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JP6174395B2 - Method for recovering copper and method for producing copper oxide - Google Patents
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JP6174395B2 - Method for recovering copper and method for producing copper oxide - Google Patents

Method for recovering copper and method for producing copper oxide Download PDF

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JP6174395B2
JP6174395B2 JP2013139293A JP2013139293A JP6174395B2 JP 6174395 B2 JP6174395 B2 JP 6174395B2 JP 2013139293 A JP2013139293 A JP 2013139293A JP 2013139293 A JP2013139293 A JP 2013139293A JP 6174395 B2 JP6174395 B2 JP 6174395B2
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copper
low
grade coal
mixture
lignite
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JP2015010276A (en
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廣幸 横島
廣幸 横島
長谷川 清
清 長谷川
吉野 淳
淳 吉野
才川 哲朗
哲朗 才川
邦明 関口
邦明 関口
幸久 廣山
幸久 廣山
恭之 宝田
恭之 宝田
和好 佐藤
和好 佐藤
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Gunma University NUC
Resonac Corp
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Gunma University NUC
Hitachi Chemical Co Ltd
Showa Denko Materials Co Ltd
Resonac Corp
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    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
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    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

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Description

本発明は、銅の回収方法及び酸化銅の製造方法に関する。   The present invention relates to a method for recovering copper and a method for producing copper oxide.

プリント配線板等の製造においては、回路形成のために金属銅を溶解するエッチングが行われる。このため、銅イオンを含む廃液が大量に発生する。銅イオンを含む廃液は、自然環境へ悪影響を与える恐れがあるためにそのまま排出することができない。そこで、廃液を物理的に固形化する方法、電気を用いて銅イオンを金属化する方法等が実用化されている。廃液を物理的に固形化する方法としては、沈殿法及び焼結法がある(例えば、特許文献1〜5参照)。また、電気を用いて銅イオンを金属化する方法としては、電析法がある(例えば、特許文献6参照)。   In manufacturing a printed wiring board or the like, etching for dissolving metallic copper is performed for circuit formation. For this reason, a large amount of waste liquid containing copper ions is generated. The waste liquid containing copper ions cannot be discharged as it is because it may adversely affect the natural environment. Therefore, a method of physically solidifying the waste liquid, a method of metallizing copper ions using electricity, and the like have been put into practical use. As a method for physically solidifying the waste liquid, there are a precipitation method and a sintering method (for example, see Patent Documents 1 to 5). Moreover, as a method of metallizing copper ions using electricity, there is an electrodeposition method (see, for example, Patent Document 6).

特開平11−60239号公報Japanese Patent Laid-Open No. 11-60239 特開2003−213346号公報JP 2003-213346 A 特開2009−167462号公報JP 2009-167462 A 特開平7−33435号公報Japanese Patent Laid-Open No. 7-33435 特開平7−3475号公報JP-A-7-3475 特開2002−60986号公報JP 2002-60986 A

沈殿法は、大規模な処理設備が必要であり、その工程もpH調整、沈殿助剤の添加、沈降工程、ろ過工程、回収工程等の多数からなり複雑である。また、各工程での処理に長時間を要する。更に、大量の水を使用する必要がある。焼結法は、上記同様に大規模な処理設備が必要であり、焼結時に700℃以上の温度が必要である。従って、その燃焼エネルギーを得るために大量の化石燃料が必要である。電析法は、上記同様に大規模な設備が必要であり、処理時間は短いが大量の電気を消費する。   The precipitation method requires a large-scale processing facility, and the process is complicated and includes many processes such as pH adjustment, addition of a precipitation aid, precipitation process, filtration process, and recovery process. Moreover, a long time is required for processing in each process. Furthermore, it is necessary to use a large amount of water. As described above, the sintering method requires a large-scale processing facility, and requires a temperature of 700 ° C. or higher during sintering. Therefore, a large amount of fossil fuel is required to obtain the combustion energy. As described above, the electrodeposition method requires large-scale equipment, and consumes a large amount of electricity although the processing time is short.

本発明は上記事情に鑑み、エネルギー消費が抑制されかつ簡便な方法で銅を回収する方法、及び酸化銅の製造方法を提供することを目的とする。   In view of the above circumstances, an object of the present invention is to provide a method for recovering copper by a simple method with reduced energy consumption and a method for producing copper oxide.

上記課題を解決するための手段は、以下のとおりである。   Means for solving the above problems are as follows.

<1>銅イオン、低品位炭、及び銅と錯体を形成しうる窒素原子含有化合物を少なくとも含む混合物を準備する工程と、銅を担持した前記低品位炭を前記混合物から取り出す工程と、前記混合物から取り出した前記低品位炭を熱処理する工程と、を含む銅の回収方法。 <1> a step of preparing a mixture containing at least a copper ion, a low-grade coal, and a nitrogen atom-containing compound capable of forming a complex with copper, a step of taking out the low-grade coal carrying copper from the mixture, and the mixture And a step of heat-treating the low-grade coal taken out from the process.

<2>前記熱処理の温度が600℃以下である、<1>に記載の銅の回収方法。 <2> The copper recovery method according to <1>, wherein the temperature of the heat treatment is 600 ° C. or less.

<3>前記混合物がさらに水を含む、<1>又は<2>に記載の銅の回収方法。 <3> The copper recovery method according to <1> or <2>, wherein the mixture further contains water.

<4>前記混合物の25℃におけるpHが8〜11の範囲にある、<1>〜<3>のいずれかに記載の銅の回収方法。 <4> The method for recovering copper according to any one of <1> to <3>, wherein the pH of the mixture at 25 ° C. is in the range of 8 to 11.

<5>銅イオン、低品位炭、及び銅と錯体を形成しうる窒素原子含有化合物を少なくとも含む混合物を準備する工程と、銅を担持した前記低品位炭を前記混合物から取り出す工程と、前記混合物から取り出した前記低品位炭を熱処理する工程と、を含む酸化銅の製造方法。 <5> preparing a mixture including at least a copper ion, a low-grade coal, and a nitrogen atom-containing compound capable of forming a complex with copper, a step of removing the low-grade coal carrying copper from the mixture, and the mixture And a step of heat-treating the low-grade coal taken out from the process.

本発明によれば、エネルギー消費が抑制されかつ簡便な方法で銅を回収する方法、及び酸化銅の製造方法が提供される。   ADVANTAGE OF THE INVENTION According to this invention, energy consumption is suppressed and the method of collect | recovering copper by a simple method and the manufacturing method of copper oxide are provided.

本明細書において「〜」を用いて示された数値範囲は、「〜」の前後に記載される数値をそれぞれ最小値及び最大値として含む範囲を示す。さらに本明細書において組成物中の各成分の含有量は、組成物中に各成分に該当する物質が複数存在する場合、特に断らない限り、組成物中に存在する当該複数の物質の合計量を意味する。   In the present specification, a numerical range indicated using “to” indicates a range including the numerical values described before and after “to” as the minimum value and the maximum value, respectively. Further, in the present specification, the content of each component in the composition is the total amount of the plurality of substances present in the composition unless there is a specific notice when there are a plurality of substances corresponding to each component in the composition. Means.

<銅の回収方法>
本発明の銅の回収方法は、銅イオン、低品位炭、及び銅と錯体を形成しうる窒素原子含有化合物を少なくとも含む混合物を準備する工程と、銅を担持した前記低品位炭を前記混合物から取り出す工程と、前記混合物から取り出した前記低品位炭を熱処理する工程と、を含む。
<Copper recovery method>
The method for recovering copper according to the present invention includes a step of preparing a mixture including at least a copper ion, a low-grade coal, and a nitrogen atom-containing compound capable of forming a complex with copper, and the low-grade coal supporting copper from the mixture. And a step of heat-treating the low-grade coal extracted from the mixture.

前記混合物を準備する方法は、特に制限されない。例えば、プリント配線板等の製造工程で生じた銅イオンを含む廃液に低品位炭と、銅と錯体を形成しうる窒素原子含有化合物(以下、単に窒素原子含有化合物ともいう)とを混合して準備することができる。前記混合の方法は特に制限されない。例えば、銅イオンを含む廃液等の溶液に、窒素原子含有化合物をそのまま又は溶液の状態で混合し、次いで低品位炭を混合する方法を挙げることができる。前記混合物は塩基性であることが好ましい。例えば、銅の低品位炭への担持を促進する観点からは25℃におけるpHが8以上であることが好ましく、水酸化銅の生成を抑制する観点からは11以下であることが好ましい。より好ましくは、9〜10の範囲内である。   The method for preparing the mixture is not particularly limited. For example, by mixing a low-grade coal and a nitrogen atom-containing compound capable of forming a complex with copper (hereinafter, also simply referred to as a nitrogen atom-containing compound) into a waste liquid containing copper ions generated in a manufacturing process such as a printed wiring board. Can be prepared. The mixing method is not particularly limited. For example, a method in which a nitrogen atom-containing compound is mixed as it is or in a solution state with a solution such as a waste liquid containing copper ions, and then a low-grade coal is mixed. The mixture is preferably basic. For example, the pH at 25 ° C. is preferably 8 or more from the viewpoint of promoting the loading of copper on low-grade coal, and is preferably 11 or less from the viewpoint of suppressing the production of copper hydroxide. More preferably, it is in the range of 9-10.

前記低品位炭は、一般に発熱量が5,000kcal/kg以下の石炭として定義されるものであり、石炭資源の半分を占めている。具体的には、褐炭(炭化度70%〜78%)、亜炭(炭化度70%以下)、泥炭(炭化度60%以下)等を挙げることができる。低品位炭は、炭化度の高い石炭と比較してヒドロキシ基、カルボキシ基等の酸素含有官能基を多く有する。これらの酸素含有官能基がイオン交換基として作用し、銅が低品位炭に担持すると考えられる。   The low-grade coal is generally defined as coal having a calorific value of 5,000 kcal / kg or less, and occupies half of coal resources. Specific examples include lignite (carbonization degree 70% to 78%), lignite (carbonization degree 70% or less), peat (carbonization degree 60% or less), and the like. Low-grade coal has many oxygen-containing functional groups such as hydroxy groups and carboxy groups as compared with coal having a high carbonization degree. It is thought that these oxygen-containing functional groups act as ion exchange groups and copper is supported on low-grade coal.

前記低品位炭は粒子状であることが好ましい。粒子径の下限は特に制限されず、凝集による取扱い性の低下を抑制する観点からは体積平均粒子径が30μm以上であることが好ましく、45μm以上であることがより好ましい。低品位炭の粒子径の上限は特に制限されず、例えば後述する酸化銅粒子の所望の粒子径に応じて選択できる。前記体積平均粒子径は、ふるいによる分級によって測定することができる。
前記混合物中の低品位炭の含有率は、特に制限されない。低品位炭の銅担持率の観点からは、10質量%以上であることが好ましく、20質量%以上であることがより好ましい。
前記低品位炭は、あらかじめ表面の不純物を除去してもよい。具体的には、塩酸で洗浄する方法等を挙げることができる。
The low-grade coal is preferably particulate. The lower limit of the particle diameter is not particularly limited, and the volume average particle diameter is preferably 30 μm or more and more preferably 45 μm or more from the viewpoint of suppressing the decrease in handleability due to aggregation. The upper limit of the particle size of the low-grade coal is not particularly limited, and can be selected according to, for example, a desired particle size of copper oxide particles described later. The volume average particle diameter can be measured by classification using a sieve.
The content of low-grade coal in the mixture is not particularly limited. From the viewpoint of the copper loading of the low-grade coal, it is preferably 10% by mass or more, and more preferably 20% by mass or more.
The low-grade coal may remove surface impurities in advance. Specific examples include a method of washing with hydrochloric acid.

前記窒素原子含有化合物は、銅と錯体を形成しうる化合物であれば特に制限されない。窒素原子含有化合物が混合物中で銅と錯体を形成することにより、銅の低品位炭への担持が促進されると考えられる。具体的には、アンモニア、第1級〜第3級アミン等のアミノ基を有する化合物;アミド基を有する化合物;コリン等の第4級アンモニウムカチオンなどを挙げることができる。銅との錯体形成の観点からは、アンモニア及び1級〜3級アミン等のアミノ基を有する化合物が好ましい。前記窒素原子含有化合物は1種を単独で用いても、2種以上を用いてもよい。   The nitrogen atom-containing compound is not particularly limited as long as it can form a complex with copper. It is considered that the loading of copper on low-grade coal is promoted by the nitrogen atom-containing compound forming a complex with copper in the mixture. Specific examples include compounds having an amino group such as ammonia and primary to tertiary amines; compounds having an amide group; quaternary ammonium cations such as choline. From the viewpoint of complex formation with copper, compounds having amino groups such as ammonia and primary to tertiary amines are preferred. The said nitrogen atom containing compound may be used individually by 1 type, or may use 2 or more types.

前記窒素原子含有化合物の前記混合物中の含有率は特に制限されない。例えば、前記混合物の25℃におけるpHが8〜11の範囲となる含有率であることが好ましく、25℃におけるpHが9〜10となる含有率であることがより好ましい。   The content of the nitrogen atom-containing compound in the mixture is not particularly limited. For example, it is preferable that it is the content rate from which the pH in 25 degreeC of the said mixture becomes the range of 8-11, and it is more preferable that it is the content rate in which pH in 25 degreeC becomes 9-10.

前記混合物は、低品位炭及び窒素原子含有化合物以外の成分を含んでもよい。その他の成分としては、水、有機溶剤、銅イオンを含む廃液に含まれる塩素イオン、硫酸イオン等の成分などが挙げられる。前記混合物中の銅イオンの濃度は、特に制限されない。   The mixture may contain components other than the low-grade coal and the nitrogen atom-containing compound. Examples of other components include water, organic solvents, and components such as chlorine ions and sulfate ions contained in a waste liquid containing copper ions. The concentration of copper ions in the mixture is not particularly limited.

前記銅の回収方法は、銅の低品位炭への担持を促進するため、前記混合物を撹拌する工程を含んでもよい。撹拌の方法、温度、時間等の条件は特に制限されない。例えば、室温(25℃)で10〜60分間、攪拌機を用いて行うことができる。   The copper recovery method may include a step of stirring the mixture in order to promote loading of copper on low-grade coal. Conditions such as the stirring method, temperature and time are not particularly limited. For example, it can be performed using a stirrer at room temperature (25 ° C.) for 10 to 60 minutes.

前記混合物から銅が担持した低品位炭を取り出す工程は特に制限されず、一般的なろ過等の方法により行うことができる。例えば、吸引ろ過器でメンブレンフィルターを用いて行うことができる。   The step of taking out the low-grade coal supported by copper from the mixture is not particularly limited, and can be performed by a general method such as filtration. For example, it can be performed using a membrane filter with a suction filter.

前記混合物から取り出した、銅が担持した低品位炭を熱処理することにより、低品位炭が分解して消失し、銅を酸化銅の状態で回収することができる。前記熱処理の温度は、エネルギー消費を抑制する観点からは低いことが好ましい。本発明者らは、銅を担持した低品位炭が、銅を担持しない状態の低品位炭よりも低い温度で分解することを見出した。この理由は、低品位炭に担持している銅が触媒として作用し、低品位炭の低温での分解を促進するためと推測される。従って、本発明の方法によれば、焼結法等の従来技術よりも低い温度で低品位炭を分解し、銅を回収することができる。   By heat-treating the low-grade coal supported by copper taken out from the mixture, the low-grade coal is decomposed and disappears, and copper can be recovered in the form of copper oxide. The temperature of the heat treatment is preferably low from the viewpoint of suppressing energy consumption. The present inventors have found that low-grade coal carrying copper is decomposed at a lower temperature than low-grade coal not carrying copper. The reason for this is presumed to be that the copper supported on the low-grade coal acts as a catalyst and promotes the decomposition of the low-grade coal at a low temperature. Therefore, according to the method of the present invention, low-grade coal can be decomposed and copper can be recovered at a temperature lower than that of conventional techniques such as a sintering method.

この点、特開2008−248363は金属イオンを含む廃液から金属を回収する方法として、無電解ニッケルめっき廃液に塩基性水溶液及び褐炭等の低品位炭粒子を添加し、ニッケルを低品位炭粒子に担持させ、熱処理する方法が知られている。しかしながら、ニッケルを担持した低品位炭については、ニッケルを担持していない低品位炭の分解温度よりも低い温度で分解する傾向は確認されていない。   In this regard, Japanese Patent Application Laid-Open No. 2008-248363 adds a low-grade coal particle such as a basic aqueous solution and lignite to an electroless nickel plating waste liquid as a method for recovering a metal from a waste liquid containing metal ions, and converts the nickel into a low-grade coal particle. A method of carrying and heat-treating is known. However, the tendency for the low-grade coal carrying nickel to decompose at a temperature lower than the decomposition temperature of the low-grade coal not carrying nickel has not been confirmed.

前記熱処理の温度の上限は、例えば600℃以下とすることができ、500℃以下であることが好ましく、300℃以下であることがより好ましい。前記熱処理の温度の下限は銅を担持した低品位炭が充分に分解する温度であればよく、例えば150℃以上とすることが好ましい。前記熱処理の時間は特に制限されず、例えば60分〜180分の範囲内とすることができる。前記熱処理の方法は特に制限されず、例えば一般的な乾燥機を用いて行うことができる。   The upper limit of the temperature of the heat treatment can be, for example, 600 ° C. or less, preferably 500 ° C. or less, and more preferably 300 ° C. or less. The lower limit of the temperature of the heat treatment may be a temperature at which the low-grade coal carrying copper is sufficiently decomposed, and is preferably set to, for example, 150 ° C. or higher. The time for the heat treatment is not particularly limited, and can be, for example, in the range of 60 minutes to 180 minutes. The method for the heat treatment is not particularly limited, and can be performed using, for example, a general dryer.

<酸化銅の製造方法>
本発明の酸化銅の製造方法は、銅イオン、低品位炭、及び銅と錯体を形成しうる窒素原子含有化合物を少なくとも含む混合物を準備する工程と、銅を担持した前記低品位炭を前記混合物から取り出す工程と、前記混合物から取り出した前記低品位炭を熱処理する工程と、を含む。前記混合物に含まれる各成分の具体例及び好ましい態様、並びに各工程の具体例及び好ましい態様は、上述の銅の回収方法におけるものと同様である。
<Method for producing copper oxide>
The method for producing copper oxide of the present invention comprises preparing a mixture containing at least a copper ion, a low-grade coal, and a nitrogen atom-containing compound capable of forming a complex with copper, and the low-grade coal supporting copper on the mixture. And a step of heat-treating the low-grade coal extracted from the mixture. Specific examples and preferred embodiments of the respective components contained in the mixture, and specific examples and preferred embodiments of the respective steps are the same as those in the above-described copper recovery method.

前記方法により得られる酸化銅は、還元して金属銅として利用することができる。還元の方法は特に制限されず、一般に使用される方法を用いることができる。例えば、水素還元することで銅を得ることができる。   The copper oxide obtained by the above method can be reduced and used as metallic copper. The reduction method is not particularly limited, and a commonly used method can be used. For example, copper can be obtained by hydrogen reduction.

前記酸化銅は、通常は粒子の状態で回収される。その場合の酸化銅の粒径は、低品位炭の粒径が大きい程大きくなる傾向にある。従って、低品位炭の粒径を調節することにより、所望の粒径の酸化銅を得ることができる。前記酸化銅の粒径は特に制限されず、例えば体積平均粒子径で45μm〜2000μmの範囲内から選択することができる。   The copper oxide is usually recovered in the form of particles. In this case, the particle size of the copper oxide tends to increase as the particle size of the low-grade coal increases. Therefore, by adjusting the particle size of the low-grade coal, copper oxide having a desired particle size can be obtained. The particle diameter of the copper oxide is not particularly limited, and can be selected, for example, from the range of 45 μm to 2000 μm in volume average particle diameter.

<実施例>
以下、実施例により本発明を詳細に説明する。ただし、本発明はこれらの実施例により何ら制限されるものではない。なお「%」は質量基準である。
<Example>
Hereinafter, the present invention will be described in detail by way of examples. However, this invention is not restrict | limited at all by these Examples. “%” Is based on mass.

[実施例1]
銅イオンを含む廃液(塩酸10%、銅イオン濃度30g/L)にアンモニア水を加え、25℃におけるpHを8に調整した。次に、pH調整をした廃液1Lに対し褐炭(オーストラリア・ロイヤン(Loy−Yang)産、体積平均粒径を45μm〜74μmの範囲内に調整)を100g加え、攪拌を10分間行い、静止沈降を30分間以上行った。その後、吸引ろ過器でメンブレンフィルターを用いて銅を担持した褐炭を廃液から取り出した。この銅を担持した褐炭を250℃の乾燥炉で180分間熱処理し、残分を回収した。評価は、褐炭への銅の銅担持率、残分の回収率、及び残分中の銅含有率を後述する方法により測定することで行った。評価結果を表2に示す。
[Example 1]
Ammonia water was added to a waste solution containing copper ions (hydrochloric acid 10%, copper ion concentration 30 g / L), and the pH at 25 ° C. was adjusted to 8. Next, 100 g of brown coal (produced by Loy-Yang, Australia, volume average particle size adjusted within the range of 45 μm to 74 μm) is added to 1 L of pH adjusted waste liquid, and the mixture is stirred for 10 minutes to perform static sedimentation. It went for 30 minutes or more. Then, the lignite supporting copper was taken out from the waste liquid using a membrane filter with a suction filter. The copper-supported lignite was heat treated for 180 minutes in a 250 ° C. drying furnace, and the residue was recovered. The evaluation was performed by measuring the copper loading rate of the copper to the brown coal, the recovery rate of the residue, and the copper content rate in the residue by the method described later. The evaluation results are shown in Table 2.

上記褐炭の工業分析値及び元素分析値は以下の表1に示す通りである。
Industrial analysis values and elemental analysis values of the lignite are as shown in Table 1 below.

[実施例2]
廃液の25℃におけるpHを11に調整した以外は実施例1と同様の工程を実施し、実施例1と同様の評価を行った。評価結果を表2に示す。
[Example 2]
Except that the pH of the waste liquid at 25 ° C. was adjusted to 11, the same steps as in Example 1 were performed, and the same evaluation as in Example 1 was performed. The evaluation results are shown in Table 2.

[実施例3]
廃液の25℃におけるpHを9.5に調整し、熱処理を400℃の乾燥炉で180分行った以外は実施例1と同様の工程を実施し、実施例1と同様の評価を行った。評価結果を表2に示す。
[Example 3]
The same process as in Example 1 was performed except that the pH of the waste liquid at 25 ° C. was adjusted to 9.5 and the heat treatment was performed in a drying furnace at 400 ° C. for 180 minutes, and the same evaluation as in Example 1 was performed. The evaluation results are shown in Table 2.

[実施例4]
廃液の25℃におけるpHを9.5に調整し、熱処理を150℃の乾燥炉で180分行った以外は実施例1と同様の工程を実施し、実施例1と同様の評価を行った。評価結果を表2に示す。
[Example 4]
The same process as in Example 1 was carried out except that the pH of the waste liquid at 25 ° C. was adjusted to 9.5 and the heat treatment was performed in a drying furnace at 150 ° C. for 180 minutes, and the same evaluation as in Example 1 was performed. The evaluation results are shown in Table 2.

[比較例1]
廃液にアンモニア水を加えなかった以外は実施例1と同様の工程を実施し、実施例1と同様の評価を行った。廃液の25℃におけるpHは1以下であった。評価結果を表2に示す。なお、廃液から取り出した褐炭を実施例1と同じ条件で熱処理を行っても褐炭が分解せず、100g残存した。
[Comparative Example 1]
The same processes as in Example 1 were performed except that ammonia water was not added to the waste liquid, and the same evaluation as in Example 1 was performed. The pH of the waste liquid at 25 ° C. was 1 or less. The evaluation results are shown in Table 2. In addition, even if the lignite extracted from the waste liquid was heat-treated under the same conditions as in Example 1, the lignite was not decomposed and 100 g remained.

[比較例2]
廃液に褐炭を加えなかったことと、25℃におけるpHを9.5に調整したこと以外は実施例1と同様の工程を実施し、実施例1と同様の評価を行った。なお、熱処理後は塩化銅が64g残存した。評価結果を表2に示す。
[Comparative Example 2]
Except that lignite was not added to the waste liquid and the pH at 25 ° C. was adjusted to 9.5, the same steps as in Example 1 were performed, and the same evaluation as in Example 1 was performed. Note that 64 g of copper chloride remained after the heat treatment. The evaluation results are shown in Table 2.

(褐炭への銅の銅担持率の評価)
褐炭への銅の担持率は、以下のようにして測定した。すなわち、銅を担持した褐炭を90℃で1時間乾燥後、その質量(M1)を測定する。次いで、前記の銅を担持した褐炭を混酸(体積比で塩酸3:硝酸1)に混合して銅を溶解し、溶解した混酸中の銅濃度を原子吸光度計で測定し銅の質量(M2)を算出する。下記計算式1により、褐炭の銅担持率(%)を計算する。
(Evaluation of copper loading on lignite)
The loading ratio of copper on lignite was measured as follows. That is, the lignite with copper supported is dried at 90 ° C. for 1 hour, and then its mass (M1) is measured. Next, the lignite supporting the copper is mixed with a mixed acid (volume ratio of hydrochloric acid 3: nitric acid 1) to dissolve copper, and the copper concentration in the dissolved mixed acid is measured with an atomic absorption meter, and the mass of copper (M2) Is calculated. The copper loading rate (%) of lignite is calculated by the following calculation formula 1.

(残分の回収率の評価)
残分の回収率は、以下のようにして測定した。すなわち、銅を担持した褐炭を90℃で1時間乾燥後、その質量(M1)を測定する。次いで、各実施例に記載の条件で熱処理を行った後、回収した残分の質量(M3)を測定する。下記計算式2により、残分の回収率(%)を計算する。
(Evaluation of recovery rate of remaining part)
The recovery rate of the residue was measured as follows. That is, the lignite with copper supported is dried at 90 ° C. for 1 hour, and then its mass (M1) is measured. Subsequently, after heat-treating under the conditions described in each Example, the mass (M3) of the recovered residue is measured. The remaining recovery rate (%) is calculated by the following calculation formula 2.

(残分中の銅含有率の評価)
回収した残分中の銅含有率は、以下のようにして測定した。すなわち、回収した残分の質量(M3)を測定後、この残分を混酸(体積比で塩酸3:硝酸1)で溶解した後、原子吸光光度計で銅濃度を測定し銅の質量(M4)を算出する。下記計算式3により、残分中の銅含有率を計算する。残分中の銅含有率が80.0%に近いことは、残分中の酸化銅の割合が100%に近く、褐炭が熱処理により充分に分解していることを意味する。
(Evaluation of copper content in the remainder)
The copper content in the collected residue was measured as follows. That is, after measuring the mass (M3) of the recovered residue, this residue was dissolved with a mixed acid (hydrochloric acid 3: nitric acid 1 by volume), and then the copper concentration was measured with an atomic absorption photometer to measure the mass of copper (M4 ) Is calculated. The copper content in the residue is calculated by the following calculation formula 3. The copper content in the residue being close to 80.0% means that the ratio of copper oxide in the residue is close to 100%, and the lignite has been sufficiently decomposed by heat treatment.

表2に示すように、実施例1〜4における低品位炭の銅担持率は9%を超えていた。また、回収された残分中の銅の含有率は80.0%であり、熱処理により褐炭がほぼ分解していることが分かった。
廃液にアンモニア水を加えなかった比較例1は褐炭への銅の担持率が0.0%であった。また、実施例1と同じ条件で熱処理を行っても褐炭が分解せずに残存した。廃液に褐炭を加えなかった比較例2は熱処理後に塩化銅が残存した。この場合、銅の回収率も少なく、また塩化銅が残るため、銅のみを回収するのは困難である。
As shown in Table 2, the copper loading of the low-grade coal in Examples 1 to 4 exceeded 9%. Moreover, the content rate of copper in the collect | recovered residue was 80.0%, and it turned out that the brown coal has decomposed | disassembled substantially by heat processing.
In Comparative Example 1 in which ammonia water was not added to the waste liquid, the loading ratio of copper to lignite was 0.0%. Moreover, even if it heat-processed on the same conditions as Example 1, lignite remained without decomposing | disassembling. In Comparative Example 2 in which lignite was not added to the waste liquid, copper chloride remained after the heat treatment. In this case, the copper recovery rate is small and copper chloride remains, so that it is difficult to recover only copper.

Claims (4)

銅イオン、低品位炭、及び銅と錯体を形成しうる窒素原子含有化合物を少なくとも含む混合物を準備する工程と、銅を担持した前記低品位炭を前記混合物から取り出す工程と、前記混合物から取り出した前記低品位炭を熱処理する工程と、を含み、前記熱処理の温度が250℃以下である、銅の回収方法。 A step of preparing a mixture containing at least a copper ion, a low-grade coal, and a nitrogen atom-containing compound capable of forming a complex with copper, a step of taking out the low-grade coal carrying copper from the mixture, and taking out of the mixture wherein the step of heat treating the low-grade coal, only including, the temperature of the heat treatment is 250 ° C. or less, the recovery method of copper. 前記混合物がさらに水を含む、請求項に記載の銅の回収方法。 The copper recovery method according to claim 1 , wherein the mixture further contains water. 前記混合物の25℃におけるpHが8〜11の範囲にある、請求項1又は請求項2に記載の銅の回収方法。 The method for recovering copper according to claim 1 or 2 , wherein the pH of the mixture at 25 ° C is in the range of 8 to 11. 銅イオン、低品位炭、及び銅と錯体を形成しうる窒素原子含有化合物を少なくとも含む混合物を準備する工程と、銅を担持した前記低品位炭を前記混合物から取り出す工程と、前記混合物から取り出した前記低品位炭を熱処理する工程と、を含み、前記熱処理の温度が250℃以下である、酸化銅の製造方法。 A step of preparing a mixture containing at least a copper ion, a low-grade coal, and a nitrogen atom-containing compound capable of forming a complex with copper, a step of taking out the low-grade coal carrying copper from the mixture, and taking out of the mixture wherein the step of heat treating the low-grade coal, only including, the temperature of the heat treatment is 250 ° C. or less, the manufacturing method of copper oxide.
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