JPS5950025A - Method for separating and recovering gallium from waste water - Google Patents

Method for separating and recovering gallium from waste water

Info

Publication number
JPS5950025A
JPS5950025A JP15924482A JP15924482A JPS5950025A JP S5950025 A JPS5950025 A JP S5950025A JP 15924482 A JP15924482 A JP 15924482A JP 15924482 A JP15924482 A JP 15924482A JP S5950025 A JPS5950025 A JP S5950025A
Authority
JP
Japan
Prior art keywords
gallium
waste water
hydrochloric acid
wastewater
precipitate
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.)
Granted
Application number
JP15924482A
Other languages
Japanese (ja)
Other versions
JPH0465013B2 (en
Inventor
Tsugio Shimono
下野 次男
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
NEC Corp
Original Assignee
NEC Corp
Nippon Electric Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by NEC Corp, Nippon Electric Co Ltd filed Critical NEC Corp
Priority to JP15924482A priority Critical patent/JPS5950025A/en
Publication of JPS5950025A publication Critical patent/JPS5950025A/en
Publication of JPH0465013B2 publication Critical patent/JPH0465013B2/ja
Granted legal-status Critical Current

Links

Abstract

PURPOSE:To recover Ga from waste water contg. Ga in a high yield by adjusting the waste water to a specified pH, adding a soluble Al salt to the waste water to precipitate Ga and Al(OH)3 together, dissolving the precipitate in hydrochloric acid, and carrying out extraction with ethyl ether. CONSTITUTION:Waste water contg. Ga discharged from a stage in the electronic industry or the like is adjusted to 5-9pH. A soluble Al salt is added to the waste water so as to make the concn. of Al>=400mg/l, thereby precipitating Ga and Al(OH)3 together. The precipitate is separated by filtration and dissolved in hydrochloric acid to prepare 5.5-6N hydrochloric acid soln. Ethyl ether is added to the soln. to extract Ga from the soln. The ethyl ether layer contg. the extracted Ga is separated, and the Ga is recovered by removing the exhyl ether by evaporation.

Description

【発明の詳細な説明】 本発明は排水からのガリウムの分離回収法、すなわちガ
リウムを高濃度に含有する電子工業や鉱工業等の工場排
水から、有価金属であるガリウムを分離回収する方法に
関するものである。
DETAILED DESCRIPTION OF THE INVENTION The present invention relates to a method for separating and recovering gallium from wastewater, that is, a method for separating and recovering gallium, which is a valuable metal, from factory wastewater from the electronics industry, mining industry, etc., which contains high concentrations of gallium. be.

最近、ガリウムはGaA1に等の半導体材料の原料とし
て需要が増加しているが、稀少元素であるためその生産
には多大のエネルギーが消費され、高価にならざるを得
々い。従ってガリウムを高濃度に含有する工場排水から
分離回収することは省エネルギー、資源の有効利用に役
立つと同時に環境汚染防止の観点からも有意義である。
Recently, demand for gallium as a raw material for semiconductor materials such as GaA1 has been increasing, but since it is a rare element, its production consumes a large amount of energy and is inevitably expensive. Therefore, separating and recovering gallium from industrial wastewater containing high concentrations is useful for energy conservation and effective use of resources, and is also meaningful from the viewpoint of preventing environmental pollution.

ガリウムは5.5〜6N塩酸溶液からHGaCfi、の
形でエチルエーテルに定量的に抽出される。しかしガリ
ウムを分離回収するためにこの方法を直接排水に適用す
ることは種々の問題があり、従来実用に供されていなか
りた。
Gallium is quantitatively extracted in ethyl ether in the form of HGaCfi from a 5.5-6N hydrochloric acid solution. However, there are various problems in directly applying this method to wastewater to separate and recover gallium, and it has not been put to practical use so far.

本発明はこのようなガリウムの排水からの分離回収に際
して、まず排水のpHを調節して適量の可溶性アルミニ
ウム塩を添加し、ガリウムを水酸化アルきニウムと共沈
させ、との沈殿物゛にエーテル抽出法を適用することに
よシ、従来予想し得なかった回収効果を実現したもので
ある。
When separating and recovering gallium from wastewater, the present invention first adjusts the pH of the wastewater, adds an appropriate amount of soluble aluminum salt, co-precipitates gallium with aluminum hydroxide, and precipitates the gallium with aluminum hydroxide. By applying the ether extraction method, we have achieved a recovery effect that was previously unimaginable.

本発明によるとガリウムを含有する排水のpHを5以上
9以下に調節してlこの排水に可溶性アルきニウム塩を
添加してガリウムを水酸化アルミニウムと共沈させる工
程と、この沈殿物を濾過分離後塩酸で溶解して5.5〜
6.ON塩酸溶液としエチルエーテルを添加してガリウ
ムをエチルエーテル抽出する工程とを含むことt−特徴
とする排水からのガリウムの分離回収法が得られる。
According to the present invention, the pH of wastewater containing gallium is adjusted to 5 or more and 9 or less, a soluble alkium salt is added to the wastewater to coprecipitate gallium with aluminum hydroxide, and the precipitate is filtered. After separation, dissolve with hydrochloric acid to 5.5~
6. A method for separating and recovering gallium from wastewater is obtained, which is characterized in that it includes a step of preparing an ON hydrochloric acid solution, adding ethyl ether, and extracting gallium with ethyl ether.

以下本発明について説明する。アルミニウムとガリウム
の共沈条件は酸化ガリウムを溶解して調製した模擬排水
を用いて検討した。pHf、調節する九めの中和剤の種
類は限定的なものでは表<、酸性排水に対しては炭酸カ
ルシウムと水酸化カルシウム、苛性ソーダなどが使用で
きる。中和剤として炭酸カルシウムと水酸化カルシウム
を用いた場合の添加量について検討した結果を表1に示
す。
The present invention will be explained below. Co-precipitation conditions for aluminum and gallium were investigated using simulated wastewater prepared by dissolving gallium oxide. The types of neutralizing agents used to adjust the pH are limited, but for acidic wastewater, calcium carbonate, calcium hydroxide, caustic soda, etc. can be used. Table 1 shows the results of a study on the amounts added when calcium carbonate and calcium hydroxide were used as neutralizing agents.

表     1 表1では11000ppアルミニウム溶液100ゴに各
中和剤の1M溶液を添加し10分間攪拌してアルミニウ
ムを沈殿させた時のpHと沈殿濾過後のろ液のAfi濃
度を示す。表1の結果よシ中和剤の添加量は、1M炭酸
カルシウム溶液で7.5−以上、1M水酸化カルシウム
溶液で5−でよく、水酸化カルシウムの方が少量ですむ
。しかし中和剤の種類によらず共沈のためpHは5以上
9以下が必要であることを確めた。アルカリ性排水に対
して酸によりこのpH範囲に調節するととが必要である
Table 1 Table 1 shows the pH when a 1M solution of each neutralizing agent was added to 100 grams of an 11000pp aluminum solution and stirred for 10 minutes to precipitate aluminum, and the Afi concentration of the filtrate after precipitation filtration. According to the results in Table 1, the amount of the neutralizing agent added may be 7.5 or more for a 1M calcium carbonate solution and 5 or more for a 1M calcium hydroxide solution, with a smaller amount of calcium hydroxide being required. However, it was confirmed that the pH must be between 5 and 9 for coprecipitation regardless of the type of neutralizing agent. For alkaline wastewater, it is necessary to adjust the pH to this range with an acid.

次に、ガリウムを排水から効率良く共沈分離するために
必要なアルミ+=−ウム濃度について検討した結果を第
1図に示す。第1図はガリウムを50およびzootr
q/Il含む模擬排水に添加するアルミニウム濃度を変
化させてガリウムを共沈分離した時の模擬排水中のガリ
ウム濃度を示す。各濃度のガリウム溶液100−に添加
した1M炭酸カルシウム溶液の量はそれぞれ7.5−と
10−であった。また中和剤添加後の攪拌時間は10分
であった。
Next, FIG. 1 shows the results of a study on the aluminum+=-um concentration required for efficient co-precipitation separation of gallium from wastewater. Figure 1 shows gallium at 50 and zootr
The gallium concentration in the simulated wastewater when gallium is coprecipitated and separated by varying the aluminum concentration added to the simulated wastewater containing q/Il is shown. The amounts of 1M calcium carbonate solution added to each concentration of gallium solution 100- were 7.5- and 10-, respectively. The stirring time after addition of the neutralizing agent was 10 minutes.

横軸は添加アルミニウム濃度を示し、片対数グラフで示
しである。図において、実線(O−O)はガリウムの初
濃度が50η/ρで、1M炭酸カルシウム溶液の添加量
が7.5−の時のプロットでおる。
The horizontal axis indicates the concentration of added aluminum, which is shown in a semi-logarithmic graph. In the figure, the solid line (O-O) is a plot when the initial concentration of gallium is 50η/ρ and the amount of 1M calcium carbonate solution added is 7.5-.

all(・・・・・・・・)はガリウムの初濃度が20
0q/Jlで1M炭酸カルシウム溶液の添加量が10−
の時のプロットである。
all(・・・・・・・・・) has an initial concentration of gallium of 20
At 0q/Jl, the amount of 1M calcium carbonate solution added is 10-
This is the plot at the time of .

第1図より、アルミニウムを添加しなくてもある程度の
濃度までガリウムは炭酸カルシウムと共沈するが、完全
に分離するためにはアルミニウム會添加する必要があり
、アルミニウム濃度が40011v/1以上でおればほ
ぼ完全に共沈分離できる。
From Figure 1, gallium co-precipitates with calcium carbonate up to a certain concentration even without adding aluminum, but in order to completely separate it, it is necessary to add aluminum, and when the aluminum concentration exceeds 40011v/1, gallium co-precipitates with calcium carbonate. Almost complete coprecipitation separation is possible.

ガリウム濃度50■/iと200111F/1の結果を
詳細に比較するとガリウム濃度が低ければアルミニウム
濃度は低くてすむ傾向が認められる。
A detailed comparison of the results for gallium concentration 50/i and 200111F/1 reveals that the lower the gallium concentration, the lower the aluminum concentration.

以上の結果よシ排水中のガリウムをアルミニウムで共沈
分離するための条件は次のように設定された。
Based on the above results, the conditions for co-precipitation separation of gallium in wastewater with aluminum were set as follows.

アルミニウム濃度=400■/ρ以上 共沈時pH:5.0〜9.0 攪拌時間:10分 5− ガリウムの共沈分離条件が設定されたので次に沈殿物か
らのガリウムの分離について検討した。
Aluminum concentration = 400■/ρ or more pH during coprecipitation: 5.0 to 9.0 Stirring time: 10 minutes 5- Now that the conditions for co-precipitation separation of gallium were set, we next considered the separation of gallium from the precipitate. .

拳法では沈殿物を塩酸で中和溶解し、溶液の塩酸濃度を
5.5〜6NK調節した後、ガリウムをエチルエーテル
で抽出して分離した実施例を表22表3に示す。
In Kempo, the precipitate was neutralized and dissolved with hydrochloric acid, the hydrochloric acid concentration of the solution was adjusted to 5.5 to 6 NK, and then gallium was extracted and separated with ethyl ether.Table 22 and Table 3 show examples.

塩酸濃度t−5,5〜6Nと限定したのは、5.5N以
下ではガリウムの抽出率が急激に低くなること、また塩
酸濃度は高い程抽出効率は大きくなるが高価表塩酸を6
Nt−こえて加えて奄実用上のメリットはなくなるとと
Kよる。
The reason why we limited the hydrochloric acid concentration to t-5, 5 to 6N is because the extraction rate of gallium decreases rapidly below 5.5N.Also, the higher the hydrochloric acid concentration, the higher the extraction efficiency.
According to K, in addition to exceeding Nt, there is no practical advantage.

6− 表2の実施例での溶液量は200mg、表3の実施例で
のガリウム濃度はtooiv/fiであった。実施手順
は以下の通ルである。共沈分離した沈殿物を中和溶解し
て25−とし、12N塩酸を加えて全量を50−とした
。この溶液を分液ロートに移し、エチルエーテル50w
t1添加した。振とう機で10分間振とうし、10分間
放置後、エーテル層を分離した。エーテルを蒸発除去し
残渣としてガリウムを回収した。表2,3ではエーテル
蒸発残渣を純水で溶解して全量を100mgとした時の
ガリウム。
6- The solution amount in the example shown in Table 2 was 200 mg, and the gallium concentration in the example shown in Table 3 was tooiv/fi. The implementation procedure is as follows. The coprecipitated precipitate was neutralized and dissolved to make 25-, and 12N hydrochloric acid was added to make the total amount 50-. Transfer this solution to a separating funnel and add 50w of ethyl ether.
t1 was added. The mixture was shaken for 10 minutes using a shaker, and after being left for 10 minutes, the ether layer was separated. Ether was removed by evaporation and gallium was recovered as a residue. In Tables 2 and 3, gallium is obtained when the ether evaporation residue is dissolved in pure water to make the total amount 100 mg.

アルミニウムおよびカルシウムの濃度とガリウムの回収
率を示した。
The concentrations of aluminum and calcium and the recovery rate of gallium are shown.

表に示されたガリウムの回収率は92チ以上であるが、
操作の過程での損失を考慮すれば回収率は100%近く
なふと思われる。沈殿中に多量に共存するアルミニウム
およびカルシウムのエーテルによる抽出の程度は表に示
されるように非常に低くガリウムとほぼ完全に分離され
た。
The recovery rate of gallium shown in the table is over 92cm,
Considering losses during the operation, the recovery rate is thought to be close to 100%. As shown in the table, the degree of extraction of aluminum and calcium, which coexisted in large quantities in the precipitation, with ether was very low, and they were almost completely separated from gallium.

また排水中に共存することが予想される元素については
、鉄を除いて殆んどの元素がエチルエーテル抽出法によ
りガリウムと分離できることは別の実験により確認した
。鉄についても塩酸ヒドロキシルアミン、亜硫酸など適
当な還元剤を加えてFe(n)にすればエチルエーテル
抽出法によシガリウムと分離された。
In addition, it was confirmed in another experiment that most of the elements expected to coexist in wastewater, except for iron, can be separated from gallium by the ethyl ether extraction method. Iron can also be separated from cigallium by the ethyl ether extraction method by adding a suitable reducing agent such as hydroxylamine hydrochloride or sulfite to convert it into Fe(n).

本発明によシ、ガリウムを選択的に非常に高回収率で排
水から分離回収できる効果がある。
The present invention has the effect of selectively separating and recovering gallium from wastewater at a very high recovery rate.

【図面の簡単な説明】[Brief explanation of drawings]

第1図はアルミニウム濃度を変化させてガリウムを共沈
分離した時の沈殿分離後の溶液中のガリウム濃度を示す
図である。 代理人 弁理士  内 原   晋
FIG. 1 is a diagram showing the gallium concentration in the solution after precipitation separation when gallium is coprecipitated while changing the aluminum concentration. Agent Patent Attorney Susumu Uchihara

Claims (1)

【特許請求の範囲】[Claims] ガリウムを含有する排水のpHt?5以上9以下に調節
してlこの排水に可溶性アルミニウム塩を添加してtガ
リウムを水酸化7゛ルミ4ウムと共沈させる工程と、こ
の沈殿物t濾過分離後塩酸で溶解して5.5〜6.ON
塩酸溶液としエチルエーテルを添加してガリウムをエチ
ルエーテル抽出する工程とを含むことを特徴とする排水
からのガリウムの分離回収法。
pHt of wastewater containing gallium? Adding a soluble aluminum salt to this wastewater to adjust the concentration to 5 or more and 9 or less to co-precipitate gallium with 7 aluminum 4 hydroxide; and 5) dissolving the precipitate with hydrochloric acid after separating it by filtration. 5-6. ON
1. A method for separating and recovering gallium from wastewater, comprising the steps of converting it into a hydrochloric acid solution, adding ethyl ether, and extracting gallium with ethyl ether.
JP15924482A 1982-09-13 1982-09-13 Method for separating and recovering gallium from waste water Granted JPS5950025A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP15924482A JPS5950025A (en) 1982-09-13 1982-09-13 Method for separating and recovering gallium from waste water

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP15924482A JPS5950025A (en) 1982-09-13 1982-09-13 Method for separating and recovering gallium from waste water

Publications (2)

Publication Number Publication Date
JPS5950025A true JPS5950025A (en) 1984-03-22
JPH0465013B2 JPH0465013B2 (en) 1992-10-16

Family

ID=15689492

Family Applications (1)

Application Number Title Priority Date Filing Date
JP15924482A Granted JPS5950025A (en) 1982-09-13 1982-09-13 Method for separating and recovering gallium from waste water

Country Status (1)

Country Link
JP (1) JPS5950025A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2005106080A1 (en) * 2004-04-30 2005-11-10 Nippon Light Metal Company Ltd. Method of recovering gallium

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2005106080A1 (en) * 2004-04-30 2005-11-10 Nippon Light Metal Company Ltd. Method of recovering gallium

Also Published As

Publication number Publication date
JPH0465013B2 (en) 1992-10-16

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