JPH01111825A - Method for recovering palladium from palladium-containing liquid - Google Patents
Method for recovering palladium from palladium-containing liquidInfo
- Publication number
- JPH01111825A JPH01111825A JP26735387A JP26735387A JPH01111825A JP H01111825 A JPH01111825 A JP H01111825A JP 26735387 A JP26735387 A JP 26735387A JP 26735387 A JP26735387 A JP 26735387A JP H01111825 A JPH01111825 A JP H01111825A
- Authority
- JP
- Japan
- Prior art keywords
- palladium
- liquid
- resin
- ion exchange
- adsorbed
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Pending
Links
- 239000007788 liquid Substances 0.000 title claims abstract description 51
- KDLHZDBZIXYQEI-UHFFFAOYSA-N Palladium Chemical compound [Pd] KDLHZDBZIXYQEI-UHFFFAOYSA-N 0.000 title claims description 331
- 229910052763 palladium Inorganic materials 0.000 title claims description 164
- 238000000034 method Methods 0.000 title claims description 32
- JUJWROOIHBZHMG-UHFFFAOYSA-N Pyridine Chemical compound C1=CC=NC=C1 JUJWROOIHBZHMG-UHFFFAOYSA-N 0.000 claims abstract description 22
- 239000003456 ion exchange resin Substances 0.000 claims abstract description 19
- 229920003303 ion-exchange polymer Polymers 0.000 claims abstract description 19
- NWUYHJFMYQTDRP-UHFFFAOYSA-N 1,2-bis(ethenyl)benzene;1-ethenyl-2-ethylbenzene;styrene Chemical compound C=CC1=CC=CC=C1.CCC1=CC=CC=C1C=C.C=CC1=CC=CC=C1C=C NWUYHJFMYQTDRP-UHFFFAOYSA-N 0.000 claims abstract description 18
- UMJSCPRVCHMLSP-UHFFFAOYSA-N pyridine Natural products COC1=CC=CN=C1 UMJSCPRVCHMLSP-UHFFFAOYSA-N 0.000 claims abstract description 11
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 claims abstract description 10
- XFXPMWWXUTWYJX-UHFFFAOYSA-N Cyanide Chemical compound N#[C-] XFXPMWWXUTWYJX-UHFFFAOYSA-N 0.000 claims abstract description 4
- 239000003513 alkali Substances 0.000 claims abstract description 4
- 229910021529 ammonia Inorganic materials 0.000 claims abstract description 3
- 150000003863 ammonium salts Chemical class 0.000 claims abstract description 3
- 239000003480 eluent Substances 0.000 claims description 15
- 239000011347 resin Substances 0.000 abstract description 35
- 229920005989 resin Polymers 0.000 abstract description 35
- 229910001385 heavy metal Inorganic materials 0.000 abstract description 16
- 229910052742 iron Inorganic materials 0.000 abstract description 5
- 229910052759 nickel Inorganic materials 0.000 abstract description 4
- 229910052725 zinc Inorganic materials 0.000 abstract description 4
- 229910052802 copper Inorganic materials 0.000 abstract description 3
- 229910052718 tin Inorganic materials 0.000 abstract description 3
- BFNBIHQBYMNNAN-UHFFFAOYSA-N ammonium sulfate Chemical compound N.N.OS(O)(=O)=O BFNBIHQBYMNNAN-UHFFFAOYSA-N 0.000 abstract description 2
- 229910052921 ammonium sulfate Inorganic materials 0.000 abstract description 2
- 235000011130 ammonium sulphate Nutrition 0.000 abstract description 2
- 239000013522 chelant Substances 0.000 abstract 2
- 239000010842 industrial wastewater Substances 0.000 abstract 1
- 229910052745 lead Inorganic materials 0.000 abstract 1
- MNWBNISUBARLIT-UHFFFAOYSA-N sodium cyanide Chemical compound [Na+].N#[C-] MNWBNISUBARLIT-UHFFFAOYSA-N 0.000 abstract 1
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 29
- 239000000243 solution Substances 0.000 description 23
- 238000005406 washing Methods 0.000 description 23
- XEEYBQQBJWHFJM-UHFFFAOYSA-N Iron Chemical compound [Fe] XEEYBQQBJWHFJM-UHFFFAOYSA-N 0.000 description 9
- 238000010828 elution Methods 0.000 description 9
- 238000011084 recovery Methods 0.000 description 9
- 238000001179 sorption measurement Methods 0.000 description 9
- QAOWNCQODCNURD-UHFFFAOYSA-N Sulfuric acid Chemical compound OS(O)(=O)=O QAOWNCQODCNURD-UHFFFAOYSA-N 0.000 description 8
- 239000010949 copper Substances 0.000 description 8
- 239000011701 zinc Substances 0.000 description 8
- 239000012535 impurity Substances 0.000 description 7
- VEXZGXHMUGYJMC-UHFFFAOYSA-N Hydrochloric acid Chemical compound Cl VEXZGXHMUGYJMC-UHFFFAOYSA-N 0.000 description 6
- HEMHJVSKTPXQMS-UHFFFAOYSA-M Sodium hydroxide Chemical compound [OH-].[Na+] HEMHJVSKTPXQMS-UHFFFAOYSA-M 0.000 description 6
- 229910052751 metal Inorganic materials 0.000 description 6
- 239000002184 metal Substances 0.000 description 6
- PXHVJJICTQNCMI-UHFFFAOYSA-N Nickel Chemical compound [Ni] PXHVJJICTQNCMI-UHFFFAOYSA-N 0.000 description 5
- 239000012141 concentrate Substances 0.000 description 5
- 239000000843 powder Substances 0.000 description 5
- 230000008929 regeneration Effects 0.000 description 5
- 238000011069 regeneration method Methods 0.000 description 5
- VHUUQVKOLVNVRT-UHFFFAOYSA-N Ammonium hydroxide Chemical compound [NH4+].[OH-] VHUUQVKOLVNVRT-UHFFFAOYSA-N 0.000 description 4
- 230000002378 acidificating effect Effects 0.000 description 4
- 235000011114 ammonium hydroxide Nutrition 0.000 description 4
- 230000007423 decrease Effects 0.000 description 4
- 238000004070 electrodeposition Methods 0.000 description 4
- 239000011133 lead Substances 0.000 description 4
- MUBZPKHOEPUJKR-UHFFFAOYSA-N Oxalic acid Chemical compound OC(=O)C(O)=O MUBZPKHOEPUJKR-UHFFFAOYSA-N 0.000 description 3
- KWYUFKZDYYNOTN-UHFFFAOYSA-M Potassium hydroxide Chemical compound [OH-].[K+] KWYUFKZDYYNOTN-UHFFFAOYSA-M 0.000 description 3
- RTAQQCXQSZGOHL-UHFFFAOYSA-N Titanium Chemical compound [Ti] RTAQQCXQSZGOHL-UHFFFAOYSA-N 0.000 description 3
- 238000000746 purification Methods 0.000 description 3
- 239000012279 sodium borohydride Substances 0.000 description 3
- 229910000033 sodium borohydride Inorganic materials 0.000 description 3
- 229910001220 stainless steel Inorganic materials 0.000 description 3
- 239000010935 stainless steel Substances 0.000 description 3
- 239000010936 titanium Substances 0.000 description 3
- 229910052719 titanium Inorganic materials 0.000 description 3
- OAKJQQAXSVQMHS-UHFFFAOYSA-N Hydrazine Chemical compound NN OAKJQQAXSVQMHS-UHFFFAOYSA-N 0.000 description 2
- ATJFFYVFTNAWJD-UHFFFAOYSA-N Tin Chemical compound [Sn] ATJFFYVFTNAWJD-UHFFFAOYSA-N 0.000 description 2
- HCHKCACWOHOZIP-UHFFFAOYSA-N Zinc Chemical compound [Zn] HCHKCACWOHOZIP-UHFFFAOYSA-N 0.000 description 2
- 239000002253 acid Substances 0.000 description 2
- QZPSXPBJTPJTSZ-UHFFFAOYSA-N aqua regia Chemical compound Cl.O[N+]([O-])=O QZPSXPBJTPJTSZ-UHFFFAOYSA-N 0.000 description 2
- 239000003638 chemical reducing agent Substances 0.000 description 2
- 239000003446 ligand Substances 0.000 description 2
- 150000003839 salts Chemical class 0.000 description 2
- 238000000926 separation method Methods 0.000 description 2
- 239000011135 tin Substances 0.000 description 2
- 239000002699 waste material Substances 0.000 description 2
- PAWQVTBBRAZDMG-UHFFFAOYSA-N 2-(3-bromo-2-fluorophenyl)acetic acid Chemical compound OC(=O)CC1=CC=CC(Br)=C1F PAWQVTBBRAZDMG-UHFFFAOYSA-N 0.000 description 1
- RYGMFSIKBFXOCR-UHFFFAOYSA-N Copper Chemical compound [Cu] RYGMFSIKBFXOCR-UHFFFAOYSA-N 0.000 description 1
- ZMZDMBWJUHKJPS-UHFFFAOYSA-M Thiocyanate anion Chemical compound [S-]C#N ZMZDMBWJUHKJPS-UHFFFAOYSA-M 0.000 description 1
- 239000003463 adsorbent Substances 0.000 description 1
- 229910001854 alkali hydroxide Inorganic materials 0.000 description 1
- 150000008044 alkali metal hydroxides Chemical class 0.000 description 1
- 239000012670 alkaline solution Substances 0.000 description 1
- 230000015572 biosynthetic process Effects 0.000 description 1
- KXZJHVJKXJLBKO-UHFFFAOYSA-N chembl1408157 Chemical compound N=1C2=CC=CC=C2C(C(=O)O)=CC=1C1=CC=C(O)C=C1 KXZJHVJKXJLBKO-UHFFFAOYSA-N 0.000 description 1
- 125000001309 chloro group Chemical group Cl* 0.000 description 1
- 150000001875 compounds Chemical class 0.000 description 1
- 238000011109 contamination Methods 0.000 description 1
- 238000007796 conventional method Methods 0.000 description 1
- 238000010586 diagram Methods 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- ZMZDMBWJUHKJPS-UHFFFAOYSA-N hydrogen thiocyanate Natural products SC#N ZMZDMBWJUHKJPS-UHFFFAOYSA-N 0.000 description 1
- 238000005342 ion exchange Methods 0.000 description 1
- 150000002500 ions Chemical class 0.000 description 1
- 239000012528 membrane Substances 0.000 description 1
- 150000002739 metals Chemical class 0.000 description 1
- 229910000069 nitrogen hydride Inorganic materials 0.000 description 1
- 230000001151 other effect Effects 0.000 description 1
- 235000006408 oxalic acid Nutrition 0.000 description 1
- NNFCIKHAZHQZJG-UHFFFAOYSA-N potassium cyanide Chemical compound [K+].N#[C-] NNFCIKHAZHQZJG-UHFFFAOYSA-N 0.000 description 1
- JBJWASZNUJCEKT-UHFFFAOYSA-M sodium;hydroxide;hydrate Chemical compound O.[OH-].[Na+] JBJWASZNUJCEKT-UHFFFAOYSA-M 0.000 description 1
- 238000000638 solvent extraction Methods 0.000 description 1
- DHCDFWKWKRSZHF-UHFFFAOYSA-N sulfurothioic S-acid Chemical compound OS(O)(=O)=S DHCDFWKWKRSZHF-UHFFFAOYSA-N 0.000 description 1
Landscapes
- Manufacture And Refinement Of Metals (AREA)
Abstract
Description
【発明の詳細な説明】
(産業上の利用分野)
本発明は、溶液中にイオンとして存在するパラジウムの
イオン交換樹脂への吸着と吸着したパラジウムのアルカ
リ性溶液による溶離を利用して効率よく回収するための
方法に関する。Detailed Description of the Invention (Industrial Application Field) The present invention efficiently recovers palladium present as ions in a solution by adsorbing it onto an ion exchange resin and eluating the adsorbed palladium with an alkaline solution. Regarding the method for.
(従来技術とその問題点)
パラジウムを含有する液よりパラジウムを回収する方法
として、ヒドラジン、水素化ホウ素ナトリウム、シュウ
酸、金属粉末(/l粉、Zn粉、Mg粉、Cu粉など)
などの還元剤を加えて回収する方法や電析法や不溶性錯
塩とする方法が一般的である。しかしこれらの方法では
、数ppmのパラジウムが回収されずに溶液中に残って
しまい、パラジウム含有液中のパラジウム濃度が希薄な
場合には、回収されずに溶液中に残るパラジウムの割合
が多くなり、回収率が低下するといった問題点がある。(Prior art and its problems) As a method for recovering palladium from a liquid containing palladium, hydrazine, sodium borohydride, oxalic acid, metal powder (/l powder, Zn powder, Mg powder, Cu powder, etc.) are used.
Common methods include a method of recovering by adding a reducing agent such as, an electrodeposition method, and a method of forming an insoluble complex salt. However, with these methods, several ppm of palladium remains in the solution without being recovered, and if the palladium concentration in the palladium-containing liquid is dilute, a large proportion of palladium remains in the solution without being recovered. , there is a problem that the recovery rate decreases.
また回収を目的としたパラジウム含有液には、パラジウ
ムの他に、鉄、ニッケル、銅、亜鉛、鉛、スズなどの重
金属が多量に含まれていることが多く、パラジウム回収
の際にこれらの重金属がパラジウムに混入し品位の高い
ものが得られず、その後のパラジウムの精製に手間がか
かるといった問題点がある。In addition to palladium, palladium-containing liquids often contain large amounts of heavy metals such as iron, nickel, copper, zinc, lead, and tin, and these heavy metals are removed during palladium recovery. There are problems in that the palladium is mixed with palladium, making it impossible to obtain a high-quality product, and the subsequent purification of palladium is time-consuming.
前者の問題点を解決するために、イオン交換樹脂にてパ
ラジウムを濃縮回収する方法が知られているが、パラジ
ウムを吸着した樹脂からパラジウムを回収する際に、樹
脂からパラジウムを溶離することかできずに高価な樹脂
を一旦灰化してからパラジウムを回収しなければならな
かったり、溶離することができても溶離率が低く回収率
が低下したり、樹脂を再利用することができなくなった
りする問題点がある。To solve the former problem, a method is known in which palladium is concentrated and recovered using an ion exchange resin, but when recovering palladium from a resin that has adsorbed palladium, it is not possible to elute palladium from the resin. Palladium must be recovered after first incinerating the expensive resin, or even if palladium can be eluted, the elution rate is low and the recovery rate decreases, or the resin cannot be reused. There is a problem.
また前述の不純物を多く含むパラジウム含有液を適用し
た場合には、パラジウムとこれらの重金属が同時に吸着
するので、イオン交換樹脂あたりのパラジウム吸着量が
少なくなり回収コストが増加するばかりでなく、回収し
たパラジウム中にも重金属が混入して得られるパラジウ
ムの品位が低下するなどの問題点がある。Furthermore, when a palladium-containing liquid containing many impurities mentioned above is used, palladium and these heavy metals are adsorbed at the same time, which not only reduces the amount of palladium adsorbed per ion exchange resin and increases recovery costs, but also increases the recovery cost. There are also problems such as heavy metals mixed into palladium, which lowers the quality of the resulting palladium.
(発明の目的)
本発明はこの様な問題点に鑑みてなされたもので、回収
率が高(、イオン交換樹脂の再利用が可能で、かつ高品
位のパラジウムを回収する方法を提供せんとするもので
ある。(Objective of the Invention) The present invention has been made in view of the above problems, and aims to provide a method for recovering high-quality palladium that has a high recovery rate (i.e., allows reuse of ion exchange resin). It is something to do.
(問題点を解決するための手段)
上述の如く本発明によるパラジウム含有液からのパラジ
ウム回収方法は、パラジウムを含有する液をpH9以下
に調製して、ピリジン系のキレート性イオン交換樹脂に
通液してパラジウムを吸着させ、次いで吸着したパラジ
ウムをアルカリ性溶離液で溶離してパラジウムを回収す
ることを特徴とするものである。(Means for Solving the Problems) As described above, the method for recovering palladium from a palladium-containing liquid according to the present invention involves adjusting the palladium-containing liquid to a pH of 9 or less and passing it through a pyridine-based chelating ion exchange resin. The method is characterized in that the palladium is adsorbed by the adsorbent, and then the adsorbed palladium is eluted with an alkaline eluent to recover the palladium.
(作用)
以下本発明の作用について述べる。パラジウムを含有す
る液はpH9以下に調製しておくことが望ましい。pH
9よりも高くするとイオン交換樹脂へのパラジウムの吸
着量が少なくなったり、全(吸着しなくなったりするこ
とがあるからである。(Function) The function of the present invention will be described below. It is desirable to adjust the pH of the palladium-containing solution to 9 or less. pH
This is because if the value is higher than 9, the amount of palladium adsorbed to the ion exchange resin may decrease or the amount of palladium may not be adsorbed at all.
パラジウムを含有する液としては、パラジウムを含むス
クラップを酸で溶解したものや、パラジウムを利用する
工程より排出されるパラジウムを含む廃液、パラジウム
の回収や精製する工程より排出される微量のパラジウム
を含む廃液などおおくのものがある。Palladium-containing liquids include palladium-containing scrap dissolved in acid, palladium-containing waste liquid discharged from processes that use palladium, and trace amounts of palladium discharged from palladium recovery and purification processes. There are many things such as waste liquid.
不純物として、鉄、ニッケル、鉛、亜鉛、スズなどの重
金属を多く含むパラジウム含有液が本発明に好適である
が、不純物を多く含まない液についても本発明の適用に
全く支障はない。Although palladium-containing liquids containing large amounts of heavy metals such as iron, nickel, lead, zinc, and tin as impurities are suitable for the present invention, the present invention can also be applied to liquids that do not contain many impurities.
またパラジウム含有液中のパラジウム濃度は、50g/
j!以下の範囲が良いが、これより高くなっても本発明
を適用することができ、特に重金属量が多〈従来の湿式
法の適用が難しい場合には好ましい方法と言える。The palladium concentration in the palladium-containing liquid is 50g/
j! Although the following range is preferable, the present invention can be applied even if it is higher than this, and it can be said to be a preferable method especially when the amount of heavy metals is large (it is difficult to apply the conventional wet method).
パラジウム含有液をピリジン系のキレート性イオン交換
樹脂に通液すると、パラジウムが選択的に吸着され、前
述の重金属は吸着されずにほとんどが流出してしまう。When a palladium-containing liquid is passed through a pyridine-based chelating ion exchange resin, palladium is selectively adsorbed, and most of the heavy metals mentioned above are not adsorbed and flow out.
本工程によりパラジウムと不純物の分離がおこなわれ、
後に述べる工程で品位の高いパラジウムを得ることがで
きる。This process separates palladium and impurities,
High quality palladium can be obtained through the process described later.
ピリジン系のキレート性イオン交換樹脂には多くのもの
があるが、実施例においてはスミキレ−)CR−2(商
品名)を使用した。Although there are many pyridine-based chelating ion exchange resins, Sumikire CR-2 (trade name) was used in the examples.
また吸着操作は、カラム式が好ましいがバッチ式などで
もよい。Further, the adsorption operation is preferably performed by a column method, but may also be performed by a batch method.
樹脂に吸着したパラジウムはアルカリ性の溶離液により
溶離されるが、以下樹脂に吸着したパラジウムがクロロ
錯体(塩化パラジウム酸)である場合について説明する
。The palladium adsorbed on the resin is eluted with an alkaline eluent, but a case where the palladium adsorbed on the resin is a chloro complex (chloropalladic acid) will be described below.
パラジウム含有液を樹脂に通液すると液中のパラジウム
(塩化パラジウム酸)は、ある一定の分配比をもって樹
脂の感応基と結合し吸着される。When a palladium-containing liquid is passed through a resin, the palladium (chloropalladate) in the liquid binds to and is adsorbed to the sensitive groups of the resin at a certain distribution ratio.
アルカリ性の溶離液としてアンモニア水を用いた場合に
は、樹脂に吸着しているパラジウムの配位子((1−)
は、アンモニア(NH3)と置換し、パラジウムのアン
ミン錯体となり、樹脂とパラジウムの分配比が変わると
ともに、樹脂自身の特性もpHにより変わるので、樹脂
に吸着していたパラジウムは、パラジウムのアンミン錯
体として溶離される。シアン化アルカリを含む溶離液を
用いた場合には、同様に吸着していたパラジウムはパラ
ジウムのシアノ錯体として溶離される。When aqueous ammonia is used as an alkaline eluent, the palladium ligand ((1-)
is substituted with ammonia (NH3) and becomes an ammine complex of palladium.The distribution ratio between the resin and palladium changes, and the properties of the resin itself also change depending on the pH. Therefore, the palladium adsorbed on the resin becomes an ammine complex of palladium. eluted. When an eluent containing alkali cyanide is used, similarly adsorbed palladium is eluted as a palladium cyano complex.
アルカリ性の溶離液としては、アンモニア水、アンモニ
ウム塩(硫酸アンモニウム、硝酸アンモニウムなど)、
シアン化アルカリ(シアン化ナトリウム、シアン化カリ
ウムなど)などの配位子を供給することができる化合物
を含んでいれば良く、この他にもチオシアン酸塩、チオ
硫酸塩などでも良く、これらのいずれか一種以上を含ん
でいればパラジウムを溶離することができる。Examples of alkaline eluents include aqueous ammonia, ammonium salts (ammonium sulfate, ammonium nitrate, etc.),
It is sufficient if it contains a compound capable of supplying a ligand such as alkali cyanide (sodium cyanide, potassium cyanide, etc.), and may also include thiocyanate, thiosulfate, etc., and any one of these may be used. If it contains the above, palladium can be eluted.
溶離液をアルカリ性としたのは、アルカリ性の溶離液の
方が酸性の溶離液よりも容易に樹脂からパラジウムを溶
離することができるからで、前述の配位子の供給するた
めの化合物の他に水酸化アルカリ(水酸化ナトリウム、
水酸化カリウム等)を加えても良い。The eluent was made alkaline because an alkaline eluent can elute palladium from the resin more easily than an acidic eluent. Alkali hydroxide (sodium hydroxide,
Potassium hydroxide, etc.) may be added.
またパラジウムを溶離した後の樹脂は、水洗、再生など
の工程をへて再び使用することができるので好都合であ
る。Further, the resin after palladium has been eluted can be used again after undergoing steps such as water washing and regeneration, which is advantageous.
樹脂をカラムにつめて使用する際には、吸着(通液)、
溶離、再生の操作において5V=0.5〜10、水洗な
どの操作において5V=5〜30位が良い。When using resin in a column, adsorption (liquid passage),
In operations such as elution and regeneration, 5V is preferably 0.5 to 10, and in operations such as washing with water, 5V is preferably 5 to 30.
得られたパラジウムの濃縮液には、重金属はほとんど含
まれていないので、これよりパラジウムを得ると不純物
の少ない金属パラジウムが得られ、その品位はおおむね
80%以上である。パラジウムを得る方法としては、前
述の還元剤を用いる方法や電析法や不溶性錯塩生成法な
どが一般的で良いがこの他にも多くの方法がある。また
より高品位のパラジウムを得るために本発明の工程を複
数回繰り返したり、膜分離や溶媒抽出やROやUFなど
の分離操作をへて、さらに不純物を除いたのちにパラジ
ウムを得ても良い。The obtained palladium concentrate contains almost no heavy metals, so when palladium is obtained from it, metallic palladium with few impurities is obtained, and its quality is approximately 80% or more. As a method for obtaining palladium, the above-mentioned method using a reducing agent, electrodeposition method, insoluble complex salt formation method, etc. are commonly used, but there are many other methods. Furthermore, in order to obtain higher quality palladium, the process of the present invention may be repeated multiple times, or palladium may be obtained after further removal of impurities through separation operations such as membrane separation, solvent extraction, RO or UF. .
(実施例1)
図面に示す如<Pdを含むスクラップを王水に溶かして
得られたパラジウム含有液(Pd:0.08g / 1
2. F e : 1.5g/ j!、N i :
0.1g/l。(Example 1) As shown in the drawing, a palladium-containing liquid obtained by dissolving Pd-containing scrap in aqua regia (Pd: 0.08 g/1
2. Fe: 1.5g/j! , N i :
0.1g/l.
P b :0,20g/j!SCu : 1.2 g/
j!、 p H=0.9) 200リツトルを、カラ
ムに詰めたピリジン系のキレート性イオン交換樹脂(ス
ミキレートCR−2)0.5リツトルに5V=2で通液
した。50リツトJし目、 100リツトJし目、 1
50リットル目、200リツトル目の通過液の分析をし
たところ表に示すようにパラジウムが吸着され、パラジ
ウム以外の重金属は、吸着せずに通過してしまった。Pb: 0.20g/j! SCu: 1.2 g/
j! , pH=0.9) was passed through 0.5 liter of pyridine-based chelating ion exchange resin (Sumichelate CR-2) packed in a column at 5V=2. 50 liters J, 100 liters J, 1
When the 50th liter and 200th liter of passing liquid were analyzed, palladium was adsorbed as shown in the table, and heavy metals other than palladium passed through without being adsorbed.
表 樹脂通過液の分析結果
NO=検出できず
パラジウム吸着後の樹脂は、3リツトルの純水で5V=
20で水洗したのち、2.5リツトルの5%アンモニア
水で5V=2で溶離し、さらに水洗水2.5リツトル5
V=5で洗浄し、パラジウムを含む溶離液2.5リツト
ルとパラジウムを含む水洗水2.5リツトルを得た。パ
ラジウムを含む両者の液を混合して5リツトルとし分析
をしたところPd:3.19g/f、F e : 2m
g/f、 N i : 1 mg/l。Table Analytical results of resin passing liquid: NO = not detectable, resin after palladium adsorption, 5V = 3 liters of pure water
After washing with water at 20°C, elution was carried out at 5V=2 with 2.5 liters of 5% ammonia water, and then eluted with 2.5 liters of washing water at 5V=2.
Washing was carried out at V=5 to obtain 2.5 liters of eluent containing palladium and 2.5 liters of washing water containing palladium. When both liquids containing palladium were mixed to make 5 liters and analyzed, Pd: 3.19 g/f, Fe: 2 m
g/f, Ni: 1 mg/l.
Cu:2■/l、Pb : lK/l以下であった。Cu: 2■/l, Pb: 1K/l or less.
この液を、希硫酸でpH=8に調製後、水素化ホウ素ナ
トリウムを20g添加して、パラジウムを還元し、ろ過
、洗浄の葎、乾燥させ、乾燥重量16.07 gで品位
99.2%の金属パラジウムが得られた。パラジウム含
有液を投入して金属パラジウムを回収するまでの収率は
、パラジウム純量に対して99.6%と高い収率であっ
た。After adjusting this solution to pH=8 with dilute sulfuric acid, 20 g of sodium borohydride was added to reduce the palladium, filtered, washed, and dried to obtain a product with a dry weight of 16.07 g and a grade of 99.2%. of metallic palladium was obtained. The yield from charging the palladium-containing liquid to recovering metal palladium was as high as 99.6% based on the pure amount of palladium.
(従来例1)
Pdを含むスクラップを王水に溶かして得られたパラジ
ウム含有液(p a : 0.08g/f、Fe:1.
5g /lSN i : 0.70g/ L P b
: 0.20g/l、Cu :1.2 g/l、pH=
1.3)1リツトルに10%水酸化ナトリウムを加え
てpH=8.0に調製したのち、水素化ホウ素ナトリウ
ムを5g添加して、パラジウムを還元し、ろ過、洗浄の
後、乾燥させ、乾燥重量0.75gで品位10.1%の
金属パラジウムが得られた。パラジウム含有液を投入し
て金属パラジウムを回収するまでの収率は、パラジウム
純量に対して94.7%と実施例1に比べて低く、品位
も10.1%と著しく低いものであった。(Conventional Example 1) A palladium-containing liquid obtained by dissolving Pd-containing scrap in aqua regia (pa: 0.08 g/f, Fe: 1.
5g/lSNi: 0.70g/LPb
: 0.20 g/l, Cu: 1.2 g/l, pH=
1.3) Add 10% sodium hydroxide to 1 liter to adjust the pH to 8.0, then add 5g of sodium borohydride to reduce palladium, filter, wash, and dry. Metallic palladium with a weight of 0.75 g and a grade of 10.1% was obtained. The yield from injecting the palladium-containing liquid to recovering metal palladium was 94.7% based on the pure amount of palladium, lower than in Example 1, and the quality was also significantly low at 10.1%. .
(実施例2)
図面に示す如< P d : 3.OOg/ (1,F
e : 0.82g/l、Cu : 0.95g /
l、Zn:0.30g/fを含む塩酸酸性のパラジウ
ム含有液(p)(=3)を、カラムに詰めたピリジン系
のキレート性イオン交換樹脂0.5リツトルに5V=1
で通液した。パラジウムが吸着され、パラジウム以外の
重金属は、吸着せずに通過してしまった。9.1リツト
ル通液したところで、通過液のパラジウム濃度が2■/
2となったので通液を中止し、5リツトルの純水で5V
=10で水洗した。樹脂に吸着したパラジウム量を算出
したところ、樹脂1リットル当り54.6gと非常に高
いものであった。(Example 2) As shown in the drawings < P d : 3. OOg/ (1,F
e: 0.82g/l, Cu: 0.95g/
A hydrochloric acid acidic palladium-containing solution (p) (=3) containing 0.30 g/f of Zn was added to 0.5 liter of a pyridine-based chelating ion exchange resin packed in a column at 5V=1.
The liquid was passed through. Palladium was adsorbed, and heavy metals other than palladium passed through without being adsorbed. 9. After passing 1 liter of liquid, the palladium concentration in the liquid passing through was 2■/
2, so I stopped passing the liquid and turned it to 5V with 5 liters of pure water.
= 10 and washed with water. When the amount of palladium adsorbed on the resin was calculated, it was found to be extremely high at 54.6 g per liter of resin.
水洗後の樹脂は、1.5リツトルの5%NaOH水で5
V=1で溶離し、さらに水洗水1.5リツトル5V=5
で洗浄し、パラジウムを含む溶離液1.5リツトルとパ
ラジウムを含む水洗水1.5リツトルを得た。パラジウ
ムを含む両者の液を混合してパラジウム濃縮液とした。After washing, the resin was washed with 1.5 liters of 5% NaOH water.
Elute at V=1 and add 1.5 liters of washing water 5V=5
1.5 liters of eluent containing palladium and 1.5 liters of washing water containing palladium were obtained. Both solutions containing palladium were mixed to form a palladium concentrate.
次いでパラジウム溶離後の樹脂を、5%H,3041リ
ットル5V−2で通液することにより再生し、純水2.
5リツトルを5V−5で洗浄し、上述の液を通過液のパ
ラジウム濃度が1〜10mg/42の範囲になるまで通
液した。Next, the resin after palladium elution was regenerated by passing 5% H, 3041 liters of 5V-2, and pure water 2.
5 liters was washed with 5V-5, and the above-mentioned solution was passed through the solution until the palladium concentration in the passing solution was in the range of 1 to 10 mg/42.
以上の方法で、パラジウム吸着−水洗−パラジウム溶離
−水洗一樹脂再生一水洗=(パラジウム吸着)の操作を
9回繰り返し行った。途中、パラジウム含有液の通液量
から樹脂1リットル当りのパラジウム吸着量を求めたと
ころ、52〜56gの間にありほとんど変わらなかった
。In the above method, the operation of palladium adsorption - water washing - palladium elution - water washing - resin regeneration - water washing = (palladium adsorption) was repeated nine times. During the process, the amount of palladium adsorbed per liter of resin was determined from the amount of palladium-containing liquid passed through, and it was found to be between 52 and 56 g, which was almost unchanged.
計10回の操作で、パラジウム含有液89.2リツトル
を処理し、パラジウム濃縮液(P d :8.91g/
り30リットルが得られた。In a total of 10 operations, 89.2 liters of palladium-containing liquid was treated and a palladium concentrate (P d : 8.91 g/
30 liters was obtained.
この濃縮液を、希硫酸でpH=10に調製ののち、陽極
に白金メツキしたチタン板、陰極にステンレス板を用い
て3A/dm”の電流密度で電解しパラジウムを電析さ
せた。This concentrated solution was adjusted to pH=10 with dilute sulfuric acid, and then electrolyzed at a current density of 3 A/dm'' using a platinum-plated titanium plate as the anode and a stainless steel plate as the cathode to deposit palladium.
パラジウム電析後、陰極より品位99.4%のパラジウ
ムが269.Og得られた。パラジウム含有液を投入し
て金属パラジウムを回収するまでの収率は、パラジウム
純量に対して99.92%、と高い収率であった。After palladium electrodeposition, 269.9% of palladium with a grade of 99.4% was deposited from the cathode. Og was obtained. The yield from the time when the palladium-containing liquid was introduced until the metal palladium was recovered was as high as 99.92% based on the pure amount of palladium.
(従来例2)
p t :3.00g/l、F e :0.82g/f
、Cu:0.95 g / l、Z n : 0.30
g/ I!を含む塩酸酸性のパラジウム含有液(pH=
3)を、カラムに詰めたピリジン系でない弱塩基性のイ
オン交換樹脂(ダイアイオン5AIO−A(商品名))
0.5リツトルに5V=1で通液した。パラジウムと共
にパラジウム以外の重金属も吸着され4.6リツトル通
液したところで、通過液のパラジウム濃度が2■/iと
なったので通液を中止し、5リツトルの純水で5V=1
0で水洗した。樹脂に吸着したパラジウム量を算出した
ところ、樹脂1リットル当り27.6gと実施例2に比
べ低いものであった。(Conventional example 2) p t : 3.00 g/l, Fe : 0.82 g/f
, Cu: 0.95 g/l, Zn: 0.30
g/I! An acidic palladium-containing solution containing hydrochloric acid (pH=
3) packed in a column using a non-pyridine-based weakly basic ion exchange resin (Diaion 5AIO-A (trade name))
The solution was passed through 0.5 liters at 5V=1. Heavy metals other than palladium were also adsorbed along with palladium, and when 4.6 liters of liquid was passed through, the palladium concentration in the passing liquid became 2 / i, so the flow was stopped and 5 liters of pure water was added to 5V = 1.
Washed with water at 0. When the amount of palladium adsorbed on the resin was calculated, it was found to be 27.6 g per liter of resin, which was lower than in Example 2.
水洗後の樹脂は、1.5リツトルの5%アンモニア水で
5V=1で溶離し、さらに水洗水1.5リツトル5V=
5で洗浄したところ、両者の液を混合してパラジウムの
一部とパラジウム以外の重金属が溶離した液3.0リッ
トルが得られた。The resin after washing was eluted with 1.5 liters of 5% ammonia water at 5V=1, and then eluted with 1.5 liters of washing water at 5V=1.
When the two solutions were mixed, 3.0 liters of a solution in which a portion of palladium and heavy metals other than palladium were eluted was obtained.
次いでパラジウム溶離後の樹脂を、5%Hz 3041
リツトル5V=2で通液することにより再生し、純水2
.5リツトルを5V=5で洗浄し、上述の液を通過液の
パラジウム濃度が1〜10■/2の範囲になるまで通液
した。The resin after palladium elution was then heated at 5% Hz 3041
It is regenerated by passing the liquid at 5V = 2, and pure water 2
.. 5 liters was washed at 5V=5, and the above-mentioned solution was passed through the solution until the palladium concentration in the passing solution was in the range of 1 to 10 .mu./2.
以上の方法で、パラジウム吸着→水洗−パラジウム溶離
−水洗一樹脂再生一水洗=(パラジウム吸着)の操作を
9回繰り返し行った。途中、パラジウム含有液の通液量
から樹脂1リットル当りのパラジウム吸着量を求めたと
ころ、はじめ27.6gもあったものが、10回目には
23.2gとなり約15%低下した。In the above method, the operation of palladium adsorption -> water washing - palladium elution - water washing - resin regeneration - water washing = (palladium adsorption) was repeated 9 times. During the course of the process, the amount of palladium adsorbed per liter of resin was determined from the amount of palladium-containing liquid passed through, and the amount was initially 27.6 g, but by the 10th time it was 23.2 g, a decrease of about 15%.
計lO回の操作で、パラジウム含有液41.6リツトル
を処理し、パラジウム濃縮液(P d : 4.03g
/2、F e :0.16g/1−1Cu : L3
g/l、Zn:0.30g/jり 30リツトルが得ら
れた。In a total of 10 operations, 41.6 liters of palladium-containing liquid was treated and palladium concentrated liquid (P d : 4.03 g
/2, Fe: 0.16g/1-1Cu: L3
g/l, Zn: 0.30 g/j, 30 liters was obtained.
この濃縮液を、希硫酸でpH=10に調製ののち、陽極
に白金メツキしたチタン板、陰極にステンレス板を用い
て3A/dm”の電流密度で電解しパラジウムを電析さ
せた。This concentrated solution was adjusted to pH=10 with dilute sulfuric acid, and then electrolyzed at a current density of 3 A/dm'' using a platinum-plated titanium plate as the anode and a stainless steel plate as the cathode to deposit palladium.
パラジウム電析後、陰極より品位78.5%のパラジウ
ムが純量で120.1g得られたが、CuやZn等が混
入して品位は低いものであった。パラジウム含有液を投
入して金属パラジウムを回収するまでの収率は、パラジ
ウム純量に対して96.2%と実施例2に比べ低いもの
であった。After palladium electrodeposition, 120.1 g of pure palladium with a grade of 78.5% was obtained from the cathode, but the grade was low due to the contamination of Cu, Zn, etc. The yield from charging the palladium-containing liquid to recovering metal palladium was 96.2% based on the pure amount of palladium, which was lower than in Example 2.
(実施例3)
図面に示す如< P t : 3.OOg/ l、 F
e : 0.82g/l、Cu :0.95g/j!
、 Zn :0.30g/ffiを含む塩酸酸性のパラ
ジウム含有液(p)I=3)をカラムに詰めたピリジン
系のキレート性イオン交換樹脂0.5リツトルに5V=
1で通液した。パラジウムが吸着され、パラジウム以外
の重金属は、吸着せずに通過してしまった。通過液のパ
ラジウム濃度が2■/2となったので通液を中止し、5
リツトルの純水で5V=10で水洗した。水洗後の樹脂
は、1リツトルあたりのKCN50g、、KOHlog
を含む溶離液1.5リツトルで5V=1の速さで溶離し
、さらに水洗水1.5リツトル5V=5で洗浄し、パラ
ジウムを含む溶離液1.5リツトルとパラジウムを含む
水洗水1.5リツトルを得た。パラジウムを含む両者の
液を混合してパラジウム濃縮液とした。(Example 3) As shown in the drawings <Pt: 3. OOg/l, F
e: 0.82g/l, Cu: 0.95g/j!
, 0.5 liters of a pyridine-based chelating ion exchange resin packed with a hydrochloric acid acidic palladium-containing solution (p) I = 3) containing 0.30 g/ffi of Zn in a column was charged with 5 V =
The liquid was passed through at step 1. Palladium was adsorbed, and heavy metals other than palladium passed through without being adsorbed. Since the palladium concentration of the passing liquid became 2 / 2, the liquid passage was stopped and 5
It was washed with a little pure water at 5V=10. The resin after washing with water is KCN50g per liter, KOHlog
Elute with 1.5 liters of eluent containing palladium at a rate of 5V=1, further wash with 1.5 liters of washing water at 5V=5, and elute with 1.5 liters of eluent containing palladium and 1.5 liters of washing water containing palladium. I got 5 liters. Both solutions containing palladium were mixed to form a palladium concentrate.
次いでパラジウム溶離後の樹脂を、5%1(,5Oa1
リツトル5V=2で通液することにより再生し、純水2
.5リツトルを5V−5で洗浄し、上述の液を通過液の
パラジウム濃度が1〜10mg//!の範囲になるまで
通液した。Then, the resin after palladium elution was mixed with 5% 1(,5Oa1
It is regenerated by passing the liquid at 5V = 2, and pure water 2
.. 5 liters was washed with 5V-5, and the palladium concentration in the liquid that passed through the above solution was 1 to 10 mg//! The liquid was passed until it reached the range of .
以上の方法で、パラジウム吸着−水洗−パラジウム溶離
−水洗一樹脂再生一水洗=(パラジウム吸着)の操作を
9回繰り返し行った。In the above method, the operation of palladium adsorption - water washing - palladium elution - water washing - resin regeneration - water washing = (palladium adsorption) was repeated nine times.
計10回の操作で、パラジウム濃縮液が得られた。A palladium concentrate was obtained through a total of 10 operations.
この濃縮液を、希硫酸でpH=12に調製ののち、陽掻
に白金メツキしたチタン板、陰極にステンレス板を用い
て3A/dm”の電流密度で電解しパラジウムを電析さ
せた。This concentrated solution was adjusted to pH=12 with dilute sulfuric acid, and then electrolyzed at a current density of 3 A/dm'' using a platinum-plated titanium plate as the positive electrode and a stainless steel plate as the cathode to deposit palladium.
陰極より高品位のパラジウムが得られるとともに樹脂は
何回でも使用することができた。High-quality palladium was obtained from the cathode, and the resin could be used many times.
(発明の効果)
本発明は、パラジウムを含有する液からパラジウムを回
収するに際して、ピリジン系のキレート性イオン交換樹
脂にパラジウムを選択的に吸着させ、アルカリ性溶離液
でパラジウムを溶離するとともに、イオン交換樹脂を再
利用し、一方で高品位のパラジウムを回収できるように
している。(Effect of the invention) When recovering palladium from a palladium-containing liquid, the present invention selectively adsorbs palladium to a pyridine-based chelating ion exchange resin, elutes palladium with an alkaline eluent, and ion exchanges the palladium. The resin is reused, while high-grade palladium can be recovered.
本発明では、従来のように回収したパラジウム中に不純
物が混じることが少なく、高品位のものが得られるとと
もに、パラジウムが吸着した樹脂が容易に溶離でき、か
つ何回でも使用できるものである。この他に収率が大幅
に改善され、回収、精製コストが低減するなどの別の効
果もあり、パラジウムのように希少な金属を回収するう
えで、産業への貢献が大なるものといえる。In the present invention, there are few impurities mixed in the palladium recovered as in the conventional method, high quality is obtained, the resin on which palladium is adsorbed can be easily eluted, and it can be used many times. In addition to this, there are other effects such as significantly improved yields and reduced recovery and purification costs, making it a great contribution to industry in recovering rare metals like palladium.
添付図面は本発明の実施要領を示すパラジウム回収のブ
ロックフローである。
出願人 田中貴金属工業株式会社The accompanying drawing is a block flow diagram of palladium recovery illustrating the implementation of the present invention. Applicant Tanaka Kikinzoku Kogyo Co., Ltd.
Claims (2)
、ピリジン系のキレート性イオン交換樹脂に通液してパ
ラジウムを吸着させ、その吸着したパラジウムをアルカ
リ性溶離液で溶離して、パラジウムを回収することを特
徴とするパラジウム含有液からのパラジウム回収方法。(1) Prepare a palladium-containing solution to pH 9 or less, pass it through a pyridine-based chelating ion exchange resin to adsorb palladium, and recover palladium by eluting the adsorbed palladium with an alkaline eluent. A method for recovering palladium from a palladium-containing liquid.
ンモニウム塩、シアン化アルカリのいずれか一種以上を
含むことを特徴とする特許請求の範囲第1項記載の方法
。(2) The method according to claim 1, wherein the alkaline eluent contains at least one of ammonia, an ammonium salt, and an alkali cyanide.
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP26735387A JPH01111825A (en) | 1987-10-23 | 1987-10-23 | Method for recovering palladium from palladium-containing liquid |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
JP26735387A JPH01111825A (en) | 1987-10-23 | 1987-10-23 | Method for recovering palladium from palladium-containing liquid |
Publications (1)
Publication Number | Publication Date |
---|---|
JPH01111825A true JPH01111825A (en) | 1989-04-28 |
Family
ID=17443637
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
JP26735387A Pending JPH01111825A (en) | 1987-10-23 | 1987-10-23 | Method for recovering palladium from palladium-containing liquid |
Country Status (1)
Country | Link |
---|---|
JP (1) | JPH01111825A (en) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH03158425A (en) * | 1989-11-14 | 1991-07-08 | Tanaka Kikinzoku Kogyo Kk | Method for recovering palladium |
WO2002059387A1 (en) * | 2000-12-22 | 2002-08-01 | Kinetico Incoporated | Process for recovering palladium from a solution |
US20090185965A1 (en) * | 2004-10-11 | 2009-07-23 | Laurence Delons | Method for separating zirconium and hafnium |
CN105039717A (en) * | 2015-09-10 | 2015-11-11 | 苏州联科纳米净化科技有限公司 | Method for recycling palladium from alkaline palladium activation section waste water |
-
1987
- 1987-10-23 JP JP26735387A patent/JPH01111825A/en active Pending
Cited By (5)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPH03158425A (en) * | 1989-11-14 | 1991-07-08 | Tanaka Kikinzoku Kogyo Kk | Method for recovering palladium |
WO2002059387A1 (en) * | 2000-12-22 | 2002-08-01 | Kinetico Incoporated | Process for recovering palladium from a solution |
US6482372B2 (en) * | 2000-12-22 | 2002-11-19 | Kinetico Incorporated | Process for recovering palladium from a solution |
US20090185965A1 (en) * | 2004-10-11 | 2009-07-23 | Laurence Delons | Method for separating zirconium and hafnium |
CN105039717A (en) * | 2015-09-10 | 2015-11-11 | 苏州联科纳米净化科技有限公司 | Method for recycling palladium from alkaline palladium activation section waste water |
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