WO2021117385A1 - Method and device for recovering catalytic metal from aqueous solution including catalytic metal coprecipitated with tin - Google Patents
Method and device for recovering catalytic metal from aqueous solution including catalytic metal coprecipitated with tin Download PDFInfo
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- C22B3/06—Extraction of metal compounds from ores or concentrates by wet processes by leaching in inorganic acid solutions, e.g. with acids generated in situ; in inorganic salt solutions other than ammonium salt solutions
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Definitions
- An object of the present invention is to provide a method for recovering a catalyst metal from an aqueous solution containing a catalyst metal such as palladium coprecipitated with tin with a high recovery rate.
- a stock tank for storing an aqueous solution (washing water) in which tin and a catalyst metal are co-settled and a tin co-sink are filtered and separated.
- a recovery device including a filter tank (filter housing) provided with a filter for the purpose and a pump for feeding liquid from the stock tank to the filter tank can be used.
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Abstract
Description
本発明は、錫と共沈した触媒金属を含有する水溶液から触媒金属を回収する方法及び回収装置に関する。 The present invention relates to a method and a recovery device for recovering a catalyst metal from an aqueous solution containing a catalyst metal coprecipitated with tin.
プラスチック、ガラス等の表面に無電解めっきを行う際には、その前処理として、触媒金属を被めっき面に担持させることが必要であり、触媒金属としては、貴金属であるパラジウム(Pd)が選定されることが一般的である。また、担持させる手法として、触媒金属塩と塩化第一錫を混合した触媒液に被めっき物を浸漬し、錫(Sn)の還元力によって、被めっき面に触媒金属を析出する方法が採られている。 When electroless plating is performed on the surface of plastic, glass, etc., it is necessary to support the catalyst metal on the surface to be plated as a pretreatment, and palladium (Pd), which is a noble metal, is selected as the catalyst metal. It is common to be done. Further, as a method of supporting the metal, a method is adopted in which the object to be plated is immersed in a catalyst solution in which a catalyst metal salt and stannous chloride are mixed, and the catalyst metal is precipitated on the surface to be plated by the reducing power of tin (Sn). ing.
被めっき物を、触媒液に浸漬して触媒金属を担持させた後は、洗浄水(主に純水)に浸漬することで余剰の触媒液が洗浄される。洗浄後の洗浄水には、触媒金属の種類にもよるが、主成分として、塩化パラジウム及び塩化錫(もしくはそれらの錯体)の他、塩酸が含まれる。また、塩酸濃度については0.005mol/L以下である。 After the object to be plated is immersed in the catalyst solution to support the catalyst metal, the excess catalyst solution is washed by immersing it in cleaning water (mainly pure water). The washing water after washing contains hydrochloric acid in addition to palladium chloride and tin chloride (or a complex thereof) as main components, although it depends on the type of catalyst metal. The hydrochloric acid concentration is 0.005 mol / L or less.
ところで、使用済みの触媒液や洗浄後の洗浄水中には、高価な触媒金属(貴金属)が含まれるため、これを回収する必要がある。使用済みの触媒液については、通常、液のまま回収業者に委託して、その後、貴金属を回収するか、或いは、工場内に貴金属回収装置を設置して、貴金属を吸着させた回収物を回収業者に委託して、回収することが行われている。 By the way, since the used catalyst solution and the washing water after washing contain an expensive catalyst metal (precious metal), it is necessary to recover it. Usually, the used catalyst liquid is outsourced to a recovery company as it is, and then the precious metal is recovered, or a precious metal recovery device is installed in the factory to collect the recovered product on which the precious metal is adsorbed. It is outsourced to a contractor for collection.
ところで、洗浄水中の触媒液は100倍程度希釈することで、触媒液(pH<1)のpHが2~3に上昇して、触媒液中の錫が沈殿し、また、その沈殿物中に触媒金属も共沈する。触媒金属は高価であることから、触媒液と同様、洗浄液中の触媒金属についても回収することが求められている。 By the way, by diluting the catalyst solution in the washing water about 100 times, the pH of the catalyst solution (pH <1) rises to 2 to 3, tin in the catalyst solution precipitates, and in the precipitate. The catalyst metal also co-precipitates. Since the catalyst metal is expensive, it is required to recover the catalyst metal in the cleaning liquid as well as the catalyst liquid.
洗浄水中の触媒金属を回収する方法としては、以下の技術が知られている。例えば、特許文献1には、洗浄水中の触媒金属を含む錫沈殿を遠心分離などの手法で固液分離して、塩酸/過酸化水素水にて沈殿を溶解し回収する方法が記載されている。
特許文献2には、洗浄水中の触媒金属を含む錫沈殿を、多孔質フィルターを使用して濾過し、逆洗浄にて分離した沈殿を塩酸/過酸化水素水分解して回収する方法が記載されている。
特許文献3、4には、洗浄水に酸を添加しpHを0.8~5mol/Lに調整して錫沈殿の生成を抑制し、細孔半径1nm以下、細孔容積45~500mm3/gである活性炭に通液して回収する方法が記載されている。
The following techniques are known as a method for recovering the catalyst metal in the washing water. For example,
In Patent Documents 3 and 4, an acid is added to the washing water to adjust the pH to 0.8 to 5 mol / L to suppress the formation of tin precipitate, the pore radius is 1 nm or less, and the pore volume is 45 to 500 mm 3 /. A method of passing the liquid through activated carbon which is g and recovering the liquid is described.
本発明は、錫と共沈したパラジウムをはじめとする触媒金属を含有する水溶液から、高回収率で、触媒金属を回収する方法を提供することを課題とする。 An object of the present invention is to provide a method for recovering a catalyst metal from an aqueous solution containing a catalyst metal such as palladium coprecipitated with tin with a high recovery rate.
上記の課題を解決するため、本発明の実施形態に係る触媒金属の回収方法は、錫と共沈した触媒金属(錫共沈物)を含有する水溶液から触媒金属を回収する方法であって、該水溶液に溶出した触媒金属の濃度が8mg/L以下の時点で、該水溶液を濾過して錫共沈物を分離し、その後、分離した錫共沈物から触媒金属を回収することを特徴とする。 In order to solve the above problems, the method for recovering the catalyst metal according to the embodiment of the present invention is a method for recovering the catalyst metal from an aqueous solution containing a catalyst metal co-precipitated with tin (tin co-precipitate). When the concentration of the catalytic metal eluted in the aqueous solution is 8 mg / L or less, the aqueous solution is filtered to separate the tin co-precipitate, and then the catalytic metal is recovered from the separated tin co-precipitate. To do.
本発明によれば、従来は廃棄されていた洗浄水中のパラジウムなどの触媒金属(貴金属)を回収することが可能となる。特に、錫と共沈したパラジウムをはじめとする触媒金属を含有する水溶液から、高回収率で触媒金属を分離する方法を提供することができる、という優れた効果を有する。 According to the present invention, it is possible to recover a catalyst metal (precious metal) such as palladium in the washing water, which has been conventionally discarded. In particular, it has an excellent effect that it is possible to provide a method for separating the catalyst metal from an aqueous solution containing a catalyst metal such as palladium coprecipitated with tin with a high recovery rate.
無電解めっき工程では、触媒金属塩と塩化第一錫を混合した触媒液に、被めっき物を浸漬して、被めっき面に触媒金属を担持させることが行われている。触媒金属としては、貴金属であるAu(金)、Ag(銀)、Pt(白金)、Pd(パラジウム)、Rh(ロジウム)、Ir(イリジウム)、Ru(ルテニウム)、Os(オスミウム)、が使用され、特にPdが主に使用される。その後、触媒金属を担持させた被めっき物は純水等からなる洗浄水に浸漬し、余剰の触媒液が洗浄される。洗浄後の洗浄水中には、貴金属である触媒金属が含まれることになり、触媒金属は高価であることから洗浄水中の触媒金属を回収することが求められている。 In the electroless plating step, the object to be plated is immersed in a catalyst solution in which a catalyst metal salt and stannous chloride are mixed to support the catalyst metal on the surface to be plated. Precious metals Au (gold), Ag (silver), Pt (platinum), Pd (palladium), Rh (rhodium), Ir (iridium), Ru (lutenium), Os (osmium) are used as catalyst metals. In particular, Pd is mainly used. After that, the object to be plated on which the catalyst metal is supported is immersed in washing water made of pure water or the like, and the excess catalyst liquid is washed. The cleaning water after cleaning contains a catalyst metal which is a noble metal, and since the catalyst metal is expensive, it is required to recover the catalyst metal in the cleaning water.
ところで、洗浄水中、触媒金属は錫と共沈しているが、本発明者は、触媒液(触媒金属:Pd)を含有する洗浄水を一晩静置していたところ、洗浄水の色が淡い茶褐色から透明になっていることに気が付いた。そして、該洗浄水中のPd濃度を測定したところ、Pd濃度が著しく高くなっていることを確認した。このことから本発明者は錫と共沈したPdをはじめとする触媒金属は、時間の経過とともにイオン化して溶出するとの知見を得た。 By the way, the catalyst metal is co-precipitated with tin in the washing water, but the present inventor left the washing water containing the catalyst solution (catalyst metal: Pd) overnight, and the color of the washing water changed. I noticed that it changed from light brown to transparent. Then, when the Pd concentration in the washing water was measured, it was confirmed that the Pd concentration was remarkably high. From this, the present inventor has found that catalyst metals such as Pd coprecipitated with tin are ionized and eluted with the passage of time.
このような知見に基づき、本実施形態は錫と共沈した触媒金属(錫共沈物)を含有する水溶液において、該水溶液中に溶出した触媒金属の濃度が8mg/L以下の時点で、触媒金属を含む錫共沈物を濾過分離し、分離した該錫共沈物から触媒金属を回収することを特徴とするものである。このように錫共沈物中から触媒金属がイオン化して溶出する前に該水溶液を濾過して錫共沈物を分離することにより、触媒金属の溶出による回収ロスを低減することができる、という優れた効果を有する。 Based on these findings, the present embodiment is a catalyst in an aqueous solution containing a catalytic metal coprecipitated with tin (tin coprecipitate) when the concentration of the catalytic metal eluted in the aqueous solution is 8 mg / L or less. It is characterized in that a tin coprecipitate containing a metal is filtered and separated, and a catalytic metal is recovered from the separated tin coprecipitate. As described above, by filtering the aqueous solution to separate the tin co-precipitate before the catalyst metal is ionized and eluted from the tin co-precipitate, the recovery loss due to the elution of the catalyst metal can be reduced. Has an effect.
触媒金属の溶出(イオン化)の開始は、pH、液温等の諸要因によって変動し、例えば、約24時間後に溶出の開始が見られるものや、約16日後になってから、溶出の開始が確認できるものもあるが、ここで重要なことは、錫と触媒金属とが共沈した水溶液(洗浄水)を保管する時間(期間)と水溶液に溶出した触媒金属の濃度との関係を事前に把握に把握し、溶出した触媒金属が特定の濃度以下の時点で、該水溶液をフィルターに通過させて濾過させることである。これにより、触媒金属が水溶液中に溶け出すロスを低減することができ、回収効率を高めることができる。好ましくは、水溶液に溶出した触媒金属の濃度が8mg/L以下、さらに好ましくは、2mg/L以下の時点で濾過することである。これにより、回収効率を50%以上とすることが可能となる。 The start of elution (ionization) of the catalytic metal varies depending on various factors such as pH and liquid temperature. For example, elution starts after about 24 hours, or elution starts after about 16 days. Although there are some that can be confirmed, what is important here is the relationship between the storage time (period) of the aqueous solution (washing water) in which tin and the catalytic metal are co-precipitated and the concentration of the catalytic metal eluted in the aqueous solution in advance. When the concentration of the eluted catalytic metal is below a specific concentration, the aqueous solution is passed through a filter to be filtered. As a result, the loss of the catalyst metal dissolving in the aqueous solution can be reduced, and the recovery efficiency can be improved. It is preferable to filter when the concentration of the catalyst metal eluted in the aqueous solution is 8 mg / L or less, more preferably 2 mg / L or less. This makes it possible to increase the recovery efficiency to 50% or more.
錫共沈物は、目開き10μm以下のフィルターを用いて濾過することが好ましい。錫共沈物は粒径が細かいため、フィルターの目開きが10μmを超えると、錫共沈物がフィルターを通過して、十分に濾過ができないということがある。より好ましくは目開き1μm以下のフィルターを用いることである。また、濾過フィルターの通液速度は100L/min以下とすることが好ましい。錫共沈物は比重が小さいため、通液速度が100L/minを超えると、錫共沈物がフィルターを通過して、十分に濾過できないということがある。 The tin coprecipitate is preferably filtered using a filter with an opening of 10 μm or less. Since the tin coprecipitate has a fine particle size, if the opening of the filter exceeds 10 μm, the tin coprecipitate may pass through the filter and cannot be sufficiently filtered. More preferably, a filter having an opening of 1 μm or less is used. Further, the liquid passing speed of the filtration filter is preferably 100 L / min or less. Since the tin coprecipitate has a small specific gravity, if the liquid passing speed exceeds 100 L / min, the tin coprecipitate may pass through the filter and cannot be sufficiently filtered.
その後、濾過した錫共沈物から触媒金属を分離、回収する方法としては、例えば、分離した錫共沈物を濾過フィルターごと焼成して減容し、その後、塩酸、過酸化水素水、及び/又は王水によって、SnおよびPd(触媒金属)を溶解し、溶解したPdを鉄粉や薬品により還元して析出してきたPd金属を回収することができる。あるいは、分離した錫共沈物を、イオン交換樹脂やキレート樹脂などの該吸着材が設置された水溶液に再投入し、一定時保持することで、水溶液中に溶出していく触媒金属を随時、吸着材で回収することができる。 Then, as a method of separating and recovering the catalytic metal from the filtered tin co-precipitate, for example, the separated tin co-precipitate is calcined together with the filtration filter to reduce the volume, and then hydrochloric acid, a hydrogen peroxide solution, and /. Alternatively, Sn and Pd (catalyst metal) can be dissolved with aqua regia, and the dissolved Pd can be reduced with iron powder or a chemical to recover the precipitated Pd metal. Alternatively, the separated tin coprecipitate is re-injected into an aqueous solution in which the adsorbent such as an ion exchange resin or a chelate resin is installed and held for a certain period of time to allow the catalyst metal to be eluted into the aqueous solution at any time. It can be recovered with an adsorbent.
具体的な回収装置として、図1に示すような、錫と触媒金属とが共沈した水溶液(洗浄水)を保管するためのストック槽(洗浄水原水槽)と、錫共沈物を濾過分離するためのフィルターを備えたフィルター槽(フィルターハウジング)と、前記ストック槽から前記濾過槽に送液するためのポンプとを備えた、回収装置を用いることができる。 As a specific recovery device, as shown in FIG. 1, a stock tank (washing water raw water tank) for storing an aqueous solution (washing water) in which tin and a catalyst metal are co-settled and a tin co-sink are filtered and separated. A recovery device including a filter tank (filter housing) provided with a filter for the purpose and a pump for feeding liquid from the stock tank to the filter tank can be used.
本発明の実施例等について説明する。なお、以下の実施例は、あくまで代表的な例を示しているもので、本発明はこれらの実施例に制限される必要はなく、明細書の記載される技術思想の範囲で解釈されるべきものである。 Examples of the present invention will be described. It should be noted that the following examples are merely representative examples, and the present invention need not be limited to these examples and should be interpreted within the scope of the technical idea described in the specification. It is a thing.
(実施例1)
錫とパラジウムが共沈した水溶液(Pd:11mg/L、Sn:1350mg/L、pH:2~3)を、液温約18℃~23℃で保持し、経過時間ごとに水溶液中のPd及びSnの濃度を計測した。その結果、表1に示すように、保持期間が24時間後、徐々に水溶液中のPdの濃度が上昇した。その後、約48時間経過後では、Pdはほとんど溶出していた。回収率が50%以上であれば一応の目標を達成できることから、水溶液から錫共沈物の濾過は36時間以前に行うことが好ましいことが分かる。
(Example 1)
An aqueous solution in which tin and palladium are co-precipitated (Pd: 11 mg / L, Sn: 1350 mg / L, pH: 2 to 3) is maintained at a liquid temperature of about 18 ° C. to 23 ° C. The Sn concentration was measured. As a result, as shown in Table 1, the concentration of Pd in the aqueous solution gradually increased after the retention period was 24 hours. Then, after about 48 hours had passed, Pd was almost eluted. Since the target can be achieved if the recovery rate is 50% or more, it can be seen that it is preferable to filter the tin coprecipitate from the aqueous solution before 36 hours.
(実施例2)
錫とパラジウムが共沈した水溶液(Pd:17mg/L、Sn:580mg/L、pH:2~3)を、液温約18℃~23℃で保持し、経過時間ごとに水溶液中のPd及びSnの濃度を計測した。その結果、表1に示すように、保持期間が16日後、徐々に水溶液中のPdの濃度が上昇した。その後、約30日経過後では、Pdはほとんど溶出していた。回収率が50%以上であれば一応の目標を達成できることから、水溶液から錫共沈物の濾過は20日以前に行うことが好ましいことが分かる。
(Example 2)
An aqueous solution in which tin and palladium are co-precipitated (Pd: 17 mg / L, Sn: 580 mg / L, pH: 2 to 3) is maintained at a liquid temperature of about 18 ° C. to 23 ° C. The Sn concentration was measured. As a result, as shown in Table 1, the concentration of Pd in the aqueous solution gradually increased after the retention period was 16 days. Then, after about 30 days had passed, Pd was almost eluted. Since the target can be achieved if the recovery rate is 50% or more, it can be seen that it is preferable to filter the tin coprecipitate from the aqueous solution before 20 days.
本発明によれば、本発明によれば、従来は廃棄されていた洗浄水中のパラジウムなどの触媒金属(貴金属)を回収することが可能となる。特に、錫と共沈したパラジウムをはじめとする触媒金属を含有する水溶液から、高回収率で触媒金属を分離する方法を提供することができるという優れた効果を有する。本発明は、無電解めっき工程で排出される有価金属を含有する排水から、該有価金属を回収するリサイクル分野において有用である。 According to the present invention, according to the present invention, it is possible to recover a catalyst metal (precious metal) such as palladium in the washing water, which has been conventionally discarded. In particular, it has an excellent effect of being able to provide a method for separating the catalyst metal from an aqueous solution containing a catalyst metal such as palladium coprecipitated with tin with a high recovery rate. The present invention is useful in the field of recycling in which the valuable metal is recovered from the wastewater containing the valuable metal discharged in the electroless plating process.
1 ストック槽(洗浄水原水槽)
2 送液ポンプ(マグネットポンプ)
3 流量計
4 フィルター(フィルターエレメント)
5 フィルター槽(フィルターハウジング)
1 Stock tank (washing water raw water tank)
2 Liquid feed pump (magnet pump)
3 Flowmeter 4 Filter (filter element)
5 Filter tank (filter housing)
Claims (7)
A recovery device for carrying out the method for recovering a catalyst metal from a catalyst metal-containing aqueous solution according to any one of claims 1 to 6, for storing an aqueous solution in which tin and the catalyst metal are co-precipitated. From a catalyst metal-containing aqueous solution, which comprises a stock tank, a filter tank for filtering and separating tin co-deposits, and a pump for passing the aqueous solution from the stock tank to the filter tank. Catalytic metal recovery device.
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| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP2021563790A JP7197729B2 (en) | 2019-12-14 | 2020-11-06 | Method and apparatus for recovering catalytic metal from aqueous solution containing catalytic metal coprecipitated with tin |
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| Application Number | Priority Date | Filing Date | Title |
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| JP2019225985 | 2019-12-14 | ||
| JP2019-225985 | 2019-12-14 |
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| Publication Number | Publication Date |
|---|---|
| WO2021117385A1 true WO2021117385A1 (en) | 2021-06-17 |
Family
ID=76329749
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| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| PCT/JP2020/041441 Ceased WO2021117385A1 (en) | 2019-12-14 | 2020-11-06 | Method and device for recovering catalytic metal from aqueous solution including catalytic metal coprecipitated with tin |
Country Status (3)
| Country | Link |
|---|---|
| JP (1) | JP7197729B2 (en) |
| TW (1) | TWI796613B (en) |
| WO (1) | WO2021117385A1 (en) |
Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2001131652A (en) * | 1999-10-28 | 2001-05-15 | Kawasaki Kasei Chem Ltd | Palladium separation and recovery method |
| US20020119085A1 (en) * | 2000-12-22 | 2002-08-29 | Kinetico Incorporated | Process for recovering palladium from a solution |
| JP2002326821A (en) * | 2001-04-27 | 2002-11-12 | Kawasaki Kasei Chem Ltd | Method for separating and recovering palladium |
| JP2003247029A (en) * | 2001-11-21 | 2003-09-05 | Shipley Co Llc | Method for recovering catalytic metal using porous metal |
| JP2005013774A (en) * | 2003-06-23 | 2005-01-20 | Azumi Roshi Kk | Device for collecting solids in waste liquid |
| JP2017226896A (en) * | 2016-06-24 | 2017-12-28 | 田中貴金属工業株式会社 | Method for separating and recovering palladium and tin |
| JP2020146633A (en) * | 2019-03-14 | 2020-09-17 | 松田産業株式会社 | Method and apparatus for collecting catalyst metal from aqueous solution containing catalyst metal coprecipitated with tin |
-
2020
- 2020-11-06 JP JP2021563790A patent/JP7197729B2/en active Active
- 2020-11-06 WO PCT/JP2020/041441 patent/WO2021117385A1/en not_active Ceased
- 2020-11-12 TW TW109139494A patent/TWI796613B/en active
Patent Citations (7)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JP2001131652A (en) * | 1999-10-28 | 2001-05-15 | Kawasaki Kasei Chem Ltd | Palladium separation and recovery method |
| US20020119085A1 (en) * | 2000-12-22 | 2002-08-29 | Kinetico Incorporated | Process for recovering palladium from a solution |
| JP2002326821A (en) * | 2001-04-27 | 2002-11-12 | Kawasaki Kasei Chem Ltd | Method for separating and recovering palladium |
| JP2003247029A (en) * | 2001-11-21 | 2003-09-05 | Shipley Co Llc | Method for recovering catalytic metal using porous metal |
| JP2005013774A (en) * | 2003-06-23 | 2005-01-20 | Azumi Roshi Kk | Device for collecting solids in waste liquid |
| JP2017226896A (en) * | 2016-06-24 | 2017-12-28 | 田中貴金属工業株式会社 | Method for separating and recovering palladium and tin |
| JP2020146633A (en) * | 2019-03-14 | 2020-09-17 | 松田産業株式会社 | Method and apparatus for collecting catalyst metal from aqueous solution containing catalyst metal coprecipitated with tin |
Also Published As
| Publication number | Publication date |
|---|---|
| TWI796613B (en) | 2023-03-21 |
| TW202129017A (en) | 2021-08-01 |
| JPWO2021117385A1 (en) | 2021-06-17 |
| JP7197729B2 (en) | 2022-12-27 |
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