JPS6222928B2 - - Google Patents
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- Publication number
- JPS6222928B2 JPS6222928B2 JP4545780A JP4545780A JPS6222928B2 JP S6222928 B2 JPS6222928 B2 JP S6222928B2 JP 4545780 A JP4545780 A JP 4545780A JP 4545780 A JP4545780 A JP 4545780A JP S6222928 B2 JPS6222928 B2 JP S6222928B2
- Authority
- JP
- Japan
- Prior art keywords
- resin
- heavy metals
- solution
- passed
- solution containing
- 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.)
- Expired
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Classifications
-
- Y—GENERAL 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
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
- Y02P10/00—Technologies related to metal processing
- Y02P10/20—Recycling
Landscapes
- Inorganic Compounds Of Heavy Metals (AREA)
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
- Manufacture And Refinement Of Metals (AREA)
Description
本発明は溶液中の重金属の分離回収法に関する
ものである。特に本発明は、ポリアルキレンポリ
アミン型キレート樹脂を用いて、アルカリ金属や
アルカリ土類金属と重金属とを含有する溶液か
ら、重金属を選択的に回収したり、二種以上の重
金属を含有する溶液からそれぞれの重金属を純度
よく回収したりする方法に関するものである。
近年、電子及び原子力産業等の進展に伴い、各
種金属材料の高純度化が一段と要求されている。
その一方では、こうした高純度金属は一般に高価
であるため、再利用及び回収が積極的に行なわれ
ている。
現在、こうした金属の精製及び回収で行なわれ
ている一般的な方法は、凝集沈澱法、溶媒抽出法
等であり、何れも量産に適し、処理費も比較的安
価であるという利点を有するが、高純度化及び回
収率に問題がある。
これに対し期待されているのがイオン交換樹脂
法、特にキレート形成基を有するキレート樹脂を
使用する方法である。なかでもポリアルキレンポ
リアミンをキレート形成基とするものは、種々の
重金属とのキレート安定度定数が大きく、かつ重
金属相互間のキレート安定度定数の差も大である
ため、重金属相互の分離精製に適すると共に、ポ
リアルキレンポリアミンはアルカリ金属、アルカ
リ土類金属とキレートを形成しないため、重金属
とこれらの金属との相互分離を完全に行なうこと
ができる。また、樹脂に吸着された重金属は酸ま
たはアルカリを含む溶液で脱着させることがで
き、かつこの吸着−脱着を反復することができ
る。
ポリアルキレンポリアミン型キレート樹脂は、
一般に遊離形で重金属に対して大きな吸着容量を
示すが、酸負荷形では重金属を全く吸着しない
か、ないしは吸着してもその吸着容量は小さい。
しかし、ポリアルキレンポリアミン型キレート樹
脂は、遊離形では塩基性が高いので、これに重金
属を含む溶液を接触させると、樹脂中に水酸化物
の沈澱が生ずることがある。
従つてポリアルキレンポリアミン型キレート樹
脂のカラムに重金属を含有する溶液を通液する場
合に、吸着容量を大きくするため樹脂を遊離形に
しておくと、重金属の水酸化物が生成してカラム
を閉塞させたり、生成した水酸化物の沈澱が不時
に流出してきて重金属相互間の分離を悪化させた
りする。また、樹脂の細孔内に生成した水酸化物
の沈澱は、通常の重金属の脱着に用いる量の酸等
の溶液では溶出し難いので、樹脂の反復使用が困
難になるという欠点がある。
ポリアルキレンポリアミン型キレート樹脂が遊
離形で重金属の水酸化物を生成させるのは、ポリ
アルキレンポリアミンの窒素原子の一部が、種々
の理由により、三級窒素となつていることによる
ものと考えられる。
本発明者らは、ポリアルキレンポリアミン型キ
レート樹脂について、吸着容量が大きくかつ重金
属水酸化物の沈澱が生成しない条件について検討
した結果、官能基の窒素原子の5〜90%を酸負荷
形としておくことによりこの目的を達成し得るこ
とを見出した。
本発明はこのような知見に基づいて達成された
もので、その要旨は官能基の窒素原子の5〜90%
を酸負荷形としたポリアルキレンポリアミン型キ
レート樹脂を充填した樹脂塔に、少くとも一種の
重金属を含む複数の金属を含有する溶液を通液し
て少くとも一種の重金属を樹脂に選択的に吸着さ
せる吸着工程と、重金属を吸着した樹脂塔に溶離
液を通液して吸着されている重金属を脱着させる
脱着工程とを反復することを特徴とする溶液中の
重金属の分離回収法に存する。
本発明について更に詳細に説明すると、本発明
で使用するポリアルキレンポリアミン型キレート
樹脂としては、例えばスチレンとジビルベンゼン
の架橋共重合物の如き芳香環を有する架橋共重合
体をメチルクロロメチルエーテル等でハロメチル
化した後、ポリアルキレンポリアミンを反応させ
て得られる樹脂や、アクリル酸エチルとジビニル
ベンゼンの共重合体にポリアルキレンポリアミン
を反応させて得られる樹脂、ポリアルキレンポリ
アミンをエピハロヒドリン又はアルキレンジブロ
マイドと反応させて得られる架橋結合を有する樹
脂等がある。
本発明で溶液中から分離回収される重金属とし
ては、銅、鉄、亜鉛、カドミウム、バナジウム、
モリブデン、ニツケル、コバルト、銀等があげら
れる。特に本発明は、ニツケル、コバルト、銀、
モリブデン、バナジウム等を純度よく分離回収す
るのに有利である。
本発明では、予じめ部分的に酸負荷形としたポ
リアルキレンポリアミン型キレート樹脂を充填し
た樹脂塔に、上記の重金属を含む溶液を常法によ
り通液する。樹脂の酸負荷の程度は5〜90%の範
囲から適宜選択される。一般に酸負荷の程度が大
きいほどキレート樹脂の重金属吸着容量は低下す
るので、重金属水酸化物が生成しない限度ででき
るだけ酸負荷率を小さくするのが好ましい。負荷
させる酸としては、硫酸、塩酸等の鉱酸や酢酸等
の有機酸から、通液する重金属含有溶液に応じて
適宜選択する。
本発明は重金属を含む溶液に応じて、種々の方
法で実施することができる。アルカリ金属やアル
カリ土類金属を含む溶液中に共存する重金属をこ
れらの金属から分離する場合には、一本の樹脂塔
を使用して回分方式により効率よく重金属を分離
回収することができる。しかし二種類またはそれ
以上の重金属を含む溶液からそれぞれの金属を分
離回収する場合には、2塔以上の樹脂塔を使用
し、樹脂塔間の溶液の流れを、樹脂塔からの流出
液の組成に応じて種々変更することにより、それ
ぞれの重金属を高純度で回収するのが好ましい。
例えば、第1図は、2塔の樹脂塔を用いて、2種
類の重金属を含む溶液から、それぞれの重金属を
高純度で回収する場合の装置の1例である。同図
の装置における定常状態のバルブの開閉は次の通
りである。
The present invention relates to a method for separating and recovering heavy metals in a solution. In particular, the present invention uses a polyalkylene polyamine type chelate resin to selectively recover heavy metals from solutions containing alkali metals or alkaline earth metals and heavy metals, or from solutions containing two or more types of heavy metals. It relates to a method for recovering each heavy metal with high purity. In recent years, with the progress of the electronic and nuclear industries, there has been a demand for higher purity of various metal materials.
On the other hand, since these high-purity metals are generally expensive, they are actively recycled and recovered. Currently, the common methods used to purify and recover these metals include coagulation-precipitation and solvent extraction, and both have the advantage of being suitable for mass production and having relatively low processing costs. There are problems with high purity and recovery rate. In response to this, ion exchange resin methods, particularly methods using chelate resins having chelate-forming groups, are promising. Among these, those with polyalkylene polyamine as a chelate-forming group have large chelate stability constants with various heavy metals, and the difference in chelate stability constants between heavy metals is also large, so they are suitable for separating and purifying heavy metals. In addition, since the polyalkylene polyamine does not form chelates with alkali metals and alkaline earth metals, heavy metals can be completely separated from these metals. Moreover, the heavy metals adsorbed on the resin can be desorbed with a solution containing acid or alkali, and this adsorption-desorption process can be repeated. Polyalkylene polyamine type chelate resin is
In general, it shows a large adsorption capacity for heavy metals in its free form, but in its acid-loaded form it either does not adsorb heavy metals at all, or even if it adsorbs them, its adsorption capacity is small.
However, since the polyalkylene polyamine type chelate resin is highly basic in its free form, when it is brought into contact with a solution containing a heavy metal, hydroxide may precipitate in the resin. Therefore, when passing a solution containing heavy metals through a polyalkylene polyamine type chelate resin column, if the resin is left in a free form to increase adsorption capacity, heavy metal hydroxides will be generated and the column will be clogged. Otherwise, the generated hydroxide precipitate may leak out inadvertently, worsening the separation of heavy metals from each other. In addition, the hydroxide precipitates formed in the pores of the resin are difficult to dissolve with a solution of acid or the like in an amount normally used for desorption of heavy metals, making it difficult to repeatedly use the resin. The reason why polyalkylene polyamine type chelate resins generate heavy metal hydroxides in free form is thought to be because some of the nitrogen atoms in polyalkylene polyamines become tertiary nitrogen for various reasons. . The present inventors investigated conditions for polyalkylene polyamine type chelate resins that have a large adsorption capacity and do not cause heavy metal hydroxide precipitation, and found that 5 to 90% of the nitrogen atoms in the functional groups are in the acid-loaded form. We have found that this purpose can be achieved by The present invention was achieved based on this knowledge, and its gist is that 5 to 90% of the nitrogen atoms in the functional group
A solution containing multiple metals including at least one heavy metal is passed through a resin tower filled with an acid-loaded polyalkylene polyamine chelate resin to selectively adsorb at least one heavy metal onto the resin. A method for separating and recovering heavy metals in a solution is characterized by repeating an adsorption step of adsorbing the heavy metals and a desorption step of passing an eluent through a resin tower adsorbing the heavy metals to desorb the adsorbed heavy metals. To explain the present invention in more detail, the polyalkylene polyamine type chelate resin used in the present invention includes a cross-linked copolymer having an aromatic ring, such as a cross-linked copolymer of styrene and dibylbenzene, and a cross-linked copolymer such as methyl chloromethyl ether. Resins obtained by reacting polyalkylene polyamines after halomethylation with polyalkylene polyamines, resins obtained by reacting polyalkylene polyamines with copolymers of ethyl acrylate and divinylbenzene, and polyalkylene polyamines with epihalohydrin or alkylene dibromide. There are resins having cross-linked bonds obtained by reaction. Heavy metals separated and recovered from the solution in the present invention include copper, iron, zinc, cadmium, vanadium,
Examples include molybdenum, nickel, cobalt, and silver. In particular, the present invention is applicable to nickel, cobalt, silver,
It is advantageous for separating and recovering molybdenum, vanadium, etc. with high purity. In the present invention, a solution containing the above-mentioned heavy metal is passed through a resin tower filled with a polyalkylene polyamine type chelate resin which has been partially acid-loaded in advance by a conventional method. The degree of acid loading of the resin is appropriately selected from the range of 5 to 90%. Generally, the greater the degree of acid loading, the lower the heavy metal adsorption capacity of the chelate resin, so it is preferable to reduce the acid loading rate as much as possible without producing heavy metal hydroxides. The acid to be loaded is appropriately selected from mineral acids such as sulfuric acid and hydrochloric acid, and organic acids such as acetic acid, depending on the heavy metal-containing solution to be passed. The invention can be carried out in various ways depending on the solution containing the heavy metal. When separating heavy metals coexisting in a solution containing alkali metals and alkaline earth metals from these metals, the heavy metals can be efficiently separated and recovered in a batch system using one resin tower. However, when separating and recovering each metal from a solution containing two or more types of heavy metals, two or more resin towers are used, and the flow of the solution between the resin towers is controlled by the composition of the effluent from the resin tower. It is preferable to recover each heavy metal with high purity by making various changes depending on the conditions.
For example, FIG. 1 shows an example of an apparatus in which two resin towers are used to recover each heavy metal with high purity from a solution containing two types of heavy metals. The opening and closing of the valve in the steady state in the device shown in the figure is as follows.
【表】
×:閉
○:開
各工程間の切替は、第1工程から第2工程およ
び第3工程から第4工程へは第1塔又は第2塔流
出液中の選択吸着性に富む重金属の濃度が許容限
度に達した時であり、また第2工程から第3工程
および第4工程から第1工程へは第1塔又は第2
塔流出液中の選択吸着性に富む重金属の濃度が原
溶液中の濃度に達したときである。
第1図に示した装置の作動原理を応用すれば、
3塔以上の樹脂塔からなる装置も同様に操作する
ことができる。
重金属を吸着した樹脂塔からの重金属の脱着
は、常法により行なわれる。通常は酸を含む溶液
を通液して重金属を脱着させ、次いで樹脂塔を水
洗したのち、樹脂の官能基の窒素原子の10〜95%
に相当するアルカリを含む溶液を通液して樹脂を
部分的に遊離形とする。樹脂塔は次いで液体また
は気体を吹込んで樹脂を均一に混合し、次回の重
金属の吸着に共する。このようにすれば最少限の
酸およびアルカリで本発明方法を実施することが
できる。
本発明方法によれば、重金属を含む溶液から容
易に重金属を分離回収することができる。また、
部分的に酸負荷形とした樹脂塔は、重金属を含む
溶液を通液しても膨張が少ないので、通液が容易
である。なお、本発明において、樹脂の官能基の
窒素原子含有量は、常法による塩酸吸着法で測定
する。
以下に実施例により本発明を更に詳細に説明す
るが、本発明はその要旨を超えない限り、以下の
実施例に限定されるものではない。
実施例 1
ポリエチレンポリアミン型キレート樹脂ダイヤ
イオンCR−20(ダイヤイオンは三菱化成工業株
式会社の登録商標)をアルカリ処理した遊離形樹
脂を100mlづつ6個のビーカーに採り、これに樹
脂の官能基の窒素原子の各々0、20、40、60、
80、100%相当量の1規定塩酸を加え、平衡にさ
せた後、各々内径15mmのカラムに充填して樹脂塔
を形成した。次いで各樹脂塔を50℃に保ち、これ
にCu〓2000ppm、Ca〓2000ppm、Na+2000ppm
を含む、金属塩化物溶液を空間速度(SV)2で
通液した。樹脂塔流出液のCu〓が1ppmに達した
時点で通液を停止した。各々の樹脂塔を脱塩水で
洗浄後、それぞれ200mlの1規定塩酸を通して樹
脂塔に吸着された銅を溶離した。表1に各樹脂塔
に通液した金属塩化物溶液量から計算した銅の吸
着量を示す。[Table] ×: Closed ○: Open Switching between each process is from the first step to the second step, and from the third step to the fourth step. When the concentration of
This is when the concentration of heavy metals with high selective adsorption properties in the tower effluent reaches the concentration in the original solution. Applying the operating principle of the device shown in Figure 1,
Apparatus consisting of three or more resin columns can be operated in a similar manner. Desorption of heavy metals from the resin column that has adsorbed heavy metals is carried out by a conventional method. Usually, a solution containing an acid is passed through to desorb heavy metals, and then the resin tower is washed with water, and then 10 to 95% of the nitrogen atoms in the functional groups of the resin are removed.
A solution containing an alkali equivalent to . The resin column is then blown with liquid or gas to mix the resin uniformly and to be used for the next heavy metal adsorption. In this way, the method of the present invention can be carried out using a minimum amount of acid and alkali. According to the method of the present invention, heavy metals can be easily separated and recovered from a solution containing heavy metals. Also,
A partially acid-loaded resin tower does not expand much even when a solution containing heavy metals is passed through it, so it is easy to pass the solution through it. In the present invention, the nitrogen atom content of the functional groups of the resin is measured by a conventional hydrochloric acid adsorption method. The present invention will be explained in more detail with reference to Examples below, but the present invention is not limited to the following Examples unless it exceeds the gist thereof. Example 1 100 ml of free resin obtained by alkali treatment of the polyethylene polyamine type chelate resin Diaion CR-20 (Diaion is a registered trademark of Mitsubishi Chemical Industries, Ltd.) was placed in six beakers, and the functional groups of the resin were added to the beakers. Nitrogen atoms each 0, 20, 40, 60,
After adding 1N hydrochloric acid in an amount equivalent to 80% and 100% to achieve equilibrium, each column was packed into a column with an inner diameter of 15 mm to form a resin tower. Next, each resin tower was kept at 50℃, and Cu = 2000ppm, Ca = 2000ppm, Na + 2000ppm were added to it.
A metal chloride solution containing . The flow of liquid was stopped when the Cu value of the resin column effluent reached 1 ppm. After washing each resin column with demineralized water, 200 ml of 1N hydrochloric acid was passed through each resin column to elute the copper adsorbed on the resin column. Table 1 shows the adsorption amount of copper calculated from the amount of metal chloride solution passed through each resin column.
【表】
回収した銅の純度は、各塩酸負荷率のものとも
99.8%以上で、カルシウム、ナトリウムは完全に
除去されていた。またNo.2〜No.6については、通
液量から計算した銅の吸着量と塩酸により溶離さ
れた銅の脱着量から計算した銅の回収率はほぼ
100%であつたが、No.1の塩酸負荷率0%のもの
は回収率は92%であり、塩酸による銅の溶離後も
樹脂は薄青色を呈していた。
実施例 2
実施例1と同様にして、ダイヤオンCR−20を
アルカリ処理した遊離形樹脂を100mlづつ8個の
ビーカーに採り、これに樹脂の官能基の窒素原子
の各々0、5、15、30、45、60、75、90%相当量
の1規定硫酸を加え、平衡後、各々内径15mmのカ
ラムに充填して樹脂塔を形成した。次いで各樹脂
塔にNi〓1000ppm、Mg〓1000ppm、Ca〓
500ppm、Na+1000ppm、NH4 +500ppmを含む硫
酸塩溶液を空間速度(SV)2で通液した。樹脂
塔の温度は75℃に保つた。樹脂塔流出液のNi〓
が1ppmに達した時点で通液を停止した。各々の
樹脂塔を脱塩水で洗浄後、それぞれ200mlの1規
定硫酸を通液して樹脂塔に吸着されたニツケルを
溶離した。表2に各樹脂塔にニツケルを含む被処
理液を通液した量から計算したニツケルの吸着量
を示す。[Table] The purity of the recovered copper is at each hydrochloric acid loading rate.
Calcium and sodium were completely removed at over 99.8%. Regarding No. 2 to No. 6, the copper recovery rate calculated from the adsorption amount of copper calculated from the amount of liquid passed and the amount of copper desorption eluted by hydrochloric acid is approximately
However, the recovery rate of No. 1 with a hydrochloric acid loading rate of 0% was 92%, and the resin remained pale blue even after copper was eluted with hydrochloric acid. Example 2 In the same manner as in Example 1, 100 ml of free resin obtained by treating Diaon CR-20 with alkali was placed in eight beakers, and 0, 5, 15, and 30 ml of each of the nitrogen atoms in the functional groups of the resin were added to the beakers. , 45, 60, 75, and 90% of 1N sulfuric acid were added, and after equilibration, each column was packed with an inner diameter of 15 mm to form a resin tower. Then Ni = 1000ppm, Mg = 1000ppm, Ca =
A sulfate solution containing 500 ppm, Na + 1000 ppm, and NH 4 + 500 ppm was passed at a space velocity (SV) of 2. The temperature of the resin column was maintained at 75°C. Ni in resin tower effluent
The flow of liquid was stopped when the amount reached 1 ppm. After washing each resin column with demineralized water, 200 ml of 1N sulfuric acid was passed through each column to elute the nickel adsorbed on the resin column. Table 2 shows the adsorption amount of nickel calculated from the amount of the treated liquid containing nickel passed through each resin tower.
【表】
回収したニツケルの純度はNo.1〜No.8について
何れも99.9%以上であつた。またニツケルの回収
率はNo.2〜No.8についてはほぼ100%であつた
が、No.1の硫酸負荷率0%のものは、ニツケルの
回収率は96%であつた。
実施例 3
ダイヤイオンCR−20をアルカリ処理した遊離
形樹脂を130mlづつ2個のビーカーに採り、これ
に樹脂の官能基の窒素原子の20%相当量の1規定
硫酸を加えて平衡にさせた。次いで、それぞれの
樹脂を内径20mmのカラムに充填して2本の樹脂塔
を形成し、第1図のように接続した。これにCu
〓1000ppm、Ag〓2000ppmを含む硫酸塩溶液を
空間速度(SV)4で通液した。第1工程または
第3工程から第2工程または第4工程への切替
は、第1塔または第2塔流出液中にCu〓が漏出
してきた時に行なつた。Cu〓を吸着した樹脂塔
は脱塩水で洗浄したのち、1規定硫酸250mlを通
液してCu〓を脱離させた。樹脂塔は次いで脱塩
水で洗浄したのち、1規定苛性ソーダを官能基の
窒素原子の80%相当量通液し、脱塩水で洗浄し、
更に樹脂を均一に混合したのち再び重金属の吸着
に供した。その結果、樹脂1当りの1回の銀の
回収量は47.9g、銅の回収量は24.0gであつた。
また回収された銀の純度は99.99%、銅の純度は
99.9%であり、回収率はいずれも100%であつ
た。
実施例 4
スチレンとジビニルベンゼンとの共重合体をク
ロルメチル化したのち、これにポリエチレンポリ
アミンを導入したキレート樹脂(アミン含有量
6.7meq/g−乾燥樹脂)を、アルカリ水溶液で
処理して遊離形としたのち、130mlづつ2個のビ
ーカーに採り、これに1規定硫酸を官能基の窒素
原子の10%相当量加えて平衡にした。これをそれ
ぞれ内径20mmのカラムに充填して2本の樹脂塔を
形成し、第1図のように接続した。これにNi〓
1500ppm、Co〓2000ppmを含む硫酸塩溶液を75
℃で供給し、実施例3と同様にしてニツケルとコ
バルトの分離回収を行なつた。Ni〓を吸着した
樹脂塔は1規定硫酸でNi〓を脱離させたのち、
1規定苛性ソーダを官能基の窒素原子の90%相当
量通液し、次回のNi〓の吸着に供した。
その結果、樹脂1当りの1回のコバルトの回
収量は23.6g、ニツケルの回収量は23.5gであつ
た。回収されたコバルトの純度は99.99%、ニツ
ケルの純度99.9%であり、回収率はいずれも100
%であつた。[Table] The purity of the recovered nickel was 99.9% or higher for all Nos. 1 to 8. Further, the recovery rate of nickel was almost 100% for Nos. 2 to 8, but the recovery rate of nickel for No. 1 with a sulfuric acid loading rate of 0% was 96%. Example 3 130 ml of free resin obtained by alkali treatment of Diaion CR-20 was placed in two beakers, and 1N sulfuric acid was added in an amount equivalent to 20% of the nitrogen atoms in the functional groups of the resin to achieve equilibrium. . Next, each resin was packed into a column with an inner diameter of 20 mm to form two resin towers, which were connected as shown in FIG. Cu for this
A sulfate solution containing 1000 ppm of Ag and 2000 ppm of Ag was passed through the tube at a space velocity (SV) of 4. Switching from the first step or third step to the second step or fourth step was performed when Cu〓 leaked into the effluent from the first column or the second column. After washing the resin tower that had adsorbed Cu with demineralized water, 250 ml of 1N sulfuric acid was passed therethrough to remove Cu. The resin tower was then washed with demineralized water, and then 1N caustic soda was passed through it in an amount equivalent to 80% of the nitrogen atoms in the functional group, and the resin tower was washed with demineralized water.
After further mixing the resin uniformly, the mixture was again subjected to heavy metal adsorption. As a result, the amount of silver recovered per resin was 47.9 g and the amount of copper recovered was 24.0 g.
The purity of the recovered silver is 99.99%, and the purity of the copper is 99.99%.
The recovery rate was 99.9%, and the recovery rate was 100% in all cases. Example 4 After chloromethylating a copolymer of styrene and divinylbenzene, a chelate resin (amine content
6.7 meq/g - dry resin) was treated with an alkaline aqueous solution to make it into a free form, and then 130 ml of each was placed in two beakers, and 1N sulfuric acid was added thereto in an amount equivalent to 10% of the nitrogen atoms in the functional group to achieve equilibrium. I made it. This was packed into columns each having an inner diameter of 20 mm to form two resin towers, which were connected as shown in Figure 1. Ni to this
75 sulfate solution containing 1500ppm, Co〓2000ppm
℃, and nickel and cobalt were separated and recovered in the same manner as in Example 3. After the resin tower that had adsorbed Ni was desorbed with 1N sulfuric acid,
1N caustic soda was passed through the solution in an amount equivalent to 90% of the nitrogen atoms in the functional group, and used for the next adsorption of Ni. As a result, the amount of cobalt recovered per resin was 23.6 g, and the amount of nickel recovered was 23.5 g. The purity of the recovered cobalt is 99.99%, and the purity of nickel is 99.9%, with a recovery rate of 100%.
It was %.
第1図は本発明方法を実施する装置の1例であ
る。
1〜6:バルブ、No.1:第1塔、No.2:第2
塔。
FIG. 1 shows an example of an apparatus for carrying out the method of the present invention. 1 to 6: Valve, No. 1: First tower, No. 2: Second
Tower.
Claims (1)
たポリアルキレンポリアミン型キレート樹脂を充
填した樹脂塔に、少くとも一種の重金属を含む複
数の金属を含有する溶液を通液して少くとも一種
の重金属を樹脂に選択的に吸着させる吸着工程
と、重金属を吸着した樹脂塔に溶離液を通液して
吸着されている重金属を脱着させる脱着工程とを
反復することを特徴とする溶液中の重金属の分離
回収法。 2 溶離液として酸水溶液を使用して重金属を脱
着させ、重金属脱着後の樹脂塔に官能基の窒素原
子の10〜95%に相当するアルカリ性水溶液を通液
したのち塔内の樹脂を均一に混合して、次回の重
金属の吸着に供することを特徴とする特許請求の
範囲第1項記載の溶液中の重金属の分離回収法。 3 官能基の窒素原子の5〜50%を酸負荷形とし
た樹脂を用いることを特徴とする特許請求の範囲
第1項記載の重金属の分離回収法。 4 樹脂塔に2種類以上の重金属を含む溶液を通
液して重金属の少くとも一種を選択的に樹脂に吸
着させ、同時に残余の重金属は含むが該重金属を
殆んど含まない溶液を樹脂塔から流出させること
を特徴とする特許請求の範囲第1項ないし第3項
のいずれかに記載の溶液中の重金属の分離回収
法。 5 樹脂塔にニツケルとコバルトとを含む溶液を
通液してニツケルを選択的に樹脂に吸着させ、同
時にコバルトは含むがニツケルを殆んど含まない
溶液を回収する吸着工程と、ニツケルを吸着した
樹脂塔に溶離液を通液してニツケルは含むがコバ
ルトは殆んど含まない溶液を回収する脱着工程と
を反復することを特徴とする特許請求の範囲第1
項ないし第3項のいずれかに記載の溶液中の重金
属の分離回収法。[Scope of Claims] 1. A solution containing a plurality of metals including at least one heavy metal in a resin column filled with a polyalkylene polyamine type chelate resin in which 5 to 90% of the nitrogen atoms of the functional groups are acid-loaded. Repeating an adsorption step in which a liquid is passed through the resin to selectively adsorb at least one type of heavy metal onto the resin, and a desorption step in which an eluent is passed through a resin column that has adsorbed heavy metals to desorb the adsorbed heavy metals. A method for separating and recovering heavy metals in a solution. 2 Heavy metals are desorbed using an acid aqueous solution as an eluent, and after the heavy metals have been desorbed, an alkaline aqueous solution corresponding to 10 to 95% of the nitrogen atoms in the functional group is passed through the resin column, and then the resin in the column is uniformly mixed. 2. The method for separating and recovering heavy metals in a solution according to claim 1, wherein the solution is subjected to the next adsorption of heavy metals. 3. The method for separating and recovering heavy metals according to claim 1, which uses a resin in which 5 to 50% of the nitrogen atoms in the functional groups are acid-loaded. 4 A solution containing two or more types of heavy metals is passed through the resin tower to selectively adsorb at least one of the heavy metals onto the resin, and at the same time, a solution that contains the remaining heavy metals but hardly any of the heavy metals is passed through the resin tower. A method for separating and recovering heavy metals in a solution according to any one of claims 1 to 3, characterized in that the heavy metals are discharged from a solution. 5 An adsorption step in which a solution containing nickel and cobalt is passed through a resin tower to selectively adsorb nickel onto the resin, and at the same time a solution containing cobalt but almost no nickel is recovered; Claim 1, characterized in that the desorption step of passing an eluent through a resin column and recovering a solution containing nickel but hardly containing cobalt is repeated.
A method for separating and recovering heavy metals in a solution according to any one of items 1 to 3.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP4545780A JPS56145122A (en) | 1980-04-07 | 1980-04-07 | Separation and recovery of heavy metal in solution |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| JP4545780A JPS56145122A (en) | 1980-04-07 | 1980-04-07 | Separation and recovery of heavy metal in solution |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| JPS56145122A JPS56145122A (en) | 1981-11-11 |
| JPS6222928B2 true JPS6222928B2 (en) | 1987-05-20 |
Family
ID=12719877
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| JP4545780A Granted JPS56145122A (en) | 1980-04-07 | 1980-04-07 | Separation and recovery of heavy metal in solution |
Country Status (1)
| Country | Link |
|---|---|
| JP (1) | JPS56145122A (en) |
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH01150587U (en) * | 1988-04-05 | 1989-10-18 |
-
1980
- 1980-04-07 JP JP4545780A patent/JPS56145122A/en active Granted
Cited By (1)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| JPH01150587U (en) * | 1988-04-05 | 1989-10-18 |
Also Published As
| Publication number | Publication date |
|---|---|
| JPS56145122A (en) | 1981-11-11 |
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