- 239000013078 crystal Substances 0.000 description 3
- 238000010790 dilution Methods 0.000 description 3
- 239000012895 dilution Substances 0.000 description 3
- 159000000011 group IA salts Chemical class 0.000 description 3
- 238000002347 injection Methods 0.000 description 3
- 239000007924 injection Substances 0.000 description 3
- 150000007524 organic acids Chemical class 0.000 description 3
- 150000002910 rare earth metals Chemical class 0.000 description 3
- 150000004671 saturated fatty acids Chemical group 0.000 description 3
- 150000003512 tertiary amines Chemical class 0.000 description 3
- FYGHSUNMUKGBRK-UHFFFAOYSA-N 1,2,3-trimethylbenzene Chemical compound CC1=CC=CC(C)=C1C FYGHSUNMUKGBRK-UHFFFAOYSA-N 0.000 description 2
- PAWQVTBBRAZDMG-UHFFFAOYSA-N 2-(3-bromo-2-fluorophenyl)acetic acid Chemical compound OC(=O)CC1=CC=CC(Br)=C1F PAWQVTBBRAZDMG-UHFFFAOYSA-N 0.000 description 2
- NGDQQLAVJWUYSF-UHFFFAOYSA-N 4-methyl-2-phenyl-1,3-thiazole-5-sulfonyl chloride Chemical compound S1C(S(Cl)(=O)=O)=C(C)N=C1C1=CC=CC=C1 NGDQQLAVJWUYSF-UHFFFAOYSA-N 0.000 description 2
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical group [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 2
- 125000000217 alkyl group Chemical group 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-N ammonia Natural products N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- 239000000284 extract Substances 0.000 description 2
- GPRLSGONYQIRFK-UHFFFAOYSA-N hydron Chemical compound [H+] GPRLSGONYQIRFK-UHFFFAOYSA-N 0.000 description 2
- XLYOFNOQVPJJNP-UHFFFAOYSA-M hydroxide Chemical compound [OH-] XLYOFNOQVPJJNP-UHFFFAOYSA-M 0.000 description 2
- 125000002496 methyl group Chemical group [H]C([H])([H])* 0.000 description 2
- IOQPZZOEVPZRBK-UHFFFAOYSA-N octan-1-amine Chemical compound CCCCCCCCN IOQPZZOEVPZRBK-UHFFFAOYSA-N 0.000 description 2
- 238000001139 pH measurement Methods 0.000 description 2
- 238000000746 purification Methods 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- 238000005201 scrubbing Methods 0.000 description 2
- YKGBNAGNNUEZQC-UHFFFAOYSA-N 6-methyl-n,n-bis(6-methylheptyl)heptan-1-amine Chemical compound CC(C)CCCCCN(CCCCCC(C)C)CCCCCC(C)C YKGBNAGNNUEZQC-UHFFFAOYSA-N 0.000 description 1
- NLXLAEXVIDQMFP-UHFFFAOYSA-N Ammonium chloride Substances [NH4+].[Cl-] NLXLAEXVIDQMFP-UHFFFAOYSA-N 0.000 description 1
- SAIKULLUBZKPDA-UHFFFAOYSA-N Bis(2-ethylhexyl) amine Chemical compound CCCCC(CC)CNCC(CC)CCCC SAIKULLUBZKPDA-UHFFFAOYSA-N 0.000 description 1
- 239000004215 Carbon black (E152) Substances 0.000 description 1
- CTQNGGLPUBDAKN-UHFFFAOYSA-N O-Xylene Chemical compound CC1=CC=CC=C1C CTQNGGLPUBDAKN-UHFFFAOYSA-N 0.000 description 1
- 239000000654 additive Substances 0.000 description 1
- 230000000996 additive effect Effects 0.000 description 1
- 239000010953 base metal Substances 0.000 description 1
- ZLMKQJQJURXYLC-UHFFFAOYSA-N bis(2-ethylhexoxy)-oxophosphanium Chemical compound CCCCC(CC)CO[P+](=O)OCC(CC)CCCC ZLMKQJQJURXYLC-UHFFFAOYSA-N 0.000 description 1
- 150000001735 carboxylic acids Chemical class 0.000 description 1
- 230000007423 decrease Effects 0.000 description 1
- 230000007812 deficiency Effects 0.000 description 1
- SEGLCEQVOFDUPX-UHFFFAOYSA-N di-(2-ethylhexyl)phosphoric acid Chemical compound CCCCC(CC)COP(O)(=O)OCC(CC)CCCC SEGLCEQVOFDUPX-UHFFFAOYSA-N 0.000 description 1
- 238000005516 engineering process Methods 0.000 description 1
- 229930195733 hydrocarbon Natural products 0.000 description 1
- 150000002430 hydrocarbons Chemical class 0.000 description 1
- 239000012535 impurity Substances 0.000 description 1
- 238000009434 installation Methods 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 239000003350 kerosene Substances 0.000 description 1
- 238000003801 milling Methods 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 239000000203 mixture Substances 0.000 description 1
- 238000006386 neutralization reaction Methods 0.000 description 1
- 230000003472 neutralizing effect Effects 0.000 description 1
- 238000010979 pH adjustment Methods 0.000 description 1
- 239000003209 petroleum derivative Substances 0.000 description 1
- 239000002244 precipitate Substances 0.000 description 1
- 238000001556 precipitation Methods 0.000 description 1
- 239000000700 radioactive tracer Substances 0.000 description 1
- 239000012266 salt solution Substances 0.000 description 1
- 235000003441 saturated fatty acids Nutrition 0.000 description 1
- 238000007790 scraping Methods 0.000 description 1
- 150000003335 secondary amines Chemical class 0.000 description 1
- 238000004088 simulation Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000000126 substance Substances 0.000 description 1
- 239000008096 xylene Substances 0.000 description 1
- 229910052727 yttrium Inorganic materials 0.000 description 1
- VWQVUPCCIRVNHF-UHFFFAOYSA-N yttrium atom Chemical compound [Y] VWQVUPCCIRVNHF-UHFFFAOYSA-N 0.000 description 1
Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Landscapes
- Manufacture And Refinement Of Metals (AREA)
- Extraction Or Liquid Replacement (AREA)
Description
【発明の詳細な説明】 〔産業上の利用分野〕 本発明は複数種類の金属塩を含む水溶液から不純物とし
ての金属イオンを除去して目的金属イオンを回収し、あ
るいは通常の方法では分離が困難な金属イオンを分別回
収するためなどの目的で行なわれる溶媒抽出方法に関す
るものである。DETAILED DESCRIPTION OF THE INVENTION [Industrial field of application] The present invention removes metal ions as impurities from an aqueous solution containing a plurality of types of metal salts to recover target metal ions, or is difficult to separate by ordinary methods. The present invention relates to a solvent extraction method performed for the purpose of separately collecting various metal ions.
金属イオンを溶媒抽出方法によつて有機溶媒相に抽出す
る抽出剤の代表的なものとして有機酸性抽出剤が知ら
れ、広く使用されている。(新金属工業1975年12月号2
頁第1表参照) このような有機酸性抽出剤による金属の抽出反応は一般
式 nHA+M+nMAn+nH+‥‥(1) 〔但しHAは有機酸性抽出剤、Mは金属を示す〕で示され
るように金属イオンM+nが溶媒相中に抽出されると同時
に水素イオンが生成する。従つて(1)式の抽出反応が進
行すると水素イオン濃度が次第に増していき、抽出反応
は途中で止つてしまう。そこでこの反応を充分右辺に進
行させるためには生成してくる水素イオンを除去する必
要があり、そのため通常水相にアルカリを添加して中和
することが行なわれるが、アルカリの添加が過剰である
と水酸化物沈殿が生成したり、あるいは金属イオンと抽
出剤とからなる不溶性化合物を生成することがあり、こ
れら固形物は反応装置の管路等の閉塞を起す原因となつ
ていた。Organic acidic extractants are known and widely used as typical extractants for extracting metal ions into an organic solvent phase by a solvent extraction method. (Shin Metal Industry December 1975 Issue 2
(See Table 1 on page 1) The extraction reaction of metals with such organic acidic extractants is as shown by the general formula nHA + M + n MAn + nH + ... (1) [where HA is an organic acidic extractant and M is a metal] At the same time, metal ions M + n are extracted into the solvent phase, and at the same time hydrogen ions are generated. Therefore, as the extraction reaction of formula (1) proceeds, the hydrogen ion concentration gradually increases, and the extraction reaction stops halfway. Therefore, in order to proceed this reaction to the right side sufficiently, it is necessary to remove the generated hydrogen ions. Therefore, it is usual to add an alkali to the aqueous phase for neutralization, but the addition of alkali is excessive. In some cases, a hydroxide precipitate may be formed or an insoluble compound composed of a metal ion and an extractant may be formed, and these solid substances are the cause of clogging of the pipeline of the reactor.
この溶媒抽出法が多段向流装置を用いて行なわれる場合
は、溶媒が新たに注入される段では仮にPHが適正に制
御されたとしても、その段のみで供給されるアルカリが
抽出反応時に消費されるため次第以降はPHが低下して
しまう。従つて第2段以降の抽出段においても良好な抽
出反応を行なわせるためには結局各段毎にPHを測定
し、適量のアルカリを夫々の段に添加する必要があり、
抽出段数が多い場合には段数に相応するアルカリ注入装
置、PH測定装置や、これらを操作するための人員、電
力、設置場所等が必要であつた。When this solvent extraction method is performed using a multi-stage countercurrent device, even if PH is properly controlled at the stage where the solvent is newly injected, the alkali supplied only at that stage is consumed during the extraction reaction. As a result, the PH decreases after that. Therefore, in order to perform a good extraction reaction also in the second and subsequent extraction stages, it is necessary to measure the pH in each stage and add an appropriate amount of alkali to each stage.
When the number of extraction stages is large, it is necessary to have an alkali injection device, a PH measurement device, personnel for operating these devices, electric power, installation place, etc. corresponding to the number of extraction stages.
このようなアルカリの添加の過不足が起らないようにす
ることは実際上極めて困難である為特公昭55-49582 号
公報に述べられているように有機抽出剤を予めアルカリ
水溶液で処理したものを用い、水酸化物沈殿や不溶性化
合物の生成なしに抽出を行なう方法がある。It is extremely difficult in practice to prevent the excess or deficiency of the addition of such an alkali. Therefore, as described in JP-B-55-49582, the organic extractant is previously treated with an alkaline aqueous solution. There is a method of performing extraction without using hydroxide precipitation and insoluble compound formation.
然しながらこの方法では有機酸性抽出剤のアルカリ塩に
水に可溶性のものがあり、この場合アルカリ処理時に水
相側へそれが溶出してアルカリ塩が有効に働かず、又前
記アルカリ塩が有機相中に留まつても、その量が一定以
上に多いと、抽出時にやはり不溶性化合物を生成し、水
相へ直接アルカリを添加してPHを制御する方法と実質
上変らない結果をもたらすことがあり、必ずしも適切な
方法とは云えなかつた。However, in this method, some of the alkaline salts of the organic acidic extractant are soluble in water, and in this case, the alkaline salt does not work effectively because it elutes to the water phase side during the alkaline treatment, and the alkaline salt is contained in the organic phase. However, if the amount is more than a certain amount, an insoluble compound may still be formed during extraction, which may result in substantially the same result as the method of controlling the pH by directly adding an alkali to the aqueous phase, It was not always the right method.
本発明は複数種類の金属イオンを含む水溶液を有機酸性
抽出剤を用いて溶媒抽出する場合に、前記した欠点を解
消し、煩雑なPH制御することなしに溶媒抽出操作を行
ない且つPH制御不良に伴なつて発生する不溶性化合物
の生成をなくして安定な抽出操作を行なうことのできる
溶媒抽出方法を提供するとにある。The present invention eliminates the above-mentioned drawbacks when performing solvent extraction of an aqueous solution containing a plurality of types of metal ions using an organic acidic extractant, and performs solvent extraction operation without complicated PH control and results in poor pH control. Another object of the present invention is to provide a solvent extraction method capable of performing a stable extraction operation by eliminating the formation of an insoluble compound that is generated.
この目的を達成するために本発明は金属イオンを含有す
る水溶液から有機酸性抽出剤を用いて金属イオンを抽出
する溶媒抽出方法において、有機相中に前記有機酸性抽
出剤及びその希釈剤には溶解するが、水には難溶性であ
るアミンを共存させて抽出を行ない、次いで有機相中の
金属イオンを逆抽出して有機酸性抽出剤を再生した後、
アミン塩の残存する有機相にアルカリを添加し、アミン
塩をアミンに再生するようにしたものである。To achieve this object, the present invention provides a solvent extraction method of extracting metal ions from an aqueous solution containing metal ions using an organic acidic extractant, wherein the organic acidic extractant and its diluent are dissolved in an organic phase. However, extraction is carried out in the presence of a poorly soluble amine in water, and then metal ions in the organic phase are back-extracted to regenerate the organic acidic extractant,
In this method, an alkali is added to the remaining organic phase of the amine salt to regenerate the amine salt into the amine.
以下本発明の反応機構を簡単な例として金属イオンを含
有する水溶液として硝酸イツトリウムY(NO3)3水溶液を
有機酸性抽出剤HAと、その希釈剤と、共存するアミンと
して3級アミンR3Nとの混合有機相で抽出する場合につ
いて説明する。Y(NO3)3を含む水溶液の有機相への抽出
は次式(2)によつて行なわれる。As a simple example of the reaction mechanism of the present invention, an aqueous solution of yttrium nitrate Y (NO 3 ) 3 as an aqueous solution containing a metal ion is used as an organic acid extractant HA and its diluent, and a tertiary amine R 3 N as a coexisting amine. The case of extraction in a mixed organic phase with and will be described. The extraction of the aqueous solution containing Y (NO 3 ) 3 into the organic phase is performed according to the following formula (2).
Y(NO3)3+3HA→A3Y+3HNO3‥‥(2) これによつてYは有機相に抽出されるが、同時に生成す
るHNO3の濃度が逐次増加するが、このHNO3が3級アミン
と次式(3)により反応する。 Y (NO 3) 3 + 3HA → A 3 Y + 3HNO 3 ‥‥ (2) This Yotsute Y but is extracted into the organic phase, although the concentration of HNO 3 to produce simultaneously increases sequentially, the HNO 3 tertiary Reacts with amines according to the following formula (3).
HNO3+R3N→R3HN+・NO3 -‥‥(3) (3)式で生成した3級アミン塩R3HN+・NO3 -は有機溶媒相
中に溶解するが水相には難溶である。又、最初の硝酸イ
ツトリウム水溶液の遊離酸濃度が高く酸性を呈している
ときは、この遊離酸も同様な形態で有機相中に抽出され
てしまう。 HNO 3 + R 3 N → R 3 HN + · NO 3 - ‥‥ (3) (3) 3 amine salt produced in formula R 3 HN + · NO 3 - in is soluble in the organic solvent phase into water phase Is insoluble. When the concentration of free acid in the initial aqueous solution of yttrium nitrate is high and acidic, this free acid is also extracted into the organic phase in a similar form.
有機相中のYは酸、例えばHNO3を用いて次式(4)に従つ
て逆抽出が行なわれる。Y in the organic phase is back-extracted with an acid such as HNO 3 according to the following equation (4).
A3Y+3HNO3→3HA+Y(NO3)3‥‥(4) この反応によつて有機酸性抽出剤が再生され、Yは処理
対象水溶液から他の水相に移されたことになる。Yは逆
抽出された後有機相中に残つた3級アミン塩R3HN+・NO3 -
はアルカリ、例えばアンモニア水によつて3級アミンに
次式(5)に従つて再生される。A 3 Y + 3HNO 3 → 3HA + Y (NO 3 ) 3 (4) By this reaction, the organic acidic extractant is regenerated, and Y is transferred from the aqueous solution to be treated to another aqueous phase. Y is ZanTsuta tertiary amine salt in the organic phase after the back extraction R 3 HN + · NO 3 -
Is regenerated to the tertiary amine with an alkali such as aqueous ammonia according to the following formula (5).
R3HN+・NO3 -+NH4OH→R3N+NH4NO3+H2O‥(5) アルカリによるこのアミン塩の再生反応は、先にイツト
リウムの逆抽出で再生された有機酸性抽出剤との塩を形
成する反応に優先して行なわれるので、アミンと当量の
アルカリを添加することによつて(5)のみを優先的に行
なわせることが可能である。R 3 HN + · NO 3 - regeneration reaction of + NH 4 OH → R 3 N + NH 4 NO 3 + H 2 O ‥ (5) the amine salts with alkali, and previously played in stripping of yttrium organic acidic extractant Since it is carried out prior to the reaction for forming the salt of (3), it is possible to preferentially carry out only (5) by adding an equivalent amount of alkali to the amine.
(4)式で再生された有機酸性抽出剤HA及び(5)式で再生さ
れたアミンR3Nは前記(2)式の抽出剤及び(3)式の添加剤
として循環使用することができる。The organic acidic extractant HA regenerated by the formula (4) and the amine R 3 N regenerated by the formula (5) can be reused as the extractant of the formula (2) and the additive of the formula (3). .
本発明において使用される有機酸性抽出剤とは、その分
子がもつ活性なHが金属イオンとイオン交換を行なうこ
とによつて、金属イオンを有機相中へ抽出する抽出剤で
あつて、例えばリン酸ビス-2-エチルヘキシルリン酸(D
2EHPA)や、2-エチルヘキシルホスホン酸モノ-2-エチ
ルヘキシル等のリン酸エステル類 構造式 (R1,R2,R3はアルキル基で少なくとも1個はメチル基
である) 炭素鎖長9,10,11のうちの一つ以上の第3級飽和脂肪
酸(商品名バーサチツク・アシツド、シエル化学社
製)、ハフテン酸等のカルボン酸が代表的なものであ
る。The organic acidic extractant used in the present invention is an extractant that extracts metal ions into the organic phase by virtue of the active H of the molecule carrying out ion exchange with the metal ions. Acid bis-2-ethylhexyl phosphate (D
2EHPA) and 2-ethylhexylphosphonate mono-2-ethylhexyl, etc. (R 1 , R 2 and R 3 are alkyl groups and at least one is a methyl group) One or more tertiary saturated fatty acids having carbon chain lengths of 9, 10 and 11 (trade name: Versatik Acid, Shell) Typical examples are carboxylic acids such as those manufactured by Kagaku Co., Ltd., and hafthenic acid.
本発明で使用されるアミンは使用する有機酸性抽出剤及
びその希釈剤には溶解するが、水には難溶性であること
が必要であり、例えばトリノルマルオクチルアミン(THO
A)などの第3級アミンが好適で、この他トリイソオクチ
ルアミンやジ-2-エチルヘキシルアミンのような2級ア
ミンも使用可能である。使用するアミンが有機酸性抽出
剤及び希釈剤に不溶であるが水に可溶性である場合は水
相中にアミンが溶出してくるので、有機溶媒のPH制御
能力がなくなる。又、このアミンが溶媒相には可溶で且
つ水にも可溶性であると、有機溶媒はある程度PH制御
能力を持つが、水相中にアミンが溶出するために、PH
制御能力は徐々に失なわれて行き、本発明の目的が達成
されない。The amine used in the present invention is soluble in the organic acidic extractant and its diluent to be used, but it is necessary that it is sparingly soluble in water, for example, trinormal octylamine (THO).
Tertiary amines such as A) are suitable, and secondary amines such as triisooctylamine and di-2-ethylhexylamine can also be used. When the amine used is insoluble in the organic acidic extractant and the diluent but is soluble in water, the amine will elute in the aqueous phase, and the pH control ability of the organic solvent will be lost. Further, when this amine is soluble in the solvent phase and also in water, the organic solvent has a PH control ability to some extent, but since the amine is eluted in the aqueous phase, PH
The controllability is gradually lost and the object of the present invention is not achieved.
本発明を実施するには前記有機酸性抽出剤に適量の前記
したようなアミンを好ましくはほぼ等モルで添加し必要
に応じて例えばケロシン、キシレンなどの石油系炭化水
素油を希釈剤として希釈して有機相の粘性を下げ処理対
象とする金属イオンを含む水溶液と接触させれば良い。
このとき処理対象液が複数の金属イオンを含んでいて、
これを選択的に抽出分離をする場合には(イ)有機溶媒相
中の有機酸性抽出剤に対するアミンのモル比を変化させ
るか(ロ)有機酸性抽出剤とアミンのモル比は一定でモル
比は1:1程度で希釈剤の量を変えて有機酸性抽出剤の
濃度を変化させることによつて金属元素の分配比を変え
ることができる。又、単独の金属イオンのみを含んでい
る場合でも前記(イ)又は(ロ)の方法によつて分配比が高く
なるように選択できる。In order to carry out the present invention, a suitable amount of the above-mentioned amine is added to the organic acidic extractant, preferably in approximately equimolar amounts, and petroleum hydrocarbon oil such as kerosene and xylene is diluted as a diluent as needed. Then, the viscosity of the organic phase is reduced to bring the organic phase into contact with an aqueous solution containing metal ions to be treated.
At this time, the liquid to be treated contains a plurality of metal ions,
In the case of selective extraction and separation, (a) is the molar ratio of the amine to the organic acidic extractant in the organic solvent phase changed? (B) The molar ratio of the organic acidic extractant and the amine is constant Can change the distribution ratio of the metal element by changing the amount of the diluent and changing the concentration of the organic acidic extractant at about 1: 1. Further, even when it contains only a single metal ion, the distribution ratio can be increased by the method (a) or (b).
しかし前記(イ)の方法においてはアミンの濃度が低くな
り過ぎると(3)式で例示した生成する水素イオンを充分
捕えるだけのアミンが不足し、又アミンの濃度が高すぎ
ると水素イオンの捕獲が進行しすぎて、PH制御効果が
有効に発揮できない場合があるので(ロ)の方法がより適
当である。However, in the above method (a), when the amine concentration is too low, there is insufficient amine to capture the generated hydrogen ions exemplified in formula (3), and when the amine concentration is too high, the hydrogen ion capture In some cases, the pH control effect cannot be effectively exerted due to excessive progress, and the method (b) is more suitable.
次に本発明の方法を適用して多数の金属イオンを含有す
る水溶液、例えば希土類含有鉱石を硝酸で溶解した水溶
液についてその抽出条件を種々変更した場合の各金属の
分配比、分離係数等の変化について説明する。Next, the distribution ratio of each metal, the change of the separation coefficient, etc., when the extraction conditions are variously changed for an aqueous solution containing a large number of metal ions by applying the method of the present invention, for example, an aqueous solution obtained by dissolving a rare earth-containing ore with nitric acid Will be described.
第1表に示す成分を含有するPH1〜6の硝酸塩水溶液
50 mlを、有機相としてトリメチルベンゼンを主体とす
る炭化水素油からなる希釈剤(商品名シエルゾールAシ
エル化学社製)中に15容量%の構造式 「R1、R2、R3はアルキル基で少なくとも1個はメチル基
である炭素鎖長10の第3級飽和脂肪酸90重量%、残部が
同第2級飽和脂肪酸からなる有機酸性抽出剤(シエルケ
ミカル社、商品名バーサチツク10,以下「VA-10」と云
う)」と35容量%のトリノルマルオクチルアミン(以下
「TNOA」と云う)(VA-10とほぼ同等モルに相当)を含む
溶媒50 mlとを室温にて分液漏斗中にて10分間振盪し、
分液後の水相のPHを測定した。原液のPHと抽出後の
PHとの関係を第1図に示す。Aqueous PH1-6 nitrate solutions containing the components shown in Table 1.
50 ml of a structural formula of 15% by volume in a diluent (trade name: Cielsol A, manufactured by Ciel Chemical Co., Ltd.) consisting of a hydrocarbon oil mainly containing trimethylbenzene as an organic phase. "R 1 , R 2 and R 3 are alkyl groups and at least one is a methyl group. 90% by weight of a tertiary saturated fatty acid having a carbon chain length of 10%, the balance being an organic acidic extractant (secondary saturated fatty acid) Ciel Chemical Co., trade name Versatik 10, hereinafter referred to as "VA-10") "and a solvent containing 35% by volume of trinormal octylamine (hereinafter referred to as" TNOA ") (corresponding to approximately the same moles as VA-10). Shake 50 ml with 10 min in a separatory funnel at room temperature,
The pH of the aqueous phase after liquid separation was measured. The relationship between the pH of the undiluted solution and the pH after extraction is shown in FIG.
第1図から明らかなように抽出前のPHの高低に拘らず
抽出後のPHはほぼ一定の値を示す。これは(2)式で例
示したように反応で生成する酸が(3)式で例示したよう
にアミンと反応してアミン塩となり、又原液に予め存在
する水素イオンも同様な形で有機相にとりこまれるため
であつて、従つて抽出に際して酸を中和するためのアル
カリを添加することが不要になる。 As is clear from FIG. 1, the PH after extraction shows a substantially constant value regardless of the level of PH before extraction. This is because the acid generated in the reaction as illustrated in formula (2) reacts with an amine to form an amine salt as illustrated in formula (3), and hydrogen ions that already exist in the undiluted solution have the same form as the organic phase. Therefore, it becomes unnecessary to add an alkali for neutralizing the acid at the time of extraction.
このように本発明方法の抽出では抽出条件が一定であれ
ば抽出反応後のPHは原液のPHの変化に拘らず一定な
ので、分配比、分離係数も一定となる。As described above, in the extraction of the method of the present invention, if the extraction conditions are constant, the PH after the extraction reaction is constant regardless of changes in the pH of the stock solution, so that the distribution ratio and the separation coefficient are also constant.
原液のPHと抽出後の水相及び有機相の各金属濃度を測
定して求めた各金属の分配比との関係を第2図に、原液
のPHと各金属間の分離係数との関係を第3図に示す。
第2図及び第3図から明らかなように原液のPHの高低
に拘らず分配率は夫夫の金属についてほぼ一定となるの
で第3図に示す各金属間の分離係数もほぼ一定となる。Fig. 2 shows the relationship between the PH of the stock solution and the distribution ratio of each metal obtained by measuring the concentration of each metal in the aqueous phase and the organic phase after extraction. Fig. 2 shows the relationship between the PH of the stock solution and the separation coefficient between the metals. It is shown in FIG.
As is clear from FIGS. 2 and 3, the distribution ratio for each metal is almost constant regardless of the pH of the stock solution, so the separation coefficient between the metals shown in FIG. 3 is also almost constant.
次いで有機酸性抽出剤としてのVA-10と、アミンとし
てのTNOAのモル比を1:1に保ちVA-10の濃度を10〜3
0容量%に変化させて、第1表の原液の等容量を用いて
抽出したときの有機酸性抽出剤の濃度と各金属の分配比
の関係及び抽出後の水相のPHとの関係を第4図に、又
有機酸性抽出剤の濃度と各金属間の分離係数との関係を
第5図に示す。第4図から判るように抽出剤の濃度が変
化しても、又原液のPHが変化してもPH6前後で大差
はないが、分配比は大幅に変化して抽出剤の濃度が高い
方が分配比は大となる。しかしながら第5図に示される
ように分離係数は抽出剤の濃度に拘らずほぼ一定であ
る。Then, the molar ratio of VA-10 as an organic acidic extractant and TNOA as an amine was kept at 1: 1 and the concentration of VA-10 was 10-3.
The relationship between the concentration of the organic acidic extractant and the distribution ratio of each metal when extracted with an equal volume of the stock solution in Table 1 and the relationship between the pH of the aqueous phase after extraction were changed to 0% by volume. FIG. 4 shows the relationship between the concentration of the organic acid extractant and the separation coefficient between metals, and FIG. As can be seen from Fig. 4, even if the concentration of the extractant changes or the pH of the stock solution changes, there is no great difference around PH6, but the distribution ratio changes greatly and the concentration of the extractant is higher. The distribution ratio becomes large. However, as shown in FIG. 5, the separation coefficient is almost constant regardless of the concentration of the extractant.
一方有機相の抽出剤濃度やアミンの濃度が一定でも処理
原液中の濃度を変えることによつて分配比を変えること
ができる。第1表に示す原液の希土類元素の合計量20.6
6g/を基準として、これを水で希釈して濃度を1/5にま
で変化させ、有機溶媒としてはVA-10とTNOAを等モル比
で混合し、VA-10の濃度を15容量%として水相と溶媒相
を同量振盪したときの原液の希釈率と分配比の関係を第
6図に、分離係数との関係を第7図に示す。この場合通
常の抽出反応が原液濃度が薄い方が分配比が高いのと反
対に、第6図に示されるように原液濃度が高いほど分配
比が高くなると云う特徴がある。しかしながら分離係数
は第7図に示されるように原液濃度の変化による差はあ
まり大きくない。On the other hand, even if the concentration of the extractant in the organic phase and the concentration of the amine are constant, the distribution ratio can be changed by changing the concentration in the stock solution for treatment. Total amount of rare earth elements in undiluted solution shown in Table 1 20.6
Based on 6 g /, this is diluted with water to change the concentration to 1/5, and VA-10 and TNOA are mixed as an organic solvent at an equimolar ratio, and the concentration of VA-10 is set to 15% by volume. FIG. 6 shows the relationship between the dilution ratio of the stock solution and the distribution ratio when the same amount of the aqueous phase and the solvent phase was shaken, and FIG. 7 shows the relationship with the separation coefficient. In this case, an ordinary extraction reaction has a characteristic that the distribution ratio is higher when the concentration of the stock solution is lower, whereas the distribution ratio is higher when the concentration of the stock solution is higher, as shown in FIG. However, as shown in FIG. 7, the separation coefficient is not so different due to the change in the concentration of the stock solution.
金属イオンを抽出後の有機溶媒の再生には公知の手段の
酸によつて逆抽出を行なう。使用する酸は有機酸性抽出
剤より強い酸性のものを用いれば良く、酸の濃度、有機
相との混合比は酸の種類によつても異なるが、例えば2
規定の硝酸を有機相と等容量用いる。To regenerate the organic solvent after extracting the metal ions, back extraction is carried out with an acid by a known means. The acid used may be one that is stronger in acidity than the organic acid extractant, and the concentration of acid and the mixing ratio with the organic phase differ depending on the type of acid.
Use the same volume of normal nitric acid as the organic phase.
次いで金属イオンが除去された有機溶媒はアルカリ水溶
液を加えて再生処理を行なう。使用するアルカリは溶媒
中に存在するアミンよりも塩基性の強いものを用い、そ
の量はアミンと等モルのアルカリが必要である。例えば
TNOA 1 mol/を含む有機相1を再生するには濃度30
%のNH4OHを約63 ml必要とする。このとき所定濃度のア
ルカリ水溶液を用いることによつて所望濃度の塩の水溶
液を得ることができる。例えば再生すべきアミン塩がア
ミンの硝酸塩でるならば、再生を濃厚なアンモニア水溶
液を用いれば、反応後の水溶液から容易に硝酸アンモニ
ウムの結晶を回収し系外に出すことができる。Next, the organic solvent from which the metal ions have been removed is subjected to a regeneration treatment by adding an alkaline aqueous solution. The alkali used has a stronger basicity than the amine present in the solvent, and the amount of the alkali needs to be equimolar to the amine. For example
A concentration of 30 to regenerate the organic phase 1 containing 1 mol / TNOA
Requires about 63 ml of% NH 4 OH. At this time, an aqueous salt solution having a desired concentration can be obtained by using an alkaline aqueous solution having a predetermined concentration. For example, when the amine salt to be regenerated is a nitrate of amine, ammonium nitrate crystals can be easily recovered from the aqueous solution after the reaction and taken out of the system by using a concentrated aqueous ammonia solution for regeneration.
このようにして有機溶媒中から抽出した金属イオンが逆
抽出されて除去され、更にアミン塩はアミンに再生され
て一般には希釈剤中に有機酸性抽出剤とアミンが共存し
た状態になるのでこれはそのまゝ本発明で用いられる有
機相として循環使用することができる。In this way, the metal ions extracted from the organic solvent are back-extracted and removed, and the amine salt is regenerated to the amine, so that the organic acidic extractant and the amine generally coexist in the diluent. As such, it can be recycled as the organic phase used in the present invention.
前記した本発明の適用例で述でたような多種の希土類イ
オンを含むような水溶液は溶媒抽出法を多段に適用する
ことによつて分離係数が1より大きな2種以上の金属を
分離することができる。例えばSmとNdの分離係数は約
2.3だが、これらを効率良く分離することができる。The aqueous solution containing various kinds of rare earth ions as described in the application example of the present invention can be separated into two or more kinds of metals having a separation coefficient of more than 1 by applying the solvent extraction method in multiple stages. You can For example, the separation coefficient for Sm and Nd is about 2.3, but they can be separated efficiently.
実施例1 NiとCoを含有する水溶液を対象として溶媒抽出を行なつ
た。原液としてNi 41.0g/、Co 17.2g/を含有するP
H3の硝酸酸性の水溶液、溶媒としてはジ-2-エチルヘ
キシル・フオスフオリツクアシツド(大八化学製PC-
88A)33.4容量%(溶媒1中に1モル含有)、TNOA
35.4容量%(1mol/溶媒)を含み、残部シエルゾール
Aからなる溶媒を夫々50 ml宛分液漏斗にとり、10分間
振盪後静置し、水相と有機相中のNi、Co含有量を分析し
た。この際有機相中の値については、この有機相を等容
量の4N硝酸と分液漏斗中で10分間振盪し、得られた逆
抽出液について分析して求めた。この有機相は再度同様
に逆抽出を行なつたが一回逆抽出を行なつたあとの残存
金属イオン含有量はNi,Co共0.1 g/以下であつた。最
初の原液のPHを4及び5としたときのものも同様に処
理した結果を併せて第2表に示す。Example 1 Solvent extraction was performed on an aqueous solution containing Ni and Co. P containing Ni 41.0 g / and Co 17.2 g / as undiluted solution
An aqueous solution of H3 in nitric acid is used as a solvent, and as a solvent, di-2-ethylhexyl phosphite hydrate (PC-
88A) 33.4% by volume (containing 1 mol in solvent 1), TNOA
The solvent containing 35.4% by volume (1 mol / solvent) and the balance consisting of Sielsol A was placed in a separating funnel for 50 ml, shaken for 10 minutes and allowed to stand, and the Ni and Co contents in the aqueous phase and the organic phase were analyzed. . At this time, the value in the organic phase was determined by shaking the organic phase with an equal volume of 4N nitric acid in a separating funnel for 10 minutes and analyzing the obtained back extract. This organic phase was back-extracted again in the same manner, but the content of residual metal ions after one back-extraction was 0.1 g / Ni or less for both Ni and Co. Table 2 also shows the results of the same treatment when the pH of the first stock solution was set to 4 and 5.
第2表の結果から、原液のPHに拘らず得られた抽出結
果はほぼ同じであり、得られた水相のPHは共に6.1、
分配比はNi 0.013、Co8.56で分離係数Co/Ni=6.6×102
であつた。 From the results of Table 2, the extraction results obtained were almost the same regardless of the pH of the undiluted solution, and the PH of the obtained aqueous phase was 6.1,
The distribution ratio is Ni 0.013, Co 8.56, and the separation coefficient Co / Ni = 6.6 × 10 2
It was.
先に逆抽出の済んだ有機相50ml(0.05 molのTNOA硝酸塩
含有)は濃度30重量%のアンモニア水2.8 g(≒3.3ml、
0.05 mol)と10分間振盪した。この結果有機相中のアミ
ンは再生され、水相としてはNH4NO3結晶を含む硝酸アン
モニア水溶液が得られた。再生用のアンモニア水は10倍
に希釈した水溶液33 mlを用いても同様に再生できた
が、その場合は水相中にはNH4NO3の結晶は析出しなかつ
た。50 ml of the organic phase that had been back-extracted (containing 0.05 mol of TNOA nitrate) was 2.8 g of ammonia water with a concentration of 30% by weight (≈3.3 ml,
(0.05 mol) and shaken for 10 minutes. As a result, the amine in the organic phase was regenerated and an aqueous ammonium nitrate solution containing NH 4 NO 3 crystals was obtained as the aqueous phase. Ammonia water for regeneration could be regenerated by using 33 ml of a 10-fold diluted aqueous solution, but in that case, no NH 4 NO 3 crystals were precipitated in the aqueous phase.
以上のように再生した溶媒は再び原液と振盪して抽出試
験を行なつたが抽出後のPH、Ni、Coの分配比、分離係
数共新たな溶媒を用いた場合と同じ値が得られた。The solvent regenerated as described above was shaken again with the stock solution and an extraction test was conducted, but after the extraction, the distribution ratios of PH, Ni, Co, and the separation coefficient were the same as those obtained when a new solvent was used. .
実施例2 本発明方法は多段向流溶媒抽出法に応用した場合、その
効果の大きさを明瞭に確認することができる。本実施例
では抽出段3段、スクラツピング段3段を有する多段向
流溶媒抽出装置において、アール・イー・トレイバル
(R.E.TREYBAL)著リキツド・エクストラクシヨン370頁9.
6 図に従い、本発明を適用した場合のバツチシユミレー
シヨンテストを行つた。この場合処理対象液としては、
第1表に示す希土類塩含有水溶液を用いSmをNdから極力
分離して回収するように対象元素を絞つて分析した。そ
の具体的方法を第8図にSm,Ndの濃度、濃度比等の関係
を第9図に示す。Example 2 When the method of the present invention is applied to a multistage countercurrent solvent extraction method, the magnitude of its effect can be clearly confirmed. In this embodiment, a multi-stage countercurrent solvent extraction apparatus having three extraction stages and three scraping stages is used as an ER tracer.
(RETREY BAL) by Liquid Extraction, page 370 9.
6 A batch simulation test was carried out according to the present invention when the present invention was applied. In this case, as the liquid to be treated,
The rare earth salt-containing aqueous solution shown in Table 1 was used to analyze the target elements so that Sm was separated from Nd as much as possible and recovered. The specific method is shown in FIG. 8 and the relationship between the concentrations of Sm and Nd, the concentration ratio, etc. is shown in FIG.
第8図(a)において「1」はVA-10 15容量%と等モルのTNO
Aを含み、残部シエルゾールAから成る溶媒50 ml、「2」
はPH5.76に調整した第1表の組成の原液25 ml、「3」
は0.1 規定の濃度の硝酸水溶液25 mlを夫々注入するこ
とを意味し各円は分液漏斗中で室温で10分間振盪を行な
うことを意味し、円内の数字は振盪後の水相のPH、
「→」は水相の注入、 は有機相の注入を示している。In Fig. 8 (a), "1" is TNO of equimolar to VA-10 15% by volume.
50 ml of a solvent containing A and the balance Sielsol A, "2"
Is a stock solution of the composition shown in Table 1 adjusted to pH 5.76, 25 ml, "3"
Means to inject 25 ml of nitric acid aqueous solution with a concentration of 0.1 N each, and each circle means to shake for 10 minutes at room temperature in a separating funnel, and the numbers in the circle mean the pH of the aqueous phase after shaking. ,
"→" is the injection of the aqueous phase, Indicates the injection of the organic phase.
第8図(b)のI,II,III,I′,II′,III′(多段向流
溶媒抽出法における段数)の各数字に第8図(a)の下方に
記載されたI,II,III等と対応している。The numbers I, II, III, I ', II', and III '(the number of stages in the multistage countercurrent solvent extraction method) in Fig. 8 (b) indicate I and II described below Fig. 8 (a). , III, etc.
第8図(a)の値から抽出段のPHは5.8前後に、スク
ラビング段のPHは平均で約5.3の値に制御されてい
ることが判る。又、各段より得られた水相、有機相中の
Sm、Ndの濃度及びSm/Nd比を第9図(a)、(b)に示した。S
m/Nd=16g/2.5 g/=6.4 の原液を用いても僅か6段
の段数でSm/Nd≒80までSmで精製されている。From the values in FIG. 8 (a), it can be seen that the PH of the extraction stage is controlled to around 5.8 and the PH of the scrubbing stage is controlled to an average value of about 5.3. In addition, in the aqueous phase and organic phase obtained from each stage
The concentrations of Sm and Nd and the Sm / Nd ratio are shown in FIGS. 9 (a) and 9 (b). S
Even with a stock solution of m / Nd = 16 g / 2.5 g / = 6.4, it was purified with Sm up to Sm / Nd≈80 in only 6 steps.
以上の実施例のいずれにおいても不溶性化合物の生成は
認められなかつた。又、有機酸性抽出剤としてリン酸エ
ステル系の抽出剤を用いた場合も同様の分離効果が得ら
れ、不溶性化合物の生成は認められなかつた。No formation of insoluble compounds was observed in any of the above examples. Also, when a phosphoric acid ester-based extractant was used as the organic acidic extractant, the same separation effect was obtained, and no formation of an insoluble compound was observed.
以上詳細に説明したように本発明によれば従来の酸性抽
出剤を用いた金属イオンの抽出に不可欠であつた抽出反
応時のアルカリ添加によるPH調節を全く不要とし、抽
出操作上で多くの問題を生ずる不溶性化合物の生成をな
くし、多段溶媒抽出を効率良く安定に行なうことができ
る。As described in detail above, according to the present invention, pH adjustment by alkali addition during the extraction reaction, which is indispensable for extraction of metal ions using a conventional acidic extractant, is completely unnecessary, and many problems occur in the extraction operation. It is possible to eliminate the formation of an insoluble compound that gives rise to a multistage solvent extraction efficiently and stably.
従つて通常の卑金属類の相互分離、精製は勿論多段向流
溶媒抽出法の採用が不可欠な希土類元素の相互分離・精
製もPH制御が自動的に行われ、PH測定や制御機器が
すべて不要でそのための運転コスト、スペースが不要で
且つこれらの故障による操業中止等も避けられ、又各抽
出段がPH制御不完全な場合に比して有効に働くため必
要な段数も減少させることが可能であり、高純度が必要
とされる希土類元素も安定して製造することができ、そ
の工業的価値は大なるものがある。Therefore, PH control is automatically performed not only for the mutual separation and purification of ordinary base metals but also for the mutual separation and purification of rare earth elements, which requires the use of a multi-stage countercurrent solvent extraction method, and PH measurement and control equipment are all unnecessary. Therefore, operating cost and space are not required, operation stoppage due to these failures can be avoided, and the number of required stages can be reduced because each extraction stage works more effectively than when the PH control is incomplete. In addition, rare earth elements that require high purity can be stably produced, and their industrial value is great.
第1図は第1表の原液のPHを1〜6と変化させて抽出
のための振盪後の水相のPHと、原液のPHとの関係を
示した図、第2図は原液のPHと各元素の分配比との関
係を示した図、第3図は原液のPHと分離係数との関係
を示した図、第4図はVA-10濃度に対する、振盪後の分
配比と、水相のPHとの関係を示した図、第5図はVA-1
0濃度と分離係数との関係を示した図、第6図は原液の
希釈率に対する分配比と、水相のPHとの関係を示した
図、第7図は原液の希釈率に対する分離係数の関係を示
した図、第8図(a)は抽出3段、スクラビング段3段の
6段向流溶媒抽出方法と同様のバツチシユミレーシヨン
テストの操作方法と水相のPHを示した図、第8図(b)
は同図(a)に相当する6段向流溶媒抽出法を示す図、第
9図(a)は第8図の各段における水相中の希土濃度とSm/
Nd比を示した図、第9図(b)は第8図の各段における有
機相中の希土濃度とSm/Nd比を示した図である。FIG. 1 is a diagram showing the relationship between the PH of the stock solution after shaking by changing the PH of the stock solution in Table 1 to 1 to 6 and the PH of the stock solution, and FIG. 2 is the PH of the stock solution. Fig. 3 shows the relationship between the distribution ratio of each element and each element, Fig. 3 shows the relationship between the PH of the undiluted solution and the separation coefficient, and Fig. 4 shows the distribution ratio after shaking against the VA-10 concentration and water. Figure 5 shows the relationship between the phase and PH. Figure 5 shows VA-1.
Fig. 6 shows the relationship between the 0 concentration and the separation coefficient, Fig. 6 shows the relationship between the distribution ratio with respect to the dilution rate of the stock solution, and PH of the aqueous phase, and Fig. 7 shows the separation coefficient with respect to the dilution rate of the stock solution. FIG. 8 (a) is a diagram showing the relationship, and FIG. 8 (a) is a diagram showing a pH of the aqueous phase and an operation method of the batch milling test similar to the six-stage countercurrent solvent extraction method of three-stage extraction and three-stage scrubbing stage. , Fig. 8 (b)
Is a diagram showing a six-stage countercurrent solvent extraction method corresponding to Fig. 9 (a), and Fig. 9 (a) is the rare earth concentration and Sm / in the aqueous phase at each stage in Fig. 8.
FIG. 9 (b) is a diagram showing the Nd ratio, and FIG. 9 (b) is a diagram showing the rare earth concentration in the organic phase and the Sm / Nd ratio in each stage of FIG.
Claims (2)
抽出剤を用いて金属イオンを抽出する溶媒抽出方法にお
いて、有機相中に前記有機酸性抽出剤及びその希釈剤に
は溶解するが水には難溶性であるアミンを共存させて金
属イオンを抽出し、次いで有機相中の金属イオンを逆抽
出して有機酸性抽出剤を再生した後、アミン塩の残存す
る有機相にアルカリを添加しアミン塩をアミンに再生す
ることを特徴とする溶媒抽出方法。1. A solvent extraction method for extracting metal ions from an aqueous solution containing metal ions using an organic acidic extractant, which is soluble in the organic acidic extractant and its diluent in the organic phase, but in water. After extracting the metal ions in the coexistence of a poorly soluble amine and then back-extracting the metal ions in the organic phase to regenerate the organic acidic extractant, an alkali is added to the organic phase in which the amine salt remains to add the amine salt. A method for extracting a solvent, which comprises regenerating the compound into an amine.
カルボン酸であることを特徴とする特許請求の範囲(1)
項記載の溶媒抽出方法。2. The organic acidic extractant is an acidic phosphoric acid ester or a carboxylic acid.
The solvent extraction method as described in the item.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP61181447A JPH0643620B2 (en) | 1986-07-31 | 1986-07-31 | Solvent extraction method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP61181447A JPH0643620B2 (en) | 1986-07-31 | 1986-07-31 | Solvent extraction method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS6338534A JPS6338534A (en) | 1988-02-19 |
| JPH0643620B2 true JPH0643620B2 (en) | 1994-06-08 |
Family
ID=16100928
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP61181447A Expired - Lifetime JPH0643620B2 (en) | 1986-07-31 | 1986-07-31 | Solvent extraction method |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPH0643620B2 (en) |
-
1986
- 1986-07-31 JP JP61181447A patent/JPH0643620B2/en not_active Expired - Lifetime
Also Published As
| Publication number | Publication date |
|---|---|
| JPS6338534A (en) | 1988-02-19 |
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