JP2024118003A - Method for producing cobalt aqueous solution - Google Patents
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本発明は、コバルト水溶液の製造方法に関し、特にニッケル及びコバルトを含んだ水溶液に対して酸性抽出剤を用いてこれら金属を相互に分離することで低マグネシウム濃度のコバルト水溶液を製造する方法に関する。 The present invention relates to a method for producing an aqueous cobalt solution, and in particular to a method for producing an aqueous cobalt solution with a low magnesium concentration by separating nickel and cobalt from each other using an acidic extractant in an aqueous solution containing these metals.
コバルトは、特殊鋼や磁性材料の合金用元素等の用途で広く利用されている。例えば特殊鋼としては、コバルトの優れた耐摩耗性や耐熱性を活かして航空宇宙、発電機、特殊工具の分野でコバルトを含んだ鋼材が用いられており、磁性材料の合金用元素としては、コバルトを含んだ強磁性合金材料が小型ヘッドホンや小型モーター等に用いられている。コバルトは更にリチウムイオン二次電池の正極材の原料としても利用されている。 Cobalt is widely used in applications such as special steels and as an alloying element for magnetic materials. For example, in the field of special steels, steel materials containing cobalt are used in the fields of aerospace, generators, and special tools, taking advantage of cobalt's excellent wear resistance and heat resistance, and as an alloying element in magnetic materials, ferromagnetic alloy materials containing cobalt are used in small headphones, small motors, etc. Cobalt is also used as a raw material for the positive electrode material of lithium-ion secondary batteries.
鉱物資源としてのコバルトは、ニッケルに付随して含まれることが多く、コバルトはニッケル製錬の副産物として製造されるものが大半を占めている。そのため、コバルトの製造においては、ニッケルのほか、種々の不純物元素からコバルトを効率的に分離する技術が求められる。複数の金属元素を含む水溶液に対して金属を相互に分離する技術としては、溶媒抽出法、沈殿法、イオン交換法などを挙げることができるが、これらの中では溶媒抽出法が簡易な設備で効率よく金属を分離できるので広く利用されてる。 As a mineral resource, cobalt is often found in association with nickel, and most cobalt is produced as a by-product of nickel smelting. Therefore, in the production of cobalt, a technology is required to efficiently separate cobalt from nickel and various other impurity elements. Techniques for separating metals from an aqueous solution containing multiple metal elements include solvent extraction, precipitation, and ion exchange, but of these, solvent extraction is widely used because it can efficiently separate metals using simple equipment.
例えば、ニッケル含有原料の湿式製錬における副産物としてコバルトを回収する場合、先ず有価金属のニッケル及びコバルトを含む原料に対して鉱酸や酸化剤等を用いて浸出処理又は抽出処理を行い、得られたニッケル及びコバルトを含む酸性水溶液に対して溶媒抽出を行うことによって、ニッケル及びコバルトを含む水溶液からコバルトを分離して回収することが一般的に行われている。上記のようにして他元素から分離されたコバルトは不純物の濃度が低いことが好ましく、特にリチウムイオン二次電池の正極材料の原料として用いる塩化コバルト水溶液では、不純物の濃度ができるだけ低いことが求められている。 For example, when recovering cobalt as a by-product in the hydrometallurgy of nickel-containing raw materials, it is common to first subject raw materials containing the valuable metals nickel and cobalt to leaching or extraction treatment using a mineral acid or an oxidizing agent, and then subject the resulting acidic aqueous solution containing nickel and cobalt to solvent extraction to separate and recover cobalt from the aqueous solution containing nickel and cobalt. It is preferable that the cobalt separated from other elements in the above manner has a low concentration of impurities, and in particular, it is required that the concentration of impurities be as low as possible in the aqueous cobalt chloride solution used as a raw material for the positive electrode material of lithium-ion secondary batteries.
そこで、有機リン酸化合物に代表される酸性抽出剤を用いて上記の有価金属のニッケル及びコバルトを含む酸性水溶液から不純物を除去してこれら有価金属を高純度で回収する技術が提案されている。例えば特許文献1には、コバルトを含む粗硫酸ニッケル溶液に対してニッケルが担持された酸性抽出剤を用いてコバルトを始めとする不純物を有機相に抽出し、その不純物が抽出された有機相に対して段階的にpHを変化させて逆抽出を行うことで、不純物が除去された高純度の硫酸ニッケル溶液を得ると共にコバルトを回収する技術が開示されている。 Therefore, a technology has been proposed in which impurities are removed from an acidic aqueous solution containing the above-mentioned valuable metals nickel and cobalt using an acidic extractant such as an organic phosphoric acid compound, and these valuable metals are recovered in high purity. For example, Patent Document 1 discloses a technology in which impurities such as cobalt are extracted into an organic phase using an acidic extractant carrying nickel from a crude nickel sulfate solution containing cobalt, and the pH of the organic phase into which the impurities have been extracted is gradually changed to perform back extraction, thereby obtaining a high-purity nickel sulfate solution from which impurities have been removed and recovering cobalt.
具体的には、この特許文献1の技術は、ナトリウム、アンモニウム等の不純物を含む粗硫酸ニッケル溶液に酸性抽出剤を接触させることで、好適にはpH6.5~7.0の条件下でニッケルを抽出してニッケルを担持した酸性抽出剤を得る抽出工程と、該抽出工程で得たニッケルを担持した酸性抽出剤にコバルトを多く含む含Co粗硫酸ニッケル水溶液を接触させることにより、好適にはpH4~5の条件下で酸性抽出剤中のニッケルと該含Co粗硫酸ニッケル水溶液中のコバルト及び不純物とを置換して高ニッケル純度の精製硫酸ニッケル溶液を得る置換工程と、該置換工程で得たコバルト及び不純物を含む酸性抽出剤に硫酸水溶液を接触させることで、該置換工程で得た酸性抽出剤中に残留するニッケルを好適にはpH4.0程度の条件下で逆抽出するニッケル回収工程と、該ニッケル回収工程で得た酸性抽出剤に塩酸水溶液を接触させることで、好適にはpH1.4~2.0の条件下でコバルトを逆抽出するコバルト回収工程から構成される。 Specifically, the technology of Patent Document 1 is composed of an extraction step in which nickel is extracted by contacting a crude nickel sulfate solution containing impurities such as sodium and ammonium with an acidic extractant, preferably under conditions of pH 6.5 to 7.0, to obtain an acidic extractant carrying nickel; a substitution step in which the nickel in the acidic extractant is contacted with a cobalt-rich aqueous solution of crude nickel sulfate containing Co, preferably under conditions of pH 4 to 5, to substitute the cobalt and impurities in the aqueous solution of crude nickel sulfate containing Co for the nickel in the acidic extractant, preferably under conditions of pH 4 to 5, to obtain a purified nickel sulfate solution with high nickel purity; a nickel recovery step in which the acidic extractant containing cobalt and impurities obtained in the substitution step is contacted with an aqueous sulfuric acid solution, thereby back-extracting the nickel remaining in the acidic extractant obtained in the substitution step, preferably under conditions of about pH 4.0; and a cobalt recovery step in which the acidic extractant obtained in the nickel recovery step is contacted with an aqueous hydrochloric acid solution to back-extract cobalt, preferably under conditions of pH 1.4 to 2.0.
上記のように、有機リン酸化合物に代表される酸性抽出剤を用いてニッケル及びコバルトを含む水溶液を抽出処理することで、これらニッケルとコバルトとを分離して別々に回収することができるうえ、水溶液の状態で回収されるこれらニッケルやコバルトに不純物が含まれるのを抑えることが可能になる。しかしながら、酸性抽出剤に有機リン酸化合物を用いる場合は、抽出され易さの順序が鉄(Fe)>亜鉛(Zn)>銅(Cu)>マンガン(Mn)>コバルト(Co)>カルシウム(Ca)>マグネシウム(Mg)>ニッケル(Ni)になるため、ニッケル及びコバルトを含む水溶液に不純物としてマグネシウムが含まれる場合は、回収したニッケル水溶液若しくはコバルト水溶液、又はこれら両方にマグネシウムが含まれることになる。この場合、回収したニッケル水溶液及びコバルト水溶液のマグネシウム濃度をいずれも低く抑えるには例えばミキサーセトラーを多段に設ける等が必要になり、設備コストが高くなることが問題になる。 As described above, by extracting an aqueous solution containing nickel and cobalt using an acidic extractant such as an organic phosphoric acid compound, it is possible to separate and recover nickel and cobalt separately, and to suppress the inclusion of impurities in the nickel and cobalt recovered in the aqueous solution. However, when an organic phosphoric acid compound is used as the acidic extractant, the order of ease of extraction is iron (Fe) > zinc (Zn) > copper (Cu) > manganese (Mn) > cobalt (Co) > calcium (Ca) > magnesium (Mg) > nickel (Ni). Therefore, if magnesium is contained as an impurity in the aqueous solution containing nickel and cobalt, magnesium will be contained in the recovered aqueous nickel solution or cobalt solution, or both. In this case, in order to keep the magnesium concentration of both the recovered aqueous nickel solution and the recovered aqueous cobalt solution low, it is necessary to install, for example, a multi-stage mixer settler, which causes a problem of high equipment costs.
本発明は上記したようにニッケル及びコバルトを含む水溶液に対して酸性抽出剤を用いてこれらニッケル及びコバルトを相互に分離して別々に回収する従来の溶媒抽出法が抱える問題点に鑑みてなされたものであり、ニッケル及びコバルトを含む水溶液に対して酸性抽出剤を用いることで、これらニッケル及びコバルトを相互に分離して低マグネシウム濃度の水溶液として回収することが可能なコバルト水溶液の製造方法を提供することを目的としている。 As described above, the present invention has been made in consideration of the problems associated with the conventional solvent extraction method in which an acidic extractant is used on an aqueous solution containing nickel and cobalt to separate the nickel and cobalt from each other and recover them separately. The object of the present invention is to provide a method for producing an aqueous cobalt solution that uses an acidic extractant on an aqueous solution containing nickel and cobalt to separate the nickel and cobalt from each other and recover them as an aqueous solution with a low magnesium concentration.
上記目的を達成するため、本発明に係るコバルト水溶液の製造方法は、コバルト及びマグネシウムを含む粗ニッケル水溶液と、ニッケル担持酸性抽出剤を含む有機溶媒とを混合接触させることで、前記粗ニッケル水溶液中のコバルトと前記ニッケル担持酸性抽出剤のニッケルとを置換して高純度ニッケル水溶液及び交換後有機を得る交換段と、前記交換後有機中に残留するニッケルを第1酸性水溶液に逆抽出することでニッケル回収液及びニッケル回収後有機を得るニッケル回収段と、前記ニッケル回収後有機中のマグネシウムをコバルト洗浄液に逆抽出してコバルト洗浄後液及びコバルト洗浄後有機を得るコバルト洗浄段と、前記コバルト洗浄後有機中のコバルトを第2酸性水溶液に逆抽出してコバルト水溶液を回収するコバルト回収段とを有し、前記コバルト水溶液の一部を前記コバルト洗浄液に用いることを特徴とする。 In order to achieve the above object, the method for producing a cobalt aqueous solution according to the present invention comprises an exchange stage in which a crude nickel aqueous solution containing cobalt and magnesium is mixed and contacted with an organic solvent containing a nickel-supported acidic extractant to replace the cobalt in the crude nickel aqueous solution with the nickel in the nickel-supported acidic extractant to obtain a high-purity nickel aqueous solution and an exchanged organic solution; a nickel recovery stage in which nickel remaining in the exchanged organic solution is stripped into a first acidic aqueous solution to obtain a nickel recovery solution and a nickel recovery organic solution; a cobalt washing stage in which magnesium in the nickel recovery organic solution is stripped into a cobalt washing solution to obtain a cobalt washing solution and a cobalt washing organic solution; and a cobalt recovery stage in which cobalt in the cobalt washing organic solution is stripped into a second acidic aqueous solution to recover a cobalt aqueous solution, and a part of the cobalt aqueous solution is used for the cobalt washing solution.
本発明によれば、ニッケル及びコバルトを含む水溶液に対して酸性抽出剤を用いることで、これらニッケル及びコバルトを相互に分離して低マグネシウム濃度のコバルト水溶液を回収することが可能になる。 According to the present invention, by using an acidic extractant for an aqueous solution containing nickel and cobalt, it is possible to separate the nickel and cobalt from each other and recover an aqueous cobalt solution with a low magnesium concentration.
以下、本発明に係る低マグネシウム濃度のコバルト水溶液の製造方法の実施形態について詳細に説明する。この本発明の実施形態のコバルト水溶液の製造方法は、図1に示すように、ニッケル・コバルト混合硫化物(MS:Mixed Sulfide)を原料に使用している。ニッケル・コバルト混合硫化物は、低品位リモナイト鉱などのニッケル酸化鉱石を加圧酸浸出(HPAL:High Pressure Acid Leaching)することで得られる浸出液に対して、鉄などの不純物を除去した後、硫化水素ガスを吹き込んで硫化反応を生じさせることで得られる。このニッケル・コバルト混合硫化物を、加圧浸出工程において高温高圧の条件下で浸出することで粗硫酸ニッケル水溶液が得られる。この粗硫酸ニッケル水溶液は、脱鉄工程で鉄分が除去されることで、脱Fe終液として少なくともコバルトを含む粗硫酸ニッケル水溶液が得られる。 The embodiment of the method for producing a cobalt aqueous solution with a low magnesium concentration according to the present invention will be described in detail below. As shown in FIG. 1, the method for producing a cobalt aqueous solution according to the embodiment of the present invention uses nickel-cobalt mixed sulfide (MS: Mixed Sulfide) as a raw material. The nickel-cobalt mixed sulfide is obtained by removing impurities such as iron from the leachate obtained by high pressure acid leaching (HPAL: High Pressure Acid Leaching) of nickel oxide ore such as low-grade limonite ore, and then injecting hydrogen sulfide gas into the leachate to cause a sulfurization reaction. A crude nickel sulfate aqueous solution is obtained by leaching this nickel-cobalt mixed sulfide under high temperature and high pressure conditions in the pressure leaching process. The iron content of this crude nickel sulfate aqueous solution is removed in the iron removal process, and a crude nickel sulfate aqueous solution containing at least cobalt is obtained as the Fe-free final solution.
上記の脱Fe終液は、次に酸性抽出剤を用いた溶媒抽出工程で処理することで、高純度硫酸ニッケル水溶液とコバルト水溶液が製造される。この溶媒抽出工程は、抽出段、洗浄段、交換段、Ni回収段、Co洗浄段、Co回収段、及び逆抽出段からなり、各段においては、溶媒抽出を行う撹拌機を備えた混合槽と、重力により有機相と水相とを相分離させる分離槽とが一体化した構造の一般的なミキサーセトラー型溶媒抽出装置(以下、単にミキサーセトラーと称する)を用いることができる。特に、複数基のミキサーセトラーを直列に接続して多段向流連続抽出処理を行うのが好ましい。この溶媒抽出工程で使用する酸性抽出剤には、一般的な有機リン酸系の酸性抽出剤を用いるのが好ましく、特に下記化1に示す構造式を有する2-エチルヘキシルホスホン酸モノ-2-エチルヘキシルを上記の酸性抽出剤に用いるのがより好ましい。
上記の溶媒抽出工程について図2を参照しながら具体的に説明すると、先ず抽出段において、次の洗浄段から供給される洗浄後液を好ましくはpH6.0~7.0の条件下で酸性抽出剤を含む有機溶媒と混合接触させることで、洗浄後液に含まれる主にニッケルを例えば下記式1に示す抽出反応(Rはヒドロキシ基のHを除いた酸性抽出剤を表している)により有機相側に抽出し、ニッケルよりも抽出率が低いナトリウム、アンモニアなどの不純物を水相側に留めることで分離除去する。これにより、ニッケルを担持した酸性抽出剤(以下、Ni担持酸性抽出剤とも称する)を含む抽出後有機が得られる。
[式1]
2(R-H)+Ni2+→R-Ni-R+2H+
The above-mentioned solvent extraction step will be specifically described with reference to Fig. 2. First, in the extraction stage, the post-wash solution supplied from the next washing stage is mixed and contacted with an organic solvent containing an acidic extractant, preferably under conditions of pH 6.0 to 7.0, to extract mainly nickel contained in the post-wash solution into the organic phase by, for example, the extraction reaction shown in the following formula 1 (R represents the acidic extractant with H of the hydroxyl group removed), while impurities such as sodium and ammonia, which have lower extraction rates than nickel, are separated and removed by remaining in the aqueous phase. This results in an extracted organic solution containing an acidic extractant carrying nickel (hereinafter also referred to as Ni-loaded acidic extractant).
[Formula 1]
2(R-H)+Ni 2+ →R-Ni-R+2H +
次に、洗浄段において、上記抽出段から有機相として抜き出される抽出後有機を、ニッケルを含む洗浄液と混合接触させることで洗浄し、これにより該抽出後有機中に懸濁状態で含まれるエントレインメントと称する前段の抽出段で有機相から分離されずに残留する微細な水相からなる液滴を洗浄液側に移行させる。更に、該抽出後有機中に残留するナトリウム、アンモニア等の不純物を、洗浄液中のニッケルと置換させることにより除去する。この洗浄液には不純物濃度が低い硫酸ニッケル水溶液を用いるのが好ましく、例えば後段の交換段から抜き出される高純度硫酸ニッケル水溶液や、高純度硫酸ニッケル結晶の製造工程から産出される脱水母液を水で希釈したものが好適に用いられる。洗浄後液は抽出段に供給される。 Next, in the washing stage, the post-extraction organic phase extracted as an organic phase from the above extraction stage is washed by mixing and contacting it with a washing liquid containing nickel, thereby transferring fine droplets of aqueous phase that remain in suspension in the post-extraction organic phase and are not separated from the organic phase in the previous extraction stage, which are called entrainment, to the washing liquid side. Furthermore, impurities such as sodium and ammonia remaining in the post-extraction organic phase are removed by replacing them with nickel in the washing liquid. For this washing liquid, it is preferable to use an aqueous nickel sulfate solution with a low impurity concentration, for example, a high-purity aqueous nickel sulfate solution extracted from the subsequent exchange stage or a solution obtained by diluting the dehydrated mother liquor produced in the manufacturing process of high-purity nickel sulfate crystals with water. The post-washing liquid is supplied to the extraction stage.
次に、例えば連続する4基のミキサーセトラーで構成される交換段において、上記の洗浄段から有機相として抜き出される洗浄後有機を、有機相の流れ方向の最上流側のミキサーセトラーから導入すると共に、この流れ方向の最下流側のミキサーセトラーから脱Fe終液を導入し、好ましくは水相のpH4.0~5.0の範囲内でこれら有機相と水相とを互いに多段向流接触させる。これにより、洗浄後有機としてのNi担持酸性抽出剤に含まれるニッケルと、脱Fe終液に含まれるコバルトなどの不純物とが例えば下記式2の交換反応により置換され、高純度硫酸ニッケル水溶液が水相側に生成される。この高純度硫酸ニッケル水溶液はそのまま製品として出荷されるか、あるいは晶析設備に移送され、ここで加熱により濃縮及び晶析されて硫酸ニッケル結晶が製造される。一方、有機相側にはコバルトを含んだ交換後有機が得られる。
[式2]
R-Ni-R+Co2+→R-Co-R+Ni2+
Next, in an exchange stage consisting of, for example, four consecutive mixer settlers, the washed organic phase extracted as an organic phase from the above-mentioned washing stage is introduced from the mixer settler on the most upstream side in the flow direction of the organic phase, and the de-Fe final solution is introduced from the mixer settler on the most downstream side in the flow direction, and these organic phases and aqueous phases are brought into multi-stage countercurrent contact with each other, preferably within the pH range of 4.0 to 5.0 of the aqueous phase. As a result, nickel contained in the Ni-loaded acidic extractant as the washed organic phase and impurities such as cobalt contained in the de-Fe final solution are replaced by, for example, an exchange reaction of the following
[Formula 2]
R-Ni-R+Co 2+ →R-Co-R+Ni 2+
上記のように、交換段では前々段の抽出段で予めニッケルを抽出したNi担持酸性抽出剤によってコバルトを抽出するため、pH調整用の中和剤を特に用いることなく高純度の硫酸ニッケル水溶液を製造することが可能になる。これにより、例えば中和剤としてNaOHを使用したときに問題になるナトリウムによる高純度硫酸ニッケル水溶液の汚染を防ぐことができる。また、コバルトの抽出に相応してニッケルが逆抽出されるため、高純度硫酸ニッケル水溶液中のニッケル濃度を高めることができる。 As described above, in the exchange stage, cobalt is extracted using a Ni-loaded acidic extractant that has already extracted nickel in the previous extraction stage, making it possible to produce a high-purity nickel sulfate aqueous solution without using a neutralizing agent for adjusting the pH. This makes it possible to prevent contamination of the high-purity nickel sulfate aqueous solution with sodium, which is a problem when using NaOH as a neutralizing agent, for example. In addition, nickel is back-extracted in proportion to the extraction of cobalt, making it possible to increase the nickel concentration in the high-purity nickel sulfate aqueous solution.
ところで、上記の洗浄後有機に含まれるコバルトや不純物の濃度が高すぎると、上記の4基のミキサーセトラーで構成される交換段での交換反応により水相中の不純物濃度が低くなったときにこれらコバルトや不純物の水相から有機相への移行が生じにくくなる。そこで、上記抽出段の前段の逆抽出段で再生した逆抽出後有機の一部を抜き出して該抽出段及びその後段の洗浄段をバイパスさせ、該交換段における有機相の流れ方向の最上流側のミキサーセトラーから導入する洗浄後有機の希釈液に用いるのが好ましい。また、上記洗浄後有機は、コバルトや不純物の濃度が高い水相の方が交換反応の効率をより一層高めることができるので、一部を抜き出して該交換段における上記流れ方向の最上流側から3基目のミキサーセトラーに導入するのが好ましい。 However, if the concentration of cobalt and impurities contained in the post-wash organic is too high, when the concentration of impurities in the aqueous phase is reduced by the exchange reaction in the exchange stage composed of the four mixer settlers, the cobalt and impurities are less likely to migrate from the aqueous phase to the organic phase. Therefore, it is preferable to extract a portion of the post-stripping organic regenerated in the stripping stage preceding the extraction stage, bypass the extraction stage and the subsequent washing stage, and use it as a dilution liquid for the post-wash organic introduced from the mixer settler on the most upstream side in the flow direction of the organic phase in the exchange stage. In addition, since the efficiency of the exchange reaction can be further increased in the aqueous phase with a high concentration of cobalt and impurities, it is preferable to extract a portion of the post-wash organic and introduce it into the third mixer settler from the most upstream side in the flow direction of the exchange stage.
次に、Ni回収段において上記交換段から有機相として抜き出される交換後有機を、好ましくは希硫酸からなるpH4.0程度の第1酸性水溶液と混合接触させることで、該交換後有機中に残留するニッケルを水相側の該第1酸性水溶液に逆抽出する。このようにして得たニッケルを含むNi回収液は、例えば硫酸ニッケルの製造プロセスに繰り返される。 Next, in the Ni recovery stage, the exchanged organic phase extracted from the exchange stage as an organic phase is mixed and contacted with a first acidic aqueous solution, preferably made of dilute sulfuric acid and having a pH of about 4.0, to back-extract nickel remaining in the exchanged organic phase into the first acidic aqueous solution on the aqueous phase side. The nickel-containing Ni recovery solution thus obtained is then reused, for example, in the nickel sulfate manufacturing process.
次に、CO洗浄段において、上記Ni回収段から有機相として抜き出されるNi回収後有機のエントレインメントをコバルト洗浄液で置換することにより、Ni回収後有機のエントレインメントに含まれるマグネシウムを水相側に分配させる。また、コバルト洗浄液は後段のCo回収段で得られるコバルト水溶液なので、Ni回収後有機に抽出されたマグネシウムとコバルト洗浄液中のコバルトとが交換反応により置換され、有機相中のマグネシウムが水相側に移行される。これにより、後段のCo回収段でコバルトよりも逆抽出されやすいマグネシウムを予め分離除去するので、該Co回収段において不純物のマグネシウムの濃度の低い高純度コバルト水溶液を得ることができる。なお、上記のNi回収後有機のコバルト濃度は3.0~6.0g/L程度である。 Next, in the CO cleaning stage, the entrainment of the organic phase after Ni recovery, which is extracted as an organic phase from the Ni recovery stage, is replaced with a cobalt cleaning solution, so that the magnesium contained in the entrainment of the organic phase after Ni recovery is distributed to the aqueous phase. Since the cobalt cleaning solution is an aqueous cobalt solution obtained in the subsequent Co recovery stage, the magnesium extracted into the organic phase after Ni recovery and the cobalt in the cobalt cleaning solution are replaced by an exchange reaction, and the magnesium in the organic phase is transferred to the aqueous phase. As a result, magnesium, which is more easily back-extracted than cobalt in the subsequent Co recovery stage, is separated and removed in advance, so that a high-purity aqueous cobalt solution with a low concentration of magnesium impurities can be obtained in the Co recovery stage. The cobalt concentration of the organic phase after Ni recovery is about 3.0 to 6.0 g/L.
上記のCo洗浄段においては、水相側のコバルト洗浄液のpHを2.0以上4.5以下にするのが好ましく、特にpHの下限値は3.0がより好ましい。このコバルト洗浄液のpHが2.0未満では、水相側に逆抽出されるコバルトの量が多くなりすぎ、逆にこのpHが4.5を超えると、マグネシウムが水相側に逆抽出されにくくなる。また、上記のCo洗浄段では、水相の供給流量Aに対する有機相の供給流量Oの体積比率O/Aを0.1以上30以下にするのが好ましく、0.5以上1.0以下にするのがより好ましい。この体積比率O/Aが0.1未満では、水相流量が過多となりセトラー部での滞留時間が短くなり油水分離不良を引き起すため、Co洗浄段から有機相として抜き出されるCo洗浄後有機のエントレインメントが増加し、結果的にCo洗浄後有機中のマグネシウム濃度の低下が阻害される。逆にこの体積比O/Aが30を超えると、コバルト洗浄液流量が少な過ぎて、洗浄効果、すなわちNi回収後有機のエントレインメントをコバルト洗浄液で置換する効果を十分に得ることができない。 In the above Co cleaning stage, it is preferable to set the pH of the cobalt cleaning solution on the aqueous phase side to 2.0 or more and 4.5 or less, and in particular, the lower limit of the pH is more preferably 3.0. If the pH of this cobalt cleaning solution is less than 2.0, the amount of cobalt back-extracted into the aqueous phase becomes too large, and conversely, if the pH exceeds 4.5, magnesium becomes difficult to back-extract into the aqueous phase. In addition, in the above Co cleaning stage, it is preferable to set the volume ratio O/A of the organic phase supply flow rate O to the aqueous phase supply flow rate A to 0.1 or more and 30 or less, and more preferably 0.5 or more and 1.0 or less. If this volume ratio O/A is less than 0.1, the aqueous phase flow rate becomes excessive, the residence time in the settler section becomes short, and oil-water separation is caused, so that the entrainment of the organic after Co cleaning extracted as an organic phase from the Co cleaning stage increases, and as a result, the decrease in the magnesium concentration in the organic after Co cleaning is inhibited. Conversely, if the volume ratio O/A exceeds 30, the flow rate of the cobalt cleaning solution is too low, and the cleaning effect, i.e., the effect of replacing the organic entrainment with the cobalt cleaning solution after Ni recovery, cannot be fully achieved.
Co洗浄液に後述する粗塩化コバルト水溶液を用いる場合は、そのコバルト濃度が80g/L程度であるのが好ましく、また、洗浄効率を高めるにはCo洗浄液のマグネシウム濃度は低ければ低いほど望ましい。上記の粗塩化コバルト水溶液を用いる場合は、マグネシウム濃度は0.080~0.090g/L程度である。Co洗浄段における液温は10℃以上50℃以下が好ましく、マグネシウムのコバルト洗浄後有機相とコバルト洗浄後水相(コバルト洗浄後液)との分配を考慮すると40℃以上が望ましい。 When using the crude cobalt chloride aqueous solution described below as the Co cleaning solution, the cobalt concentration is preferably about 80 g/L, and the lower the magnesium concentration of the Co cleaning solution, the more desirable it is to increase cleaning efficiency. When using the crude cobalt chloride aqueous solution described above, the magnesium concentration is about 0.080 to 0.090 g/L. The liquid temperature in the Co cleaning stage is preferably 10°C to 50°C, and considering the distribution of magnesium between the organic phase after cobalt cleaning and the aqueous phase after cobalt cleaning (liquid after cobalt cleaning), it is desirable to have a temperature of 40°C or higher.
次に、Co回収段において、上記Co洗浄段から有機相として抜き出されるコバルト洗浄後有機を、好ましくは塩酸からなるpH1.0程度に調整された第2酸性水溶液と混合接触させることで該コバルト洗浄後有機に含まれるコバルトを水相側の該第2酸性水溶液に逆抽出する。このようにして回収されたコバルトを含む粗塩化コバルト水溶液は、その一部が前段のCo洗浄段におけるコバルト洗浄液に使用され、残部は必要に応じて浄液工程において亜鉛、マンガン、銅、カドミウム等の不純物が除去されることで高純度塩化コバルト水溶液となる。この高純度塩化コバルト水溶液は、水溶液のまま二次電池の正極材の原料として用いられたり電解採取工程に供給されて高品位の電気コバルトが製造されたりする。最後に逆抽出段において、上記Co回収段から有機相として抜き出されるコバルト回収後有機を希硫酸と混合接触させることで、鉄などの不純物を該希硫酸に逆抽出する。 Next, in the Co recovery stage, the organic solution after cobalt washing, which is extracted as an organic phase from the Co washing stage, is mixed and contacted with a second acidic aqueous solution adjusted to about pH 1.0, preferably made of hydrochloric acid, to back-extract the cobalt contained in the organic solution after cobalt washing into the second acidic aqueous solution on the aqueous phase side. A part of the crude cobalt chloride aqueous solution containing cobalt thus recovered is used as a cobalt washing solution in the preceding Co washing stage, and the remainder is turned into a high-purity aqueous cobalt chloride solution by removing impurities such as zinc, manganese, copper, and cadmium in a solution purification process as necessary. This high-purity aqueous cobalt chloride solution is used as a raw material for the positive electrode material of secondary batteries as it is, or is supplied to an electrowinning process to produce high-quality electrolytic cobalt. Finally, in the back extraction stage, the organic solution after cobalt recovery, which is extracted as an organic phase from the Co recovery stage, is mixed and contacted with dilute sulfuric acid to back-extract impurities such as iron into the dilute sulfuric acid.
上記したように、溶媒抽出の抽出剤に酸性抽出剤を用いることで、抽出反応に水素イオンが関与するので、pHによって抽出率を変化させることができる。抽出率は金属によって異なり、Fe>Zn>Cu>Mn>Co>Ca>Mg>Niの順に抽出されやすい。従って、有機相の流れの順である抽出段、洗浄段、交換段、Ni回収段、Co洗浄段、Co回収段、及び逆抽出段の順にpHを下げていくことで、それぞれの段で異なる金属を分離することができる。 As mentioned above, by using an acidic extractant for the solvent extraction, hydrogen ions are involved in the extraction reaction, and the extraction rate can be changed by changing the pH. The extraction rate differs depending on the metal, with the metals most likely to be extracted in the following order: Fe>Zn>Cu>Mn>Co>Ca>Mg>Ni. Therefore, by lowering the pH in the order of the organic phase flow, which is the extraction stage, washing stage, exchange stage, Ni recovery stage, Co washing stage, Co recovery stage, and back extraction stage, different metals can be separated in each stage.
[実施例1]
大八化学工業株式会社製の有機リン酸系の酸性抽出剤である2-エチルヘキシルホスホン酸モノ-2-エチルヘキシル(商品名:PC88A)に対して、希釈剤としてENEOS株式会社製の飽和炭化水素(商品名:テクリーンN-20)を用いて20体積%に希釈することで有機溶媒を調製した。この酸性抽出剤を含む有機溶媒を用いた溶媒抽出において、コバルトを含んだ酸性抽出剤から不純物のマグネシウムを分離除去する工程であるCo洗浄段の除去効果を確認した。
[Example 1]
An organic solvent was prepared by diluting mono-2-ethylhexyl 2-ethylhexyl phosphonate (product name: PC88A), an organophosphate acidic extractant manufactured by Daihachi Chemical Industry Co., Ltd., to 20% by volume using a saturated hydrocarbon (product name: Teclain N-20) manufactured by ENEOS Corporation as a diluent. In solvent extraction using an organic solvent containing this acidic extractant, the removal effect of the Co washing stage, which is a process for separating and removing magnesium impurities from the cobalt-containing acidic extractant, was confirmed.
具体的には、図2に示す溶媒抽出工程に沿って高純度硫酸ニッケル水溶液の製造を行う抽出設備において、そのNi回収段から排出されるNi回収後有機をサンプリングし、これを容量100mLの7個のポリ容器に始液有機相として30mLずつ小分けした。これら始液有機相を含む7個のポリ容器に、上記抽出設備のCo回収段から排出される粗塩化Co水溶液をサンプリングして30mLずつ7つに小分けしたものをそれぞれ始液水相として装入して試料1~7を調製した。 Specifically, in an extraction facility that produces a high-purity nickel sulfate aqueous solution according to the solvent extraction process shown in Figure 2, the post-Ni recovery organic solution discharged from the Ni recovery stage was sampled and divided into seven 100 mL plastic containers as the initial organic phase, each containing 30 mL of the sample. The crude Co chloride aqueous solution discharged from the Co recovery stage of the extraction facility was sampled and divided into seven 30 mL portions, each of which was charged as the initial aqueous phase into the seven plastic containers containing the initial organic phase, to prepare samples 1 to 7.
この調製の際、7つに小分けした始液水相のうち試料2~7に用いた6つについては、pH2.1~5.1の範囲内でそれぞれ異なるpH値となるように、希塩酸及び希釈水酸化ナトリウム水溶液を用いてpH調整した。一方、比較のため、試料1の始液水相は、pH調整せずにそのまま用いた。
During this preparation, the starting aqueous phase was divided into seven portions, and six of them, used for
上記のようにして調製した試料1~7の液がそれぞれ入った7個のポリ容器の各々を、マグネチックスターラーで強撹拌することにより、始液有機相と始液水相とを混合接触させて抽出処理を行なった後、静置して終液有機相と終液水相とに分離させた。その際、液温は特に調整せずに成り行きにしたところ、室温とほぼ同程度の約20℃であった。この抽出処理前後の有機相と水相の金属元素濃度を蛍光X線分析装置で分析した結果を前後の水相のpH値と共に下記表1~7に示す。更に、試料1~7に対して行った抽出処理におけるコバルトとマグネシウムの分離性能の結果を下記表8に示す。 Seven plastic containers containing the liquid samples 1 to 7 prepared as described above were each strongly stirred with a magnetic stirrer to mix and contact the initial organic phase and initial aqueous phase for extraction, and then the mixture was left to stand to separate into the final organic phase and final aqueous phase. The liquid temperature was left to run without any special adjustment, and was approximately 20°C, which is roughly the same as room temperature. The metal element concentrations in the organic and aqueous phases before and after this extraction process were analyzed with an X-ray fluorescence analyzer, and the results are shown in Tables 1 to 7 below, along with the pH values of the aqueous phase before and after. Furthermore, the results of the separation performance of cobalt and magnesium in the extraction process performed on samples 1 to 7 are shown in Table 8 below.
上記表8に示すように、始液有機相中のコバルト濃度(g/L)に対するマグネシウム濃度(g/L)の比率Aを終液有機相中のコバルト濃度(g/L)に対するマグネシウム濃度(g/L)の比率Bで除した値は3.36~8.75であり、いずれの条件においても、Co洗浄段において酸性抽出剤を有する有機溶媒からマグネシウムを効果的に除去できることが分かる。ただし、試料6ではコバルトが抽出されている一方で、マグネシウムが逆抽出されていない。従って、酸性抽出剤からのマグネシウムの逆抽出という観点からすると、pHは5.0未満が好ましく、2.0~4.5の範囲内がより好ましいと言える。 As shown in Table 8 above, the ratio A of the magnesium concentration (g/L) to the cobalt concentration (g/L) in the initial organic phase divided by the ratio B of the magnesium concentration (g/L) to the cobalt concentration (g/L) in the final organic phase is 3.36 to 8.75, which shows that magnesium can be effectively removed from the organic solvent having the acidic extractant in the Co washing stage under all conditions. However, in sample 6, while cobalt is extracted, magnesium is not back-extracted. Therefore, from the viewpoint of back-extraction of magnesium from the acidic extractant, a pH of less than 5.0 is preferable, and a pH in the range of 2.0 to 4.5 is more preferable.
[実施例2]
実施例1と同様の抽出設備のNi回収段から排出されるNi回収後有機をサンプリングし、これを容量100mLの8個のポリ容器に始液有機相として20mLずつ小分けした。一方、上記の抽出設備のCo回収段から排出される粗塩化Co水溶液をサンプリングして4つに小分けし、それらのCo濃度が5~40g/Lの範囲内でそれぞれ異なるように水で希釈し、始液水相とした。
[Example 2]
The organic phase after Ni recovery discharged from the Ni recovery stage of the extraction equipment similar to that of Example 1 was sampled and divided into 20 mL portions as the initial liquid organic phase in eight 100 mL plastic containers. Meanwhile, the crude Co chloride aqueous solution discharged from the Co recovery stage of the above extraction equipment was sampled and divided into four portions, which were diluted with water so that the Co concentrations were different within the range of 5 to 40 g/L, and used as the initial liquid aqueous phase.
このようにしてCo濃度が調整された4種類の始液水相から60mLずつ採取して希釈水酸化ナトリウム水溶液を用いてpH3.5~3.8の範囲内にpH調整した後、上記の始液有機相が入っている8個のポリ容器のうちの4個にそれぞれ装入して試料8~11とし、それらを室温とほぼ同じ液温約20℃にした。また、上記の8個のポリ容器のうち残る4個にも同様に4種類の始液水相から60mLずつ採取して、希釈水酸化ナトリウム水溶液を用いてpH3.5~3.8の範囲内にpH調整したものをそれぞれ装入して試料12~15としたが、これら試料12~15は恒温槽内に浸漬させて液温50℃にした。 60 mL each was taken from each of the four types of starting aqueous phases with adjusted Co concentrations in this way, and the pH was adjusted to within the range of 3.5 to 3.8 using a diluted aqueous sodium hydroxide solution. The samples were then placed in four of the eight plastic containers containing the starting organic phases to prepare samples 8 to 11, and the liquid temperature of these samples was adjusted to approximately 20°C, which is almost the same as room temperature. Similarly, 60 mL each was taken from each of the four types of starting aqueous phases in the remaining four of the eight plastic containers, and the pH was adjusted to within the range of 3.5 to 3.8 using a diluted aqueous sodium hydroxide solution. The samples were then placed in the remaining four of the eight plastic containers to prepare samples 12 to 15, and the liquid temperature of these samples 12 to 15 was adjusted to 50°C by immersing them in a thermostatic bath.
以降は実施例1と同様にして始液有機相と始液水相とを混合接触させて抽出処理を行なった後、静置して終液有機相と終液水相とに分離させた。この抽出処理前後の有機相と水相に対して実施例1と同様に金属元素濃度を分析した結果を始液水相のpH値と共に下記表9~16に示す。更に、試料8~15に対して行った抽出処理におけるコバルトとマグネシウムの分離性能の結果を下記表17に示す。 Then, the initial organic phase and the initial aqueous phase were mixed and contacted in the same manner as in Example 1 to carry out the extraction process, and then the mixture was allowed to stand to separate into a final organic phase and a final aqueous phase. The organic phase and the aqueous phase were analyzed for metal element concentration before and after this extraction process in the same manner as in Example 1, and the results are shown in Tables 9 to 16 below, along with the pH value of the initial aqueous phase. Furthermore, the results of the separation performance of cobalt and magnesium in the extraction process carried out on samples 8 to 15 are shown in Table 17 below.
上記表17に示すように、始液有機相中のコバルト濃度(g/L)に対するマグネシウム濃度(g/ L)の比率Aを終液有機相中のコバルト濃度(g/L)に対するマグネシウム濃度(g/L)の比率Bで除した値は3.79~4.94であり、いずれの条件においても、Co洗浄段において酸性抽出剤を有する有機溶媒からマグネシウムを効率的に除去できることが分かる。また、始液水相コバルト濃度が低い方が、始液有機相中のマグネシウムの洗浄効果は、幾分かは高くなるが、始液水相のpHが3.5~3.8の範囲内では、水相コバルト濃度の影響は小さいと考えられる。また、液温20℃と50℃を比較すると、洗浄時の温度が高い方がマグネシウムとコバルトの分離効率が高い結果となった。なお、試料1~7がO/Aで1.0、試料8~15がO/Aで0.33に相当するが、この程度の差であればO/Aの影響も無いと考えられる。 As shown in Table 17 above, the ratio A of the magnesium concentration (g/L) to the cobalt concentration (g/L) in the initial organic phase divided by the ratio B of the magnesium concentration (g/L) to the cobalt concentration (g/L) in the final organic phase is 3.79 to 4.94, and it can be seen that under all conditions, magnesium can be efficiently removed from the organic solvent having an acidic extractant in the Co washing stage. In addition, the lower the initial aqueous phase cobalt concentration, the higher the washing effect of magnesium in the initial organic phase, but it is thought that the effect of the aqueous phase cobalt concentration is small when the initial aqueous phase pH is in the range of 3.5 to 3.8. In addition, comparing the liquid temperatures of 20°C and 50°C, the higher the washing temperature, the higher the separation efficiency of magnesium and cobalt. Incidentally, samples 1 to 7 correspond to 1.0 in O/A, and samples 8 to 15 correspond to 0.33 in O/A, and it is thought that there is no effect of O/A with a difference of this magnitude.
Claims (4)
前記交換後有機中に残留するニッケルを第1酸性水溶液に逆抽出することでニッケル回収液及びニッケル回収後有機を得るニッケル回収段と、
前記ニッケル回収後有機中のマグネシウムをコバルト洗浄液に逆抽出してコバルト洗浄後液及びコバルト洗浄後有機を得るコバルト洗浄段と、
前記コバルト洗浄後有機中のコバルトを第2酸性水溶液に逆抽出してコバルト水溶液を回収するコバルト回収段とを有し、
前記コバルト水溶液の一部を前記コバルト洗浄液に用いることを特徴とするコバルト水溶液の製造方法。 an exchange stage in which a crude nickel aqueous solution containing cobalt and magnesium is mixed and contacted with an organic solvent containing a nickel-supported acidic extractant to replace the cobalt in the crude nickel aqueous solution with the nickel in the nickel-supported acidic extractant, thereby obtaining a high-purity nickel aqueous solution and an exchanged organic solvent;
a nickel recovery stage in which nickel remaining in the post-exchange organic is stripped into a first acidic aqueous solution to obtain a nickel recovery solution and a post-nickel recovery organic;
a cobalt wash stage in which magnesium in the nickel-recovery organic is stripped into a cobalt wash solution to obtain a cobalt wash solution and a cobalt wash organic;
a cobalt recovery stage for recovering an aqueous cobalt solution by back-extracting the cobalt in the organic solvent after the cobalt washing into a second acidic aqueous solution;
A method for producing an aqueous cobalt solution, comprising using a part of the aqueous cobalt solution as the cobalt cleaning solution.
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