JP7090877B2 - How to recover valuable metals - Google Patents
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Description
本発明は、有価金属例えばニッケルを含む固体廃棄物や中間廃液からリン、スズ等の不純物を有効に分離でき、有価金属を容易に回収することができる有価金属の回収方法に関する。 The present invention relates to a method for recovering a valuable metal, which can effectively separate impurities such as phosphorus and tin from solid waste containing valuable metals such as nickel and intermediate waste liquid, and can easily recover the valuable metal.
メッキ工場等から排出される廃液や廃スラッジ中にはニッケル、銅、亜鉛等の有価金属が含まれている。このため、そのような廃液や廃スラッジ中から有価金属を回収するために、中和凝集沈殿法、溶媒抽出法、イオン交換樹脂法等の分離方法が検討されている。 Valuable metals such as nickel, copper and zinc are contained in the waste liquid and waste sludge discharged from plating factories and the like. Therefore, in order to recover valuable metals from such waste liquids and waste sludge, separation methods such as a neutralization coagulation precipitation method, a solvent extraction method, and an ion exchange resin method have been studied.
例えば、特許文献1にはニッケルスラッジからのニッケルの分離方法が開示されている。この分離方法は、ニッケルスラッジに硫酸溶液を添加してpHを4~6に調整して沈殿物と浸出液とに固液分離する浸出工程と、その浸出工程で得た浸出液を濃縮する濃縮工程と、濃縮工程で得た濃縮液を冷却して硫酸ニッケルの結晶を晶析させる冷却工程と、固液分離により硫酸ニッケルの結晶を回収する晶析工程とを有している。
For example,
前述した特許文献1に記載されている従来構成のニッケルの分離方法では、浸出工程、濃縮工程、冷却工程及び晶析工程を経て硫酸ニッケルの結晶を得ている。このため、硫酸ニッケルの結晶を得るまでの工程数が多く、有価金属の回収が煩雑である上に、濃縮や結晶を晶出させる冷却には相当の時間を要し、回収効率が悪い。さらに、ニッケルスラッジにはリン、スズ等の不純物が含まれており、そのような不純物の含有量を簡易に低減させることが難しく、従って有価金属の含有量を十分に向上させることができなかった。なお、ニッケルの酸化物を得るには硫酸ニッケルを1000℃程度の高温で焼成する焼成工程が必要である。
In the conventional nickel separation method described in
そこで、本発明の目的とするところは、不純物の含有量を低減させるとともに、有価金属の含有量を向上させ、かつ簡易な方法で有価金属を回収できる有価金属の回収方法を提供することにある。 Therefore, an object of the present invention is to provide a method for recovering a valuable metal, which can reduce the content of impurities, improve the content of the valuable metal, and recover the valuable metal by a simple method. ..
上記の目的を達成するために、本発明の有価金属の回収方法は、有価金属を含有する廃棄物に無機酸を加え、有価金属の溶解液とリン及びスズを含む不純物の沈殿物に分離する分離工程と、前記有価金属の溶解液にシュウ酸を加えて有価金属のシュウ酸塩の沈殿物を生成させる有価金属のシュウ酸塩生成工程と、前記有価金属のシュウ酸塩を焼成して有価金属の酸化物を生成させる焼成工程とを含む。 In order to achieve the above object, the method for recovering a valuable metal of the present invention adds an inorganic acid to a waste containing a valuable metal and separates it into a solution of the valuable metal and a precipitate of impurities containing phosphorus and tin. A separation step, a valuable metal oxalate production step in which oxalic acid is added to the valuable metal solution to form a precipitate of the valuable metal oxalate, and a valuable metal oxalate generation step by firing the valuable metal oxalate. It includes a firing step of producing metal oxides.
このため、分離工程、シュウ酸塩生成工程及び焼成工程という簡単な工程の組合せで有価金属を回収することができる。さらに、分離工程において、有価金属は無機酸の塩となって溶解液中に存在する一方、不純物は沈殿物中に多く含まれるため、分離操作で溶解液から沈殿物が分離される。シュウ酸塩生成工程においては、有価金属がシュウ酸と速やかに反応してシュウ酸塩となって沈殿する一方、不純物はシュウ酸と反応し難く、溶解液中に残る傾向を示す。このため、分離操作により有価金属のシュウ酸塩の沈殿物を取得することができる。 Therefore, the valuable metal can be recovered by a simple combination of a separation step, an oxalate production step, and a calcination step. Further, in the separation step, the valuable metal becomes a salt of an inorganic acid and is present in the solution, while impurities are contained in a large amount in the precipitate, so that the precipitate is separated from the solution by the separation operation. In the oxalate production step, valuable metals rapidly react with oxalic acid to form oxalate and precipitate, while impurities are difficult to react with oxalic acid and tend to remain in the solution. Therefore, a precipitate of valuable metal oxalate can be obtained by the separation operation.
焼成工程では、有価金属のシュウ酸塩が酸化され、目的とする有価金属の酸化物を含む焼成物を350℃の低温で得ることができる。従って、焼成物中の不純物の含有量を低減させることができるとともに、有価金属の含有量を高めることができる。 In the firing step, the oxalate of the valuable metal is oxidized, and a calcined product containing an oxide of the target valuable metal can be obtained at a low temperature of 350 ° C. Therefore, the content of impurities in the fired product can be reduced and the content of valuable metals can be increased.
本発明の有価金属の回収方法によれば、不純物の含有量を低減させるとともに、有価金属の含有量を向上させ、かつ簡易な方法で有価金属を回収できるという効果を奏する。 According to the method for recovering a valuable metal of the present invention, the content of impurities can be reduced, the content of the valuable metal can be improved, and the valuable metal can be recovered by a simple method.
以下、本発明の実施形態について詳細に説明する。
本実施形態における有価金属の回収方法は、有価金属が溶解された溶解液と不純物を含有する沈殿物に分離する分離工程と、有価金属のシュウ酸塩生成工程と、有価金属の酸化物を生成させる焼成工程とを含むものである。有価金属としては、メッキ工場の廃棄スラッジ等の廃棄物中に含まれるニッケル(Ni)、銅(Cu)、亜鉛(Zn)等が挙げられる。また、不純物としては、例えばリン(P)、スズ(Sn)等が挙げられる。
Hereinafter, embodiments of the present invention will be described in detail.
The method for recovering the valuable metal in the present embodiment includes a separation step of separating the solution in which the valuable metal is dissolved and a precipitate containing impurities, a sinter generation step of the valuable metal, and an oxide of the valuable metal. It includes a firing step of making the metal. Examples of the valuable metal include nickel (Ni), copper (Cu), zinc (Zn) and the like contained in waste such as waste sludge from a plating factory. Examples of impurities include phosphorus (P) and tin (Sn).
次に、前記各工程について順に説明する。
(分離工程)
前記分離工程は、有価金属を含有する廃棄物に無機酸(無機酸の水溶液)を加えて撹拌し、有価金属が溶解された溶解液と、リン及びスズを含む不純物を含有する沈殿物とに分離する工程である。すなわち、有価金属は無機酸の塩となって溶解液中に存在する一方、不純物の多くは不溶性の沈殿物となる。このため、常法に従って沈殿物を濾過して取り除くことにより、有価金属の溶解液を得ることができる。
Next, each of the above steps will be described in order.
(Separation process)
In the separation step, an inorganic acid (an aqueous solution of an inorganic acid) is added to a waste containing a valuable metal and stirred to form a solution in which the valuable metal is dissolved and a precipitate containing impurities containing phosphorus and tin. This is the process of separation. That is, while the valuable metal becomes a salt of an inorganic acid and exists in the solution, most of the impurities become an insoluble precipitate. Therefore, a solution of valuable metal can be obtained by filtering and removing the precipitate according to a conventional method.
前記無機酸としては、硫酸(H2SO4)、硝酸(HNO3)、塩酸(HCl)等の無機の強酸が好適に用いられる。無機酸の濃度は、1~2M(モル濃度)が好ましい。このように、無機の強酸を1~2Mの濃度で使用することにより、硫酸ニッケル(NiSO4)、硫酸銅(CuSO4)、硫酸亜鉛(ZnSO4)等を含む溶解液を高濃度で生成させることができる。すなわち、これら硫酸ニッケル、硫酸銅、硫酸亜鉛等は水に対する溶解度が高い。無機酸の濃度が1M未満の場合には、溶解液中に有価金属を十分に溶解させることができないことがある。一方、無機酸の濃度が2Mを超える場合には、溶解液中に不純物であるリンやスズの無機酸塩の共存量が増大することがある。 As the inorganic acid, a strong inorganic acid such as sulfuric acid (H 2 SO 4 ), nitric acid (HNO 3 ), and hydrochloric acid (HCl) is preferably used. The concentration of the inorganic acid is preferably 1 to 2 M (molar concentration). As described above, by using a strong inorganic acid at a concentration of 1 to 2 M, a solution containing nickel sulfate (NiSO 4 ), copper sulfate (CuSO 4 ), zinc sulfate (ZnSO 4 ), etc. is produced at a high concentration. be able to. That is, these nickel sulfate, copper sulfate, zinc sulfate and the like have high solubility in water. If the concentration of the inorganic acid is less than 1 M, it may not be possible to sufficiently dissolve the valuable metal in the solution. On the other hand, when the concentration of the inorganic acid exceeds 2M, the coexistence amount of the inorganic acid salts of phosphorus and tin, which are impurities, may increase in the solution.
(有価金属のシュウ酸塩生成工程)
前記有価金属のシュウ酸塩生成工程は、前述の溶解液にシュウ酸〔(COOH)2〕を加えて有価金属のシュウ酸塩の沈殿物を生成させる工程である。有価金属(の無機酸塩)のイオンとシュウ酸とは常温で容易に反応して有価金属のシュウ酸塩が沈殿物となって析出する。析出した有価金属のシュウ酸塩の沈殿物を常法に従って濾過することにより、不純物を溶解液中に残した状態で有価金属のシュウ酸塩を沈殿物として取得することができる。
(Oxalate production process for valuable metals)
The precious metal oxalate production step is a step of adding oxalic acid [(COOH) 2 ] to the above-mentioned solution to form a precious metal oxalate precipitate. The ions of the valuable metal (inorganic acid salt) and oxalic acid easily react at room temperature, and the oxalate of the valuable metal precipitates as a precipitate. By filtering the precipitated precious metal oxalate precipitate according to a conventional method, the precious metal oxalate can be obtained as a precipitate with impurities remaining in the solution.
この場合、前記溶解液のpHは1.5~3.5であることが好ましく、この場合有価金属のシュウ酸塩の析出率を高めて有価金属の純度向上に資することができる。このpHが1.5未満の場合、有価金属のシュウ酸塩の析出に時間を要し、生成効率が低下する。その一方、pHが3.5を超える場合、前記分離工程で溶解液中における有価金属のイオンの含有量が低下する傾向がある。 In this case, the pH of the solution is preferably 1.5 to 3.5, and in this case, the precipitation rate of the valuable metal oxalate can be increased to contribute to the improvement of the purity of the valuable metal. When this pH is less than 1.5, it takes time to precipitate the valuable metal oxalate, and the production efficiency is lowered. On the other hand, when the pH exceeds 3.5, the ion content of the valuable metal in the solution tends to decrease in the separation step.
さらに、有価金属のシュウ酸塩生成工程では、予め溶解液中に含まれる有価金属含有量を分析し、その有価金属含有量に対して1~3当量のシュウ酸を加えることが好ましい。このように、溶解液中の有価金属含有量を予め分析し、それに対して過剰のシュウ酸を添加することにより、有価金属のシュウ酸塩を効率良く生成させることができる。シュウ酸の使用量が有価金属含有量に対して1当量未満の場合には、有価金属のシュウ酸塩を十分に回収することができない。その一方、3当量を超える場合には、シュウ酸の添加量が過剰となり、未反応のシュウ酸が多量に残存して無駄が生ずる。 Further, in the step of producing oxalate of a valuable metal, it is preferable to analyze the content of the valuable metal contained in the solution in advance and add 1 to 3 equivalents of oxalic acid to the valuable metal content. As described above, by analyzing the valuable metal content in the solution in advance and adding an excess of oxalic acid to the content, the valuable metal oxalate can be efficiently produced. If the amount of oxalic acid used is less than 1 equivalent with respect to the valuable metal content, the valuable metal oxalate cannot be sufficiently recovered. On the other hand, if it exceeds 3 equivalents, the amount of oxalic acid added becomes excessive, and a large amount of unreacted oxalic acid remains, resulting in waste.
溶解液中に含まれる有価金属含有量の分析法としては、誘導結合プラズマ分析法(ICP分析法)、具体的にはICP-AES(ICP発光分光分析法)等が採用される。有価金属のシュウ酸塩としては、例えばシュウ酸ニッケル〔(COO)2Ni〕、シュウ酸銅〔(COO)2Cu〕、シュウ酸亜鉛〔(COO)2Zn〕等が挙げられる。この有価金属のシュウ酸塩生成工程で得られる有価金属のシュウ酸塩は、X線回折法(XRD法)等で分析して金属に特有のピークからその存在を確認することができる。 As a method for analyzing the content of valuable metal contained in the solution, an inductively coupled plasma analysis method (ICP analysis method), specifically ICP-AES (ICP emission spectroscopic analysis method) or the like is adopted. Examples of the oxalate of a valuable metal include nickel oxalate [(COO) 2 Ni], copper oxalate [(COO) 2 Cu], zinc oxalate [(COO) 2 Zn] and the like. The existence of the valuable metal oxalate obtained in the precious metal oxalate production step can be confirmed by analysis by an X-ray diffraction method (XRD method) or the like from a peak peculiar to the metal.
(焼成工程)
前記シュウ酸塩生成工程で得られた有価金属のシュウ酸塩を焼成することにより有価金属の酸化物を生成させることができる。この焼成は、例えば電気炉等を使用し、有価金属のシュウ酸塩の発熱を伴いながら350~800℃の焼成温度で行われる。焼成温度が350℃を下回る場合には、焼成が不十分で、有価金属のシュウ酸塩から酸化物への転換が不足する傾向を示す。その一方、焼成温度が800℃を上回る場合には、焼成が過度となりやすく、有価金属の酸化物の分解が生じたりして好ましくない。有価金属の酸化物としては、酸化ニッケル(NiO、Ni2O3)、酸化銅(Cu2O、CuO)、酸化亜鉛(ZnO)等が挙げられる。
(Baking process)
An oxide of a valuable metal can be produced by calcining the oxalate of the valuable metal obtained in the oxalate production step. This calcination is carried out using, for example, an electric furnace or the like at a calcination temperature of 350 to 800 ° C. with heat generation of the valuable metal oxalate. When the calcination temperature is lower than 350 ° C., the calcination is insufficient and the conversion of the valuable metal from oxalate to an oxide tends to be insufficient. On the other hand, when the calcination temperature exceeds 800 ° C., the calcination tends to be excessive and the oxide of the valuable metal is decomposed, which is not preferable. Examples of the oxide of the valuable metal include nickel oxide (NiO, Ni2O3 ), copper oxide ( Cu2O, CuO ), zinc oxide (ZnO) and the like.
焼成後の有価金属の酸化物は、XRD法で金属特有のピークを確認することによってその存在を明らかにすることができる。そして、有価金属の酸化物を含む焼成物を王水に溶解させた後、前記ICP分析法で分析することにより、焼成物中の有価金属の含有量を定量することができる。 The existence of the oxide of the valuable metal after firing can be clarified by confirming the peak peculiar to the metal by the XRD method. Then, the content of the valuable metal in the calcined product can be quantified by dissolving the calcined product containing the oxide of the valuable metal in aqua regia and then analyzing by the ICP analysis method.
次に、本実施形態の有価金属の回収方法について作用を説明する。
さて、有価金属を含有する廃棄物から有価金属を回収する場合には、まず分離工程において廃棄物に無機酸溶液を加え、有価金属のイオンを含有する溶解液と不純物を含有する沈殿物とに分離する。このとき、無機酸の濃度や添加量を調整することにより、溶解液中に含まれる有価金属の無機酸塩を増大させるとともに、沈殿物中に含まれる不純物の不溶解物を増大させることができる。
Next, the operation of the method for recovering the valuable metal of the present embodiment will be described.
When recovering valuable metal from waste containing valuable metal, first, an inorganic acid solution is added to the waste in the separation step to prepare a solution containing ions of the valuable metal and a precipitate containing impurities. To separate. At this time, by adjusting the concentration and the amount of the inorganic acid added, the inorganic acid salt of the valuable metal contained in the solution can be increased, and the insoluble matter of the impurities contained in the precipitate can be increased. ..
続いて、シュウ酸塩生成工程において、溶解液にシュウ酸を加えて有価金属のシュウ酸塩の沈殿物を生成させる。この場合、ニッケル等の有価金属のイオンはシュウ酸との反応性が良く、有価金属のシュウ酸塩が速やかに生成して沈殿物となる。一方、リン、スズ等の不純物はシュウ酸との反応性が低く、前記溶解液中に残存しやすい。このため、有価金属と不純物との分離性を高めることができる。 Subsequently, in the oxalate production step, oxalic acid is added to the solution to form a precipitate of valuable metal oxalate. In this case, the ions of a valuable metal such as nickel have good reactivity with oxalic acid, and the oxalate of the valuable metal is rapidly formed and becomes a precipitate. On the other hand, impurities such as phosphorus and tin have low reactivity with oxalic acid and tend to remain in the solution. Therefore, the separability between the valuable metal and the impurities can be improved.
次いで、焼成工程において、有価金属のシュウ酸塩を焼成することにより、有価金属の酸化物を得ることができる。このとき、有価金属のシュウ酸塩から酸化物への反応は容易でかつ発熱反応であることから、弱い強制加熱で速やかに目的とする有価金属の酸化物を得ることができる。 Next, in the firing step, the valuable metal oxide can be obtained by firing the valuable metal oxalate. At this time, since the reaction of the valuable metal from the oxalate to the oxide is easy and is an exothermic reaction, the oxide of the target valuable metal can be quickly obtained by weak forced heating.
以上詳述した実施形態によって得られる効果を以下にまとめて記載する。
(1)この実施形態における有価金属の回収方法では、無機酸により有価金属が溶解された溶解液と不純物を含有する沈殿物に分離する分離工程と、溶解液にシュウ酸を加えて沈殿物を生成させる有価金属のシュウ酸塩生成工程と、有価金属のシュウ酸塩を焼成して有価金属の酸化物を生成させる焼成工程とを含む。このため、分離工程で有価金属と不純物との第1の分離を図り、さらにシュウ酸塩生成工程で有価金属と不純物との第2の分離を図ることができる。
The effects obtained by the embodiments described in detail above are summarized below.
(1) In the method for recovering a valuable metal in this embodiment, a separation step of separating the valuable metal into a solution containing an inorganic acid and a precipitate containing impurities, and a separation step of adding oxalic acid to the solution to form a precipitate. It includes a step of producing a oxalate of a valuable metal to be produced and a firing step of calcining the oxalate of the valuable metal to produce an oxide of the valuable metal. Therefore, the first separation between the valuable metal and the impurities can be achieved in the separation step, and the second separation between the valuable metal and the impurities can be achieved in the oxalate production step.
従って、この実施形態における有価金属の回収方法によれば、不純物の含有量を低減させるとともに、有価金属の含有量を向上させ、かつ簡易な方法で有価金属を回収することができる。 Therefore, according to the method for recovering valuable metal in this embodiment, it is possible to reduce the content of impurities, improve the content of valuable metal, and recover the valuable metal by a simple method.
(2)前記無機酸は硫酸、硝酸又は塩酸である。このため、これらの無機の強酸により、有価金属の無機酸塩を容易かつ迅速に形成することができる。
(3)前記無機酸の濃度は1~2Mである。そのため、溶解液中における有価金属の浸出率を高める一方、不純物の浸出率を抑制することができる。
(2) The inorganic acid is sulfuric acid, nitric acid or hydrochloric acid. Therefore, these inorganic strong acids can easily and quickly form an inorganic acid salt of a valuable metal.
(3) The concentration of the inorganic acid is 1 to 2M. Therefore, it is possible to increase the leaching rate of valuable metals in the solution while suppressing the leaching rate of impurities.
(4)前記有価金属の溶解液のpHは1.5~3.5である。従って、溶解液中における有価金属の浸出率を維持するとともに、有価金属のシュウ酸塩の析出時間を短縮することができる。 (4) The pH of the solution of the valuable metal is 1.5 to 3.5. Therefore, it is possible to maintain the leaching rate of the valuable metal in the solution and shorten the precipitation time of the valuable metal oxalate.
(5)前記有価金属のシュウ酸塩の生成工程において、予め溶解液中に含まれる有価金属含有量を分析し、その有価金属含有量に対して1~3当量のシュウ酸を加える。この場合には、有価金属のシュウ酸塩を十分かつ速やかに生成させることができるとともに、シュウ酸の使用量を適切に設定することができる。 (5) In the step of producing the oxalate of the valuable metal, the content of the valuable metal contained in the solution is analyzed in advance, and 1 to 3 equivalents of oxalic acid is added to the valuable metal content. In this case, the valuable metal oxalate can be sufficiently and quickly produced, and the amount of oxalic acid used can be appropriately set.
(6)前記焼成工程では、有価金属のシュウ酸塩の発熱を伴いながら350~800℃で焼成を行う。このため、少ない強制加熱で焼成を迅速に行うことができるとともに、有価金属の酸化物を容易に取得することができる。 (6) In the firing step, firing is performed at 350 to 800 ° C. with heat generation of the valuable metal oxalate. Therefore, firing can be performed quickly with a small amount of forced heating, and oxides of valuable metals can be easily obtained.
(7)前記有価金属はニッケルである。この場合、焼成物中の酸化ニッケルの含有量を高め、不純物としてのリンやスズの酸化物の生成を抑制することができる。 (7) The valuable metal is nickel. In this case, the content of nickel oxide in the calcined product can be increased, and the formation of oxides of phosphorus and tin as impurities can be suppressed.
以下に、実施例及び比較例を挙げて前記実施形態をさらに具体的に説明する。
(実施例1)
反応容器内にニッケルの廃棄物であるニッケルスラッジ10gを収容し、そこに下記に示すモル濃度の硫酸を50mL添加して撹拌したところ、硫酸ニッケルを含む溶解液と、不純物を含む沈殿物とが得られた。常法に従って沈殿物を濾過し、硫酸ニッケルを含む溶解液を得た。この溶解液のpHを測定するとともに、溶解液中のニッケルと不純物であるリン及びスズの含有量(浸出率)をICP分析法で分析した。
Hereinafter, the embodiment will be described in more detail with reference to Examples and Comparative Examples.
(Example 1)
When 10 g of nickel sludge, which is a waste of nickel, was placed in a reaction vessel, 50 mL of sulfuric acid having a molar concentration shown below was added thereto, and the mixture was stirred, a solution containing nickel sulfate and a precipitate containing impurities were found. Obtained. The precipitate was filtered according to a conventional method to obtain a solution containing nickel sulfate. The pH of this solution was measured, and the content (leaching rate) of nickel and impurities phosphorus and tin in the solution was analyzed by ICP analysis method.
前記硫酸の濃度を0.5M(実施例1-1)、1.0M(実施例1-2)、1.5M(実施例1-3)、2.0M(実施例1-4)、3.0M(実施例1-5)、4.0M(実施例1-6)及び5.0M(実施例1-7)に設定した。 The concentration of sulfuric acid is 0.5M (Example 1-1), 1.0M (Example 1-2), 1.5M (Example 1-3), 2.0M (Example 1-4), 3 It was set to 0.0M (Example 1-5), 4.0M (Example 1-6) and 5.0M (Example 1-7).
次いで、前記溶解液に、ニッケルスラッジ中のニッケル量とほぼ当量のシュウ酸を加えて撹拌し、シュウ酸ニッケルの沈殿物を生成させた。この沈殿物の析出時間(h)を測定した。そして、前記沈殿物を常法により濾過して取得した。続いて、シュウ酸ニッケルを含む沈殿物を電気炉にて700℃で焼成し、酸化ニッケルを含む焼成物を得た。 Next, oxalic acid having an amount equivalent to that of nickel in the nickel sludge was added to the solution and stirred to form a nickel oxalate precipitate. The precipitation time (h) of this precipitate was measured. Then, the precipitate was obtained by filtering by a conventional method. Subsequently, the precipitate containing nickel oxalate was fired in an electric furnace at 700 ° C. to obtain a fired product containing nickel oxide.
得られた焼成物を王水に溶解し、ICP分析法でニッケルと、不純物であるリン及びスズの含有量(質量%)を定量した。それらの結果を表1に示した。
また、前記溶解液のpHと浸出率(質量%)との関係を図1に示し、溶解液のpHと析出時間(反応時間)との関係を図4に示した。
The obtained calcined product was dissolved in aqua regia, and the contents (% by mass) of nickel and impurities phosphorus and tin were quantified by ICP analysis method. The results are shown in Table 1.
Further, the relationship between the pH of the solution and the leaching rate (% by mass) is shown in FIG. 1, and the relationship between the pH of the solution and the precipitation time (reaction time) is shown in FIG.
また、図1に示すように、溶解液のpHを1.5~3.5の範囲に設定することにより、ニッケルの浸出率を高め、リン及びスズの浸出率を抑えることができた。さらに、図4に示すように、溶解液のpHを1.5~3.5の範囲に設定することにより、シュウ酸ニッケルの沈殿物の析出時間を短くすることができた。 Further, as shown in FIG. 1, by setting the pH of the solution in the range of 1.5 to 3.5, the leaching rate of nickel could be increased and the leaching rate of phosphorus and tin could be suppressed. Further, as shown in FIG. 4, by setting the pH of the solution in the range of 1.5 to 3.5, the precipitation time of the nickel oxalate precipitate could be shortened.
(実施例2)
反応容器内にニッケルスラッジ10gを収容し、そこに1Mの硝酸を50mL添加して撹拌したところ、硝酸ニッケルを含む溶解液と、不純物を含む沈殿物とが得られた。常法に従って沈殿物を濾過し、硝酸ニッケルを含む溶解液を得た。この溶解液のpHを測定するとともに、溶解液中のニッケルと不純物であるリン及びスズの含有量(浸出率)をICP分析法で分析した。
(Example 2)
When 10 g of nickel sludge was placed in the reaction vessel, 50 mL of 1 M nitric acid was added thereto, and the mixture was stirred, a solution containing nickel nitrate and a precipitate containing impurities were obtained. The precipitate was filtered according to a conventional method to obtain a solution containing nickel nitrate. The pH of this solution was measured, and the content (leaching rate) of nickel and impurities phosphorus and tin in the solution was analyzed by ICP analysis method.
前記硝酸の濃度を0.5M(実施例2-1)、1.0M(実施例2-2)、1.5M(実施例2-3)、2.0M(実施例2-4)、3.0M(実施例2-5)、4.0M(実施例2-6)及び5.0M(実施例2-7)に設定した。 The concentration of nitric acid was 0.5M (Example 2-1), 1.0M (Example 2-2), 1.5M (Example 2-3), 2.0M (Example 2-4), 3 It was set to 0.0M (Example 2-5), 4.0M (Example 2-6) and 5.0M (Example 2-7).
次いで、前記溶解液に、ニッケルスラッジ中のニッケル量とほぼ当量のシュウ酸を加えて撹拌し、シュウ酸ニッケルの沈殿物を生成させた。この沈殿物を常法により濾過して取得した。続いて、シュウ酸ニッケルを含む沈殿物を電気炉にて700℃で焼成し、酸化ニッケルを含む焼成物を得た。 Next, oxalic acid having an amount equivalent to that of nickel in the nickel sludge was added to the solution and stirred to form a nickel oxalate precipitate. This precipitate was obtained by filtering by a conventional method. Subsequently, the precipitate containing nickel oxalate was fired in an electric furnace at 700 ° C. to obtain a fired product containing nickel oxide.
得られた焼成物を王水に溶解し、ICP分析法でニッケルと、不純物であるリン及びスズの含有量を定量した。それらの結果を表2に示した。
また、前記溶解液のpHと浸出率(質量%)との関係を図2に示し、溶解液のpHと析出時間(h)との関係を図5に示した。
The obtained calcined product was dissolved in aqua regia, and the contents of nickel and impurities phosphorus and tin were quantified by ICP analysis method. The results are shown in Table 2.
Further, the relationship between the pH of the solution and the leaching rate (% by mass) is shown in FIG. 2, and the relationship between the pH of the solution and the precipitation time (h) is shown in FIG.
また、図2に示すように、溶解液のpHを1.5~3.5の範囲に設定することにより、ニッケルの浸出率を高め、リン及びスズの浸出率を抑えることができた。さらに、図5に示すように、溶解液のpHを1.5~3.5の範囲に設定することにより、シュウ酸ニッケルの沈殿物の析出時間を短くすることができた。 Further, as shown in FIG. 2, by setting the pH of the solution in the range of 1.5 to 3.5, the leaching rate of nickel could be increased and the leaching rate of phosphorus and tin could be suppressed. Further, as shown in FIG. 5, by setting the pH of the solution in the range of 1.5 to 3.5, the precipitation time of the nickel oxalate precipitate could be shortened.
(実施例3)
反応容器内にニッケルスラッジ10gを収容し、そこに1Mの塩酸を50mL添加して撹拌したところ、塩化ニッケルを含む溶解液と、不純物を含む沈殿物とが得られた。常法に従って沈殿物を濾過し、塩化ニッケルを含む溶解液を得た。この溶解液のpHを測定するとともに、溶解液中のニッケルと不純物であるリン及びスズの含有量(浸出率)をICP分析法で分析した。
(Example 3)
When 10 g of nickel sludge was placed in the reaction vessel, 50 mL of 1 M hydrochloric acid was added thereto, and the mixture was stirred, a solution containing nickel chloride and a precipitate containing impurities were obtained. The precipitate was filtered according to a conventional method to obtain a solution containing nickel chloride. The pH of this solution was measured, and the content (leaching rate) of nickel and impurities phosphorus and tin in the solution was analyzed by ICP analysis method.
前記塩酸の濃度を0.5M(実施例3-1)、1.0M(実施例3-2)、1.5M(実施例3-3)、2.0M(実施例3-4)、3.0M(実施例3-5)、4.0M(実施例3-6)及び5.0M(実施例3-7)に設定した。 The concentration of hydrochloric acid is 0.5M (Example 3-1), 1.0M (Example 3-2), 1.5M (Example 3-3), 2.0M (Example 3-4), 3 It was set to 9.0M (Example 3-5), 4.0M (Example 3-6) and 5.0M (Example 3-7).
次いで、前記溶解液に、ニッケルスラッジ中のニッケル量とほぼ当量のシュウ酸を加えて撹拌し、シュウ酸ニッケルの沈殿物を生成させた。この沈殿物を常法により濾過して取得した。続いて、シュウ酸ニッケルを含む沈殿物を電気炉にて700℃で焼成し、酸化ニッケルを含む焼成物を得た。 Next, oxalic acid having an amount equivalent to that of nickel in the nickel sludge was added to the solution and stirred to form a nickel oxalate precipitate. This precipitate was obtained by filtering by a conventional method. Subsequently, the precipitate containing nickel oxalate was fired in an electric furnace at 700 ° C. to obtain a fired product containing nickel oxide.
得られた焼成物を王水に溶解し、ICP分析法でニッケルと、不純物であるリン及びスズの含有量を定量した。それらの結果を表3に示した。
また、前記溶解液のpHと浸出率(質量%)との関係を図3に示し、溶解液のpHと析出時間(h)との関係を図6に示した。
The obtained calcined product was dissolved in aqua regia, and the contents of nickel and impurities phosphorus and tin were quantified by ICP analysis method. The results are shown in Table 3.
Further, the relationship between the pH of the solution and the leaching rate (% by mass) is shown in FIG. 3, and the relationship between the pH of the solution and the precipitation time (h) is shown in FIG.
また、図3に示すように、溶解液のpHを1.5~3.5の範囲に設定することにより、ニッケルの浸出率を高め、リン及びスズの浸出率を抑えることができた。さらに、図6に示すように、溶解液のpHを1.5~3.5の範囲に設定することにより、シュウ酸ニッケルの沈殿物の析出時間を短くすることができた。 Further, as shown in FIG. 3, by setting the pH of the solution in the range of 1.5 to 3.5, the leaching rate of nickel could be increased and the leaching rate of phosphorus and tin could be suppressed. Further, as shown in FIG. 6, by setting the pH of the solution in the range of 1.5 to 3.5, the precipitation time of the nickel oxalate precipitate could be shortened.
(実施例4)
実施例1において、ニッケルスラッジの使用量を133kg、1Mの硫酸の使用量を650Lとした以外は実施例1と同様に実施し、酸化ニッケルの焼成物を得た。得られた焼成物を王水に溶解し、ICP分析法でニッケルと、不純物であるリン及びスズの含有量(質量%)を定量した結果、ニッケル68.5質量%、リン0.06質量%及びスズ0.06質量%であった。
(Example 4)
In Example 1, the same procedure as in Example 1 was carried out except that the amount of nickel sludge used was 133 kg and the amount of 1 M sulfuric acid used was 650 L, to obtain a calcined product of nickel oxide. The obtained calcined product was dissolved in royal water, and the content (% by mass) of nickel and impurities phosphorus and tin was quantified by ICP analysis method. As a result, nickel was 68.5% by mass and phosphorus was 0.06% by mass. And tin was 0.06% by mass.
従って、ニッケルスラッジの使用量を増大しても、実施例1~3と同様にニッケルの回収率を高め、不純物の含有量を抑制することができた。
(実施例5)
前記実施例1の焼成工程において、シュウ酸ニッケルを含む沈殿物の焼成温度を300~900℃に100℃間隔で変化させるとともに、焼成時間を30~120分まで30分間隔で変化させ、焼成物中のニッケルの含有量(質量%)をICP分析法で定量した。その結果を表4に示した。
Therefore, even if the amount of nickel sludge used was increased, the recovery rate of nickel could be increased and the content of impurities could be suppressed as in Examples 1 to 3.
(Example 5)
In the firing step of Example 1, the firing temperature of the precipitate containing nickel oxalate was changed to 300 to 900 ° C. at 100 ° C. intervals, and the firing time was changed from 30 to 120 minutes at 30 minute intervals. The nickel content (% by mass) in the calcination was quantified by the ICP analysis method. The results are shown in Table 4.
(比較例1)
反応容器内にニッケルスラッジ10gを収容し、そこに1Mの硫酸50mLを添加して撹拌したところ、硫酸ニッケルを含む溶解液と、不純物を含む沈殿物とが得られた。常法に従って沈殿物を濾過し、硫酸ニッケルを含む溶解液を得た。この溶解液に、ニッケルスラッジ中のニッケル量とほぼ当量の水酸化ナトリウムを加えて撹拌し、水酸化ニッケルの沈殿物を生成させた。この沈殿物を常法により濾過して取得した。続いて、水酸化ニッケルの沈殿物を電気炉にて700℃で焼成し、酸化ニッケルを含む焼成物を得た。
(Comparative Example 1)
When 10 g of nickel sludge was placed in the reaction vessel, 50 mL of 1 M sulfuric acid was added thereto, and the mixture was stirred, a solution containing nickel sulfate and a precipitate containing impurities were obtained. The precipitate was filtered according to a conventional method to obtain a solution containing nickel sulfate. To this solution was added sodium hydroxide in approximately the same amount as the amount of nickel in the nickel sludge and stirred to form a nickel hydroxide precipitate. This precipitate was obtained by filtering by a conventional method. Subsequently, the nickel hydroxide precipitate was fired in an electric furnace at 700 ° C. to obtain a fired product containing nickel oxide.
得られた焼成物を王水に溶解し、ICP分析法でニッケルと、不純物であるリン及びスズの含有量を定量した結果、ニッケル63.4質量%、リン4.3質量%及びスズ3.8質量%であった。この結果から、焼成物中の不純物であるリン及びスズの含有量がそれぞれ0.1質量%を遥かに超える高い値を示した。
The obtained calcined product was dissolved in royal water, and the contents of nickel and impurities phosphorus and tin were quantified by ICP analysis. As a result, nickel 63.4% by mass, phosphorus 4.3% by mass and
なお、前記実施形態を次のように変更して具体化することも可能である。
・前記分離工程の前に、廃棄物中の夾雑物を濾過して除去するなどの前処理工程を設けてもよい。
It is also possible to modify and embody the embodiment as follows.
-Before the separation step, a pretreatment step such as filtering and removing impurities in the waste may be provided.
・前記焼成工程の後に、焼成物の粒度を調整するなどの後処理工程を設けることも可能である。
・前記廃棄物中には、複数の有価金属が含まれていても差支えない。
-It is also possible to provide a post-treatment step such as adjusting the particle size of the fired product after the firing step.
-The waste may contain a plurality of valuable metals.
・前記有価金属のシュウ酸塩に代えて、有価金属の炭酸塩や有価金属の水酸化物を生成させるように構成してもよい。
-Instead of the oxalate of the precious metal, it may be configured to generate a carbonate of the precious metal or a hydroxide of the valuable metal.
Claims (4)
前記溶解液にシュウ酸を加えて有価金属のシュウ酸塩の沈殿物を生成させる有価金属のシュウ酸塩生成工程と、
前記有価金属のシュウ酸塩を焼成して、リン及びスズの含有量が各々0.1質量%以下である有価金属の酸化物を生成させる焼成工程とを含み、
前記無機酸の濃度は1~2Mであり、
前記有価金属の溶解液のpHは1.5~3.5であり、
前記有価金属はニッケルである有価金属の回収方法。 A separation step in which an inorganic acid is added to a waste containing a valuable metal to form a precipitate containing a solution containing the valuable metal and an impurity containing phosphorus and tin, and the precipitate is filtered and separated.
A valuable metal oxalate production step in which oxalic acid is added to the solution to form a precious metal oxalate precipitate.
It includes a firing step of calcining the oxalate of the precious metal to produce an oxide of the valuable metal having a phosphorus and tin contents of 0.1% by mass or less, respectively .
The concentration of the inorganic acid is 1 to 2 M, and the concentration is 1 to 2 M.
The pH of the solution of the valuable metal is 1.5 to 3.5, and the pH is 1.5 to 3.5.
The valuable metal is nickel. A method for recovering a valuable metal.
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| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2003176112A (en) | 2001-12-11 | 2003-06-24 | National Institute Of Advanced Industrial & Technology | Porous tin phosphate and method for producing the same |
| JP2007323868A (en) | 2006-05-31 | 2007-12-13 | Toyota Motor Corp | Method for recovering metal constituting electrode from lithium battery |
| JP2009228030A (en) | 2008-03-19 | 2009-10-08 | Toda Kogyo Corp | Method for recovering residual nickel in electroless plating waste solution |
| JP2010277868A (en) | 2009-05-29 | 2010-12-09 | Jx Nippon Mining & Metals Corp | Metal recovery method |
| JP2011074410A (en) | 2009-09-29 | 2011-04-14 | Jx Nippon Mining & Metals Corp | Method for separating and recovering nickel and lithium |
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| Publication number | Priority date | Publication date | Assignee | Title |
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| US3953306A (en) * | 1973-10-03 | 1976-04-27 | Dart Environment And Services Company | Metal recovery from waste treatment sludges |
| JPS59185770A (en) * | 1983-04-05 | 1984-10-22 | Oosakafu | Method for recovering nickel from waste chemical nickel plating bath |
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Patent Citations (5)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2003176112A (en) | 2001-12-11 | 2003-06-24 | National Institute Of Advanced Industrial & Technology | Porous tin phosphate and method for producing the same |
| JP2007323868A (en) | 2006-05-31 | 2007-12-13 | Toyota Motor Corp | Method for recovering metal constituting electrode from lithium battery |
| JP2009228030A (en) | 2008-03-19 | 2009-10-08 | Toda Kogyo Corp | Method for recovering residual nickel in electroless plating waste solution |
| JP2010277868A (en) | 2009-05-29 | 2010-12-09 | Jx Nippon Mining & Metals Corp | Metal recovery method |
| JP2011074410A (en) | 2009-09-29 | 2011-04-14 | Jx Nippon Mining & Metals Corp | Method for separating and recovering nickel and lithium |
Non-Patent Citations (1)
| Title |
|---|
| 梅村耕造,種々の雰囲気中でのニッケル,コバルトおよび鉄(II)シュウ酸塩2水和物の熱分解,日本化学会誌,日本,日本化学会,1975年06月10日,Vol.1975, No.6,p.969-975 |
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