Deprecated: The each() function is deprecated. This message will be suppressed on further calls in /home/zhenxiangba/zhenxiangba.com/public_html/phproxy-improved-master/index.php on line 456
JP7664873B2 - How to recover selenium - Google Patents
[go: Go Back, main page]

JP7664873B2 - How to recover selenium - Google Patents

How to recover selenium Download PDF

Info

Publication number
JP7664873B2
JP7664873B2 JP2022026097A JP2022026097A JP7664873B2 JP 7664873 B2 JP7664873 B2 JP 7664873B2 JP 2022026097 A JP2022026097 A JP 2022026097A JP 2022026097 A JP2022026097 A JP 2022026097A JP 7664873 B2 JP7664873 B2 JP 7664873B2
Authority
JP
Japan
Prior art keywords
selenium
acetone
added
acidic solution
amount
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.)
Active
Application number
JP2022026097A
Other languages
Japanese (ja)
Other versions
JP2023122414A (en
Inventor
学 真鍋
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.)
JX Nippon Mining and Metals Corp
Original Assignee
JX Nippon Mining and Metals Corp
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 JX Nippon Mining and Metals Corp filed Critical JX Nippon Mining and Metals Corp
Priority to JP2022026097A priority Critical patent/JP7664873B2/en
Publication of JP2023122414A publication Critical patent/JP2023122414A/en
Application granted granted Critical
Publication of JP7664873B2 publication Critical patent/JP7664873B2/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P10/00Technologies related to metal processing
    • Y02P10/20Recycling

Landscapes

  • Manufacture And Refinement Of Metals (AREA)

Description

本発明はセレンの回収方法に関し、特に、亜セレン酸を含む酸性液からセレンを回収する方法に関する。 The present invention relates to a method for recovering selenium, and in particular, to a method for recovering selenium from an acidic solution containing selenious acid.

銅乾式製錬では銅精鉱を熔解し、転炉、精製炉で99%以上の粗銅とした後に電解精製工程において例えば純度99.99%以上の電気銅を生産する。銅以外の有価物は電解精製時にスライムとして沈殿する。 In copper pyrometallurgy, copper concentrate is melted and processed into crude copper of 99% purity or more in a converter and a refining furnace, after which electrolytic refining produces electrolytic copper with a purity of, for example, 99.99% or more. Valuable materials other than copper are precipitated as slime during electrolytic refining.

このスライムには貴金族類、希少金属、銅精鉱に含まれているセレンやテルルも同時に濃縮される。銅製錬副産物としてこれらの元素は個別に分離・回収される。 This slime also contains concentrated precious metals, rare metals, and the selenium and tellurium contained in copper concentrate. These elements are separated and recovered individually as by-products of copper smelting.

このスライムの処理には湿式製錬法が適用される場合が多い。例えば特許文献1においてはスライムを塩酸-過酸化水素により銀を回収し、溶解した金は溶媒抽出により回収した後に、その他の有価物を二酸化硫黄で順次還元回収する方法が開示されている。特許文献2には同様の方法で金銀を回収した後、二酸化硫黄で有価物を還元して沈殿せしめ、セレンのみを蒸留して除去して貴金属類を濃縮する方法が開示されている。 This slime is often treated by hydrometallurgy. For example, Patent Document 1 discloses a method in which silver is recovered from the slime using hydrochloric acid-hydrogen peroxide, the dissolved gold is recovered by solvent extraction, and then other valuables are sequentially reduced and recovered using sulfur dioxide. Patent Document 2 discloses a method in which gold and silver are recovered using a similar method, and then the valuables are reduced and precipitated using sulfur dioxide, and only the selenium is removed by distillation to concentrate the precious metals.

貴金属を回収した後の溶液には希少金属イオン、テルル、セレンが含まれておりさらにこれら有価物を回収することが必要である。回収方法としては還元剤により生じた沈殿を回収する方法、溶液ごと銅精鉱に混合しドライヤーで乾燥させて製錬炉に繰り返す方法が知られる。 The solution left after precious metals are recovered contains rare metal ions, tellurium, and selenium, and it is necessary to further recover these valuable materials. Known recovery methods include recovering the precipitate produced by the use of a reducing agent, and mixing the solution with copper concentrate, drying it in a dryer, and then feeding it back into the smelting furnace.

とりわけ特許文献1に示されている、二酸化硫黄により生じた沈殿を回収する方法はコストや製造規模の面で利点が多い。加えて各元素が酸化還元電位の高さに従って順次沈殿することから分離精製にも効果がある。 In particular, the method of recovering precipitates produced by sulfur dioxide, as shown in Patent Document 1, has many advantages in terms of cost and production scale. In addition, it is also effective for separation and purification, as each element precipitates sequentially according to the level of its redox potential.

セレンを還元する二酸化硫黄としては、乾式製錬排ガスを使用することが一般的である。コスト面でのメリットが大きく、反応後には硫酸イオンとなり排水に悪影響を及ぼさないことが理由である。 Dry smelting exhaust gas is generally used as the sulfur dioxide used to reduce selenium. This is because it has a significant cost advantage, and after the reaction it becomes sulfate ions, which do not adversely affect wastewater.

ところが、乾式製錬排ガスを使用する場合、定期的な炉修や突発的な事故で二酸化硫黄を供給できない事態に遭遇することがある。この時、高純度の液化二酸化硫黄で代替するが試薬コストが上昇する。他にも代用品としては亜硫酸塩も可能であるが液中の酸濃度が減少する、ナトリウム濃度が上昇すると難溶性無機塩が析出する、試薬コストが上昇する等の問題がある。 However, when using dry smelting exhaust gas, there are cases where sulfur dioxide cannot be supplied due to regular furnace maintenance or sudden accidents. In such cases, high-purity liquefied sulfur dioxide can be used instead, but this increases the cost of the reagent. Another possible substitute is sulfite, but this has problems such as a decrease in the acid concentration in the liquid, the precipitation of sparingly soluble inorganic salts when the sodium concentration increases, and increased reagent costs.

安価で効率的な二酸化硫黄の代用還元剤としてはケトン類が挙げられる(特許文献3)。特にアセトンは安価で毒性も低く、単位量当たりの還元効率も高い。 Ketones are an inexpensive and efficient alternative reducing agent to sulfur dioxide (Patent Document 3). Acetone in particular is inexpensive, has low toxicity, and has a high reduction efficiency per unit amount.

特開2001-316735号公報JP 2001-316735 A 特開2004-190134号公報JP 2004-190134 A 特開2018-109207号公報JP 2018-109207 A 特開2019-77902号公報JP 2019-77902 A

ケトン類を還元剤にして亜セレン酸を還元すると大部分の亜セレン酸はセレンに還元されるが、一部は難還元性セレン化合物を生じる。本件で記す「難還元性セレン化合物」とは、二酸化硫黄により単体セレンに還元することが困難なセレン化合物を示す。セレン回収後に、さらにテルルや白金族元素といった有価物を二酸化硫黄により還元回収するため、溶液中の当該難還元性セレン化合物は排水処理工程に持ち越される。 When selenious acid is reduced using ketones as a reducing agent, most of the selenious acid is reduced to selenium, but some of it produces difficult-to-reduc selenium compounds. In this case, "difficult-to-reduc selenium compounds" refers to selenium compounds that are difficult to reduce to elemental selenium using sulfur dioxide. After selenium is recovered, valuable materials such as tellurium and platinum group elements are further reduced and recovered using sulfur dioxide, so the difficult-to-reduc selenium compounds in the solution are carried over to the wastewater treatment process.

ところが、セレンには排水中の濃度規制が定められており、少量の副反応生成物とはいえ難還元性セレン化合物は著しく排水処理工程に負荷を与える。このような問題への対応として特許文献4に示すように活性炭による吸着除去法も知られているが、効果は十分とは言えない。活性炭のみで除去すると大量の活性炭を必要とし、活性炭の試薬コストばかりでなく使用後の活性炭処理も考えなければならない。 However, there are regulations regarding the concentration of selenium in wastewater, and although it is only a small amount of a by-product, difficult-to-reduc selenium compounds place a significant burden on wastewater treatment processes. As a solution to this problem, a method of adsorption and removal using activated carbon is known, as shown in Patent Document 4, but this is not effective enough. Removal using activated carbon alone requires a large amount of activated carbon, and it is necessary to consider not only the cost of the activated carbon reagent, but also how to dispose of the activated carbon after use.

難還元性セレン化合物は、亜セレン酸のごく一部がアセトンと反応した結果生じるものであり、主反応ではない。その詳細な生成機構も判明しておらず、難還元性セレン化合物の生成を抑制しつつ亜セレン酸をセレンとして回収する方法は知られていない。 Hardly reducible selenium compounds are produced when a small portion of selenious acid reacts with acetone, and are not the main reaction. The detailed mechanism of their production is not known, and there is no known method for recovering selenious acid as selenium while suppressing the production of hard-to-reducible selenium compounds.

本発明はこのような従来の事情を鑑み、亜セレン酸を含む酸性液からケトンを還元剤としてセレンを沈殿分離させる時に、難還元性セレン化合物の生成を抑制してセレンを回収する方法を提供する。 In view of the above-mentioned conventional circumstances, the present invention provides a method for recovering selenium by suppressing the formation of difficult-to-reduc selenium compounds when precipitating and separating selenium from an acidic solution containing selenious acid using a ketone as a reducing agent.

本発明者は上記課題を解決すべく鋭意研究を重ねた結果、酸性液にアセトンを連続的または間歇的に添加しつつ、アセトンと亜セレン酸との反応で生じる有機化合物を酸化剤を用いて酸化することにより、難還元性セレン化合物の生成を抑制できることを見出した。本発明はかかる知見により完成されたものである。 As a result of intensive research conducted by the inventors to solve the above problems, they discovered that the production of difficult-to-reduc selenium compounds can be suppressed by continuously or intermittently adding acetone to an acidic solution while oxidizing the organic compounds produced by the reaction between acetone and selenious acid using an oxidizing agent. The present invention was completed based on this finding.

すなわち本発明は以下の発明を包含する。
(1)亜セレン酸を含む酸性液からセレンを還元沈殿して回収する方法であり、
前記酸性液にアセトンを連続的または間歇的に添加しつつ、前記アセトンと前記亜セレン酸との反応で生じる有機化合物を酸化剤を用いて酸化する、セレンの回収方法。
(2)前記酸性液の液温を70℃以上に加温し、前記酸性液中のセレン濃度1g/Lに対してアセトンを0.4mL/L以下の量だけ、1分以上の間隔をとりつつ間歇的に添加する、(1)に記載のセレンの回収方法。
(3)前記アセトンを0.4mL/L以下の量だけ、30分以上の間隔をとりつつ間歇的に添加する、(2)に記載のセレンの回収方法。
(4)前記酸性液へのアセトンの添加において、一回のアセトンの添加量を段階的に減少させる、(1)~(3)のいずれかに記載のセレンの回収方法。
(5)前記酸性液中の亜セレン酸の濃度がセレン濃度として25g/L以下に達した以降は、前記酸性液中のセレン濃度1g/Lに対してアセトンを0.04mL/L以下の量だけ間歇的に添加する、(4)に記載のセレンの回収方法。
(6)前記酸性液にアセトンを間歇的に添加し、且つ、前記アセトンの毎回の添加後に前記酸化剤を添加する、(1)~(5)のいずれかに記載のセレンの回収方法。
(7)前記セレンを還元沈殿した後の前記酸性液に対し、二酸化硫黄を吹き込んで過剰な酸化剤を分解し、残存セレンを沈殿回収する、(1)~(6)のいずれかに記載のセレンの回収方法。
(8)前記酸化剤は、ケトカルボン酸を酸化させる酸化剤である、(1)~(7)のいずれかに記載のセレンの回収方法。
(9)前記ケトカルボン酸を酸化させる酸化剤は、過酸化水素、酸素、次亜塩素酸及びオゾンのいずれか一種以上である、(8)に記載のセレンの回収方法。
(10)前記過酸化水素の前記酸性液への添加量は、一回のアセトンの添加量の0.03体積倍以上である、(9)に記載のセレンの回収方法。
That is, the present invention includes the following inventions.
(1) A method for recovering selenium from an acidic solution containing selenious acid by reduction and precipitation,
A method for recovering selenium, comprising the steps of: continuously or intermittently adding acetone to the acidic solution; and oxidizing an organic compound produced by a reaction between the acetone and the selenious acid with an oxidizing agent.
(2) The method for recovering selenium described in (1), wherein the temperature of the acidic solution is raised to 70° C. or higher, and acetone is intermittently added at intervals of 1 minute or more in an amount of 0.4 mL/L or less per 1 g/L of selenium concentration in the acidic solution.
(3) The method for recovering selenium according to (2), wherein the acetone is added intermittently in an amount of 0.4 mL/L or less at intervals of 30 minutes or more.
(4) The method for recovering selenium according to any one of (1) to (3), wherein the amount of acetone added at one time is gradually decreased in the addition of acetone to the acidic solution.
(5) The method for recovering selenium described in (4), wherein after the concentration of selenious acid in the acidic solution reaches 25 g/L or less in terms of selenium concentration, acetone is intermittently added in an amount of 0.04 mL/L or less per 1 g/L of selenium concentration in the acidic solution.
(6) The method for recovering selenium according to any one of (1) to (5), wherein acetone is intermittently added to the acidic liquid, and the oxidizing agent is added after each addition of the acetone.
(7) The method for recovering selenium according to any one of (1) to (6), further comprising blowing sulfur dioxide into the acidic liquid after the selenium has been reduced and precipitated to decompose excess oxidizing agent and recover remaining selenium by precipitation.
(8) The method for recovering selenium according to any one of (1) to (7), wherein the oxidizing agent is an oxidizing agent that oxidizes a ketocarboxylic acid.
(9) The method for recovering selenium according to (8), wherein the oxidizing agent for oxidizing the ketocarboxylic acid is at least one of hydrogen peroxide, oxygen, hypochlorous acid, and ozone.
(10) The method for recovering selenium according to (9), wherein the amount of hydrogen peroxide added to the acidic liquid is 0.03 volume times or more the amount of acetone added at one time.

本発明によれば、亜セレン酸を含む酸性液からケトンを還元剤としてセレンを沈殿分離させる時に、難還元性セレン化合物の生成を抑制してセレンを回収する方法を提供することができる。 The present invention provides a method for recovering selenium while suppressing the formation of difficult-to-reduc selenium compounds when precipitating and separating selenium from an acidic solution containing selenious acid using a ketone as a reducing agent.

次に本発明を実施するための形態を詳細に説明する。本発明は以下の実施形態に限定されるものではなく、本発明の趣旨を逸脱しない範囲で、当業者の通常の知識に基づいて、適宜設計の変更、改良等が加えられることが理解されるべきである。 Next, a detailed description of the embodiment of the present invention will be given. The present invention is not limited to the following embodiment, and it should be understood that appropriate design changes, improvements, etc. may be made based on the ordinary knowledge of a person skilled in the art without departing from the spirit of the present invention.

非鉄金属製錬、とりわけ銅製錬の電解精製工程で生じる電解スライムはカルコゲン元素と貴金属を多く含む。一例を示すと金を10~30kg/ton、銀を100~250kg/ton、パラジウムを1~3kg/ton、白金を200~500g/ton、セレンを5~15質量%程度含有する。 Electrolytic slime, which is produced during the electrolytic refining process of non-ferrous metal smelting, especially copper smelting, contains a lot of chalcogen elements and precious metals. For example, it contains about 10-30 kg/ton of gold, 100-250 kg/ton of silver, 1-3 kg/ton of palladium, 200-500 g/ton of platinum, and 5-15 mass% of selenium.

塩酸と過酸化水素を添加してこの電解スライムを溶解することで、銅電解殿物の溶解液が生成されるが、銀は溶解直後に塩化物イオンと不溶性の塩化銀沈殿を形成する。酸化剤と塩素を含む溶液、例えば王水や塩素水であれば貴金属類は溶解して銀を塩化銀として分離できる。塩化物浴であるため浸出貴液(PLS)には貴金属元素、希少金属元素、セレン、テルルが分配される。セレンは、当該酸性液中にセレンオキソニウムとして含まれるが大部分は亜セレン酸である。 By adding hydrochloric acid and hydrogen peroxide to dissolve this electrolytic slime, a solution of copper electrolytic deposits is produced, in which silver forms an insoluble silver chloride precipitate with chloride ions immediately after dissolution. In a solution containing an oxidizing agent and chlorine, such as aqua regia or chlorine water, the precious metals dissolve and the silver can be separated as silver chloride. Because it is a chloride bath, precious metal elements, rare metal elements, selenium, and tellurium are distributed in the pregnant leach solution (PLS). Selenium is contained in the acidic solution as selenium oxonium, but most of it is in the form of selenite.

貴金属類は溶媒抽出や酸化還元電位差を利用して回収する。その後セレンを還元回収するが、このとき、二酸化硫黄を使用して回収する方法が一般的である。このセレン回収工程で二酸化硫黄が利用できない時はアセトンにより亜セレン酸をセレンに還元することができる。 Precious metals are recovered using solvent extraction or redox potential difference. Selenium is then recovered by reduction, and the most common method is to use sulfur dioxide for this. If sulfur dioxide is not available in the selenium recovery process, selenite can be reduced to selenium using acetone.

亜セレン酸又は二酸化セレンはアリール位の炭素-水素結合に対してセレン酸化と呼ばれる反応を起こすことが知られる。アセトンは反応するが、2-プロパノールは反応しないことから、アセトンの場合はケト-エノール互変異性により生じるエノールが反応すると考えられる。アセトンに限定されず、アリール位の炭素-水素結合をもつケトン類はすべて同様の反応を生じ、亜セレン酸をセレンに還元する。 It is known that selenious acid or selenium dioxide undergoes a reaction called selenization with carbon-hydrogen bonds at aryl positions. Since acetone reacts but 2-propanol does not, it is believed that in the case of acetone, the enol produced by keto-enol tautomerization reacts. This is not limited to acetone, but all ketones with carbon-hydrogen bonds at aryl positions undergo a similar reaction, reducing selenious acid to selenium.

セレン酸化反応を受けたアセトンはヒドロキシアセトンとなり、亜セレン酸は還元を受けて単体セレンとして沈殿する。沈殿した単体セレンは温度により赤色セレン、又は黒色セレンとなる。一方で、アセトンに代表されるケトン類はアセチルアルデヒド、ケトカルボン酸となるまで反応は進行し、これらの反応後の化合物はさらに還元反応を起こす余地を残す。 After the selenium oxidation reaction, acetone becomes hydroxyacetone, and selenious acid is reduced and precipitates as elemental selenium. The precipitated elemental selenium becomes red or black selenium depending on the temperature. On the other hand, the reaction of ketones such as acetone proceeds until they become acetylaldehyde and ketocarboxylic acids, and these compounds after the reaction have room to undergo further reduction reactions.

おそらくはこのアセチルアルデヒドやケトカルボン酸(アセトンを使用した時はピルビン酸)が還元剤としてさらに作用するためにアセトンの単位量当たりの亜セレン酸還元効率は良いと考えられる。 It is likely that the efficiency of selenite reduction per unit amount of acetone is good because the acetylaldehyde and ketocarboxylic acid (pyruvic acid when acetone is used) also act as reducing agents.

他方で、ピルビン酸を、亜セレン酸を含む酸性液に添加してアセトンで還元すると、亜セレン酸は二酸化硫黄により単体セレンまで還元を受けなくなる。すなわち、難還元性セレン化合物を生じる。当然、一部ピルビン酸も亜セレン酸を還元するが、アセトンと亜セレン酸、ピルビン酸の三者が反応すると、難還元性セレン化合物が生じやすい。これに対し、中間生成物であるケトカルボン酸の生成と同時にこれを酸化分解すれば難還元性セレン化合物の生成抑制につながる。 On the other hand, when pyruvic acid is added to an acidic solution containing selenious acid and reduced with acetone, the selenious acid is no longer reduced to elemental selenium by sulfur dioxide. In other words, difficult-to-reduc selenium compounds are produced. Naturally, some pyruvic acid also reduces selenious acid, but when acetone, selenious acid, and pyruvic acid react, difficult-to-reduc selenium compounds are likely to be produced. In response to this, the intermediate product ketocarboxylic acid can be produced and simultaneously oxidized and decomposed, which leads to the suppression of the production of difficult-to-reduc selenium compounds.

本発明の実施形態では、亜セレン酸を含む酸性液にアセトンを連続的または間歇的に添加しつつ、アセトンと亜セレン酸との反応で生じるピルビン酸等の難還元性セレン化合物の生成を促す有機化合物を、酸化剤を用いて酸化することで、セレンを還元沈殿して回収する。このような構成によれば、亜セレン酸を含む酸性液にアセトンを添加することで生じるピルビン酸等の難還元性セレン化合物の生成を促す有機化合物を、酸化剤の添加によって酸化することで分解することができる。このため、難還元性セレン化合物の生成を抑制することができる。なお、酸化剤の添加によるアセトンへの影響については、もともとケトン類が酸化反応に対して活性が低いため、添加する酸化剤がアセトンによる亜セレン酸の還元に与える影響は小さい。 In an embodiment of the present invention, acetone is continuously or intermittently added to an acidic solution containing selenious acid, and an organic compound that promotes the production of difficult-to-reduc selenium compounds such as pyruvic acid produced by the reaction of acetone with selenious acid is oxidized using an oxidizing agent, thereby reducing and precipitating and recovering selenium. According to this configuration, the organic compound that promotes the production of difficult-to-reduc selenium compounds such as pyruvic acid produced by adding acetone to an acidic solution containing selenious acid can be decomposed by oxidation using an oxidizing agent. Therefore, the production of difficult-to-reduc selenium compounds can be suppressed. Regarding the effect of the addition of an oxidizing agent on acetone, since ketones are originally less active in oxidation reactions, the effect of the added oxidizing agent on the reduction of selenious acid by acetone is small.

酸化剤は過量添加すると沈殿したセレンを再度溶解することがある。そのため、酸化剤としてはケトカルボン酸を酸化させる酸化剤であるのが好ましく、例えば、過酸化水素、酸素、次亜塩素酸及びオゾンのいずれか一種以上が挙げられる。中でも反応性、非毒性、取り扱いやすさから過酸化水素が最も好適である。 If an excessive amount of oxidizing agent is added, it may re-dissolve the precipitated selenium. Therefore, the oxidizing agent is preferably an oxidizing agent that oxidizes ketocarboxylic acids, such as one or more of hydrogen peroxide, oxygen, hypochlorous acid, and ozone. Among these, hydrogen peroxide is the most suitable due to its reactivity, non-toxicity, and ease of handling.

酸性液の液温は70℃以上に加温することが好ましい。このような構成によれば、セレンを黒色セレンとして回収しやすくなる。酸性液の液温は75℃以上に加温することがより好ましい。また、加熱効率の観点から、酸性液の液温は100℃以下としてもよい。 It is preferable to heat the acidic liquid to a temperature of 70°C or higher. This configuration makes it easier to recover selenium as black selenium. It is more preferable to heat the acidic liquid to a temperature of 75°C or higher. From the viewpoint of heating efficiency, the temperature of the acidic liquid may be 100°C or lower.

酸性液の液温を70℃以上に加温し、酸性液中のセレン濃度1g/Lに対してアセトンを0.4mL/L以下の量だけ、1分以上の間隔をとりつつ間歇的に添加することが好ましい。このような構成によれば、アセトンを一度に大量に添加せずに、少量ずつ間歇的に添加することができるため、酸性液中のケトカルボン酸濃度をより良好に抑えることができる。従って、難還元性セレン化合物の生成を良好に抑制することができる。アセトンの添加量を抑えることで、アセトンの添加間隔は短くすることができる。また、アセトンの添加量が多いと、アセトンの添加間隔は長くすることが好ましい。アセトンの添加間隔が長いほど、アセトンが十分に還元剤として反応する時間を設けることができる。このため、アセトンの添加量によって、当該アセトンの添加間隔は、5分以上、10分以上、さらには30分以上としてもよい。 It is preferable to heat the acidic solution to 70°C or higher, and add acetone at intervals of 1 minute or more in an amount of 0.4 mL/L or less per 1 g/L selenium concentration in the acidic solution. With this configuration, acetone can be added intermittently in small amounts rather than at once, so that the concentration of ketocarboxylic acid in the acidic solution can be better suppressed. Therefore, the generation of difficult-to-reduc selenium compounds can be well suppressed. By suppressing the amount of acetone added, the interval between acetone additions can be shortened. Furthermore, if the amount of acetone added is large, it is preferable to make the interval between acetone additions longer. The longer the interval between acetone additions, the more time can be provided for acetone to react as a reducing agent. Therefore, depending on the amount of acetone added, the interval between acetone additions may be 5 minutes or more, 10 minutes or more, or even 30 minutes or more.

また、毎回のアセトンの添加後に、上記の酸化剤を添加するのが好ましい。このように、毎回のアセトンの添加後に酸化剤を添加することで、難還元性セレン化合物の生成をより良好に抑制することができる。 It is also preferable to add the above-mentioned oxidizing agent after each addition of acetone. In this way, by adding the oxidizing agent after each addition of acetone, the production of difficult-to-reduc selenium compounds can be more effectively suppressed.

酸性液へのアセトンの添加において、一回のアセトンの添加量を段階的に減少させることが好ましい。酸性液において、アセトンと亜セレン酸は最初に反応して有機セレン中間物が生じる。この中間物は転位後にアルデヒドもしくはピルビン酸となる。このうち、ピルビン酸は難還元性セレン化合物の生成原因と考えられる。ピルビン酸自身は熱分解や亜セレン酸に酸化されるが反応速度が速くない。この性質を利用し、酸性液へのアセトンの添加を段階的に減少させることで、亜セレン酸が少なくなる反応後期に添加量を下げることができ、反応系内のピルビン酸が過多にならないよう調節する。このようにして、酸性液中のケトカルボン酸濃度を更に良好に抑えることができる。また、このような観点から、酸性液中の亜セレン酸の濃度がセレン濃度として25g/L以下に達した以降は、酸性液中のセレン濃度1g/Lに対してアセトンを0.04mL/L以下の量だけ間歇的に添加することが好ましい。 In the addition of acetone to the acidic solution, it is preferable to gradually reduce the amount of acetone added at one time. In the acidic solution, acetone and selenious acid react first to produce an organic selenium intermediate. This intermediate becomes an aldehyde or pyruvic acid after rearrangement. Of these, pyruvic acid is considered to be the cause of the production of difficult-to-reduc selenium compounds. Pyruvic acid itself is thermally decomposed or oxidized to selenious acid, but the reaction rate is not fast. By utilizing this property and gradually reducing the addition of acetone to the acidic solution, the amount of addition can be reduced in the later stage of the reaction when selenious acid is reduced, and the pyruvic acid in the reaction system is adjusted so that it does not become excessive. In this way, the concentration of ketocarboxylic acid in the acidic solution can be further suppressed. From this perspective, it is preferable to intermittently add acetone in an amount of 0.04 mL/L or less per 1 g/L of selenium concentration in the acidic solution after the concentration of selenious acid in the acidic solution reaches 25 g/L or less in terms of selenium concentration.

酸化剤として過酸化水素を使用する場合、過酸化水素は一般に20~60%水溶液として取り扱われるがその濃度は特に指定されない。過酸化水素としての添加量は、一回のアセトンの添加量の0.03体積倍以上であることが好ましい。 When hydrogen peroxide is used as the oxidizing agent, it is generally handled as a 20-60% aqueous solution, but the concentration is not specifically specified. The amount of hydrogen peroxide added is preferably at least 0.03 volume times the amount of acetone added at one time.

アセチルアルデヒドやケトカルボン酸が酸性液中に蓄積すると溶液の粘度が高くなり、さらに亜セレン酸の被還元速度が上昇することで析出するセレンが大きな球となることがある。沈殿したセレンはスラリーとして扱うことが好ましく、過酸化水素にはアセチルアルデヒドやケトカルボン酸を酸化分解して沈殿する単体セレンをスラリー化する効果もある。 When acetylaldehyde and ketocarboxylic acids accumulate in the acidic solution, the viscosity of the solution increases, and the rate at which selenious acid is reduced increases, which can cause the precipitated selenium to form large spheres. It is preferable to handle the precipitated selenium as a slurry, and hydrogen peroxide also has the effect of oxidizing and decomposing the acetylaldehyde and ketocarboxylic acids, turning the precipitated elemental selenium into a slurry.

酸性液中に析出した沈殿物に対し、フィルタープレス等により固液分離することでセレンを得る。固液分離で回収された後のセレンは、さらに蒸留することで純度を上げることができる。また、セレンを還元沈殿した後の酸性液に対し、二酸化硫黄を吹き込んで過剰な酸化剤を分解し、残存セレンを沈殿回収してもよい。 Selenium is obtained by solid-liquid separation of the precipitate that has formed in the acidic solution using a filter press or similar. The purity of the selenium recovered by solid-liquid separation can be increased by further distillation. In addition, sulfur dioxide can be blown into the acidic solution after the selenium has been reduced and precipitated to break down the excess oxidizing agent, and the remaining selenium can be recovered by precipitation.

以下、本発明及びその利点をより良く理解するための実施例を例示するが、本発明は実施例に限定されるものではない。 The following examples are provided to better understand the present invention and its advantages, but the present invention is not limited to these examples.

<処理対象液(亜セレン酸を含む酸性液)の調製>
銅製錬の銅電解精製工程から回収された電解殿物を硫酸で処理することで銅を除いた。
次に、濃塩酸と60%過酸化水素水を添加して溶解し、固液分離してPLS(浸出貴液)を得た。
次に、PLSを6℃まで冷却して卑金属分を沈殿除去した後、酸濃度を2N以上に調整したDBC(ジブチルカルビトール)と当該PLSとを混合して金を抽出した。
金抽出後のPLSを処理対象液とした。処理対象液のセレン濃度は36g/Lであった。
<Preparation of treatment target liquid (acidic liquid containing selenious acid)>
Copper was removed from the electrolytic precipitate recovered from the copper electrorefining process of copper smelting by treating it with sulfuric acid.
Next, concentrated hydrochloric acid and 60% hydrogen peroxide were added to dissolve the mixture, and the mixture was subjected to solid-liquid separation to obtain PLS (pure leach liquor).
Next, the PLS was cooled to 6°C to precipitate and remove the base metals, and then the PLS was mixed with DBC (dibutyl carbitol) whose acid concentration had been adjusted to 2N or more to extract the gold.
The PLS after gold extraction was used as the treatment liquid. The selenium concentration in the treatment liquid was 36 g/L.

(試験例1)
上記処理対象液を300mL量り取り、80~85℃に加温した。
次に、実施例1として、アセトンを1mL添加して反応を開始した。60分ごとにアセトンを1mL添加した。ここで、2回目以降の各アセトンの添加の40分前に、それぞれ過酸化水素水(30体積%)を0.1mL添加した。
また、実施例2として、アセトンを1mL添加して反応を開始した。60分ごとにアセトンを1mL添加した。実施例2では過酸化水素水を添加せず、アセトン添加後から反応停止まで、反応中エアレーションを行った条件で実施した。当該エアレーションとしては、反応液にチューブを差し込み、ポンプを用いて200mL/分で空気を供給した。
実施例1及び2のいずれの場合でも、添加したアセトンの総量が5mLに達した後さらに30分攪拌した。
アセトン添加を終了した後、残ったアルデヒドやピルビン酸を分解してこの後の二酸化硫黄による還元時に難還元性のセレンが発生することを抑制するため、再度過酸化水素水を2mL添加して30分攪拌した。
次に、75℃に反応液の液温を調整し、二酸化硫黄と空気の混合気を吹き込んだ。1時間後に反応を停止し、固液分離した。この段階で溶液中に残留しているセレンを難還元性セレン化合物とした。セレン還元反応中、減少した水分量は純水で補充した。
(Test Example 1)
300 mL of the liquid to be treated was measured out and heated to 80 to 85°C.
Next, 1 mL of acetone was added to start the reaction in Example 1. 1 mL of acetone was added every 60 minutes. Here, 0.1 mL of hydrogen peroxide solution (30% by volume) was added 40 minutes before each addition of acetone from the second time onwards.
In Example 2, 1 mL of acetone was added to start the reaction. 1 mL of acetone was added every 60 minutes. In Example 2, hydrogen peroxide solution was not added, and the reaction was aerated during the reaction from the addition of acetone until the reaction was stopped. For the aeration, a tube was inserted into the reaction solution, and air was supplied at 200 mL/min using a pump.
In both cases of Examples 1 and 2, after the total amount of acetone added reached 5 mL, stirring was continued for an additional 30 minutes.
After the addition of acetone was completed, 2 mL of hydrogen peroxide was added again and stirred for 30 minutes in order to decompose the remaining aldehyde and pyruvic acid and suppress the generation of difficult-to-reduc selenium during the subsequent reduction with sulfur dioxide.
Next, the temperature of the reaction solution was adjusted to 75°C, and a mixture of sulfur dioxide and air was blown in. After one hour, the reaction was stopped and solid-liquid separation was performed. At this stage, the selenium remaining in the solution was treated as a difficult-to-reduc selenium compound. The amount of water lost during the selenium reduction reaction was replenished with pure water.

二酸化硫黄と空気の混合気を吹き込む前と吹き込み終了後に、それぞれ実施例1及び2のサンプル溶液を採取した。サンプル溶液から2mLを分取して50mLに規正した。ICP-OES(セイコー社製SPS3100)により溶液中のセレン濃度を定量した。
試験条件及び評価結果を表1に示す。
Before and after the blowing of the mixture of sulfur dioxide and air, sample solutions of Examples 1 and 2 were collected. 2 mL was taken from the sample solution and adjusted to 50 mL. The selenium concentration in the solution was quantified using ICP-OES (Seiko SPS3100).
The test conditions and evaluation results are shown in Table 1.

表1によれば、亜セレン酸の還元中に酸化剤を供給することで難還元性セレンの生成が抑えられたことが分かる。その添加量は過酸化水素で見ると、アセトン1mLに対して過酸化水素水(30体積%)0.1mLで効果を示した。すなわち添加アセトン量の0.03体積倍の過酸化水素であった。 Table 1 shows that the production of difficult-to-reduc selenium was suppressed by supplying an oxidizing agent during the reduction of selenious acid. In terms of the amount of hydrogen peroxide added, the effect was seen with 0.1 mL of hydrogen peroxide (30% by volume) per 1 mL of acetone. In other words, the amount of hydrogen peroxide added was 0.03 times the volume of acetone.

(試験例2)
試験例1と同じ処理対象液を300mL量り取り、80~85℃に加温した。
次に、アセトンを0.5mL添加して反応を開始した。30分毎(実施例3)もしくは60分毎(実施例4)にアセトンを0.5mL添加した。アセトンの添加15分前に過酸化水素水を都度0.1mL添加した。アセトン添加量の合計が2mLに達した後30分攪拌し、二酸化硫黄と空気の混合気を吹き込んだ。
比較例1として初期にアセトンを2mL投入し、120分攪拌後に二酸化硫黄と空気の混合気を吹き込んで亜セレン酸の還元を行った。
実施例、比較例共に二酸化硫黄と空気の混合気を吹き込む前に改めて過酸化水素水の添加はしなかった。
後の操作は試験例1に準じる。ICP-OES(セイコー社製SPS3100)によりセレンの濃度を定量した。
試験条件及び評価結果を表2に示す。
(Test Example 2)
300 mL of the same liquid to be treated as in Test Example 1 was measured out and heated to 80 to 85°C.
Next, 0.5 mL of acetone was added to start the reaction. 0.5 mL of acetone was added every 30 minutes (Example 3) or every 60 minutes (Example 4). 15 minutes before the addition of acetone, 0.1 mL of hydrogen peroxide solution was added each time. After the total amount of acetone added reached 2 mL, the mixture was stirred for 30 minutes and a mixture of sulfur dioxide and air was blown in.
In Comparative Example 1, 2 mL of acetone was initially added, and after stirring for 120 minutes, a mixture of sulfur dioxide and air was blown in to reduce selenious acid.
In both the Example and Comparative Example, hydrogen peroxide solution was not added before blowing in the mixture of sulfur dioxide and air.
The subsequent procedures were the same as in Test Example 1. The selenium concentration was quantified using ICP-OES (Seiko SPS3100).
The test conditions and evaluation results are shown in Table 2.

表2によれば、アセトン2mL/対象液300mLによって還元-沈殿されるセレンは12g/Lであり、生じた難還元性セレンはアセトン添加間隔が長いほど少量であることがわかった。
アセトンによる亜セレン酸の還元速度は速く、難還元性セレンの生成抑制には亜セレン酸の還元速度が影響するが、アセトンを間歇的に添加すれば難還元性セレンの生成を抑制でき、その時間間隔は30分以上であることがより好ましいことがわかる。
According to Table 2, the amount of selenium reduced and precipitated by 2 mL of acetone/300 mL of the target solution was 12 g/L, and it was found that the amount of hardly-reducible selenium produced was smaller the longer the interval between additions of acetone.
The reduction rate of selenious acid by acetone is fast, and the inhibition of the production of difficult-to-reducible selenium is affected by the reduction rate of selenious acid. However, it is clear that the production of difficult-to-reducible selenium can be inhibited by intermittently adding acetone, and that the time interval is preferably 30 minutes or more.

(試験例3)
試験例1と同じ処理対象液を300mL量り取り、75~80℃に加温した。
次に、アセトンを1mL添加して反応を開始した。60分毎にアセトンを添加した。アセトンの添加量は徐々に減らした。アセトンの添加15分前に過酸化水素水を都度0.1mL(実施例5、7)もしくは0.2mL(実施例6)添加した。
アセトン添加量の合計が2mLに達した後30分攪拌し、二酸化硫黄と空気の混合気を吹き込んで残った亜セレン酸の還元を行った。二酸化硫黄と空気の混合気を吹き込む前に改めて過酸化水素の添加はしなかった。
比較例2として、過酸化水素の都度添加を行わなかった還元も実施した。
後の操作は試験例1に準じる。ICP-OES(セイコー社製SPS3100)によりセレンの濃度を定量した。
試験条件及び評価結果を表3に示す。なお、反応途中のセレン濃度は表4に示す。表4に記載の「アセトン添加量/Se」は、「アセトン一回添加当たりのアセトン添加量(ml/L)÷酸性液中のセレン濃度(g/L)」を示す。
(Test Example 3)
300 mL of the same liquid to be treated as in Test Example 1 was measured out and heated to 75 to 80°C.
Next, 1 mL of acetone was added to start the reaction. Acetone was added every 60 minutes. The amount of acetone added was gradually reduced. 0.1 mL (Examples 5 and 7) or 0.2 mL (Example 6) of hydrogen peroxide solution was added each time 15 minutes before the addition of acetone.
After the total amount of acetone added reached 2 mL, the mixture was stirred for 30 minutes and then a mixture of sulfur dioxide and air was blown in to reduce the remaining selenious acid. No hydrogen peroxide was added before blowing in the mixture of sulfur dioxide and air.
As comparative example 2, a reduction was also carried out in which no hydrogen peroxide was added each time.
The subsequent procedures were the same as in Test Example 1. The selenium concentration was quantified using ICP-OES (Seiko SPS3100).
The test conditions and the evaluation results are shown in Table 3. The selenium concentration during the reaction is shown in Table 4. "Amount of acetone added/Se" in Table 4 indicates "amount of acetone added per one addition (ml/L) ÷ selenium concentration in the acidic solution (g/L)."

実施例5~7の結果から、亜セレン酸の還元反応中に過酸化水素を添加して、さらに反応の進行に従ってアセトンの添加量を減らすと、難還元性のセレンの生成がより良好に抑制されることが分かった。 The results of Examples 5 to 7 show that adding hydrogen peroxide during the reduction reaction of selenious acid and then decreasing the amount of acetone added as the reaction progresses can better suppress the production of difficult-to-reduc selenium.

難還元性のセレンは、アセトンと反応した亜セレン酸が、最終還元生成物の単体セレンに到る前にアセトンと反応した時に生じると考えられる。そこで、中間生成物を過酸化水素で酸化分解し、かつ中間生成物とアセトンの会合を極力抑えるようアセトンを添加することで効果を示した。なお比較例1と比較例2とを比較すると、アセトン添加量を徐々に減らすだけでも効果があることは分かる。 It is believed that difficult-to-reduc selenium is produced when selenious acid reacts with acetone before it reaches the final reduction product, elemental selenium. Therefore, the intermediate product was oxidized and decomposed with hydrogen peroxide, and acetone was added to minimize association between the intermediate product and acetone, demonstrating its effectiveness. Furthermore, a comparison of Comparative Example 1 and Comparative Example 2 shows that even gradually reducing the amount of acetone added is effective.

実施例3と実施例5~7では反応温度が異なるが、アセトンの添加量を調整すると温度の効果をしのぐことも可能であることを示す。特に実施例7との比較では温度が低いのにもかかわらず難還元性のセレン生成量は半分になっている。 The reaction temperatures in Example 3 and Examples 5 to 7 are different, but this shows that it is possible to overcome the effect of temperature by adjusting the amount of acetone added. In particular, compared to Example 7, the amount of difficult-to-reduc selenium produced is half, despite the lower temperature.

Claims (10)

亜セレン酸を含む酸性液からセレンを還元沈殿して回収する方法であり、
前記酸性液にアセトンを連続的または間歇的に添加しつつ、前記アセトンと前記亜セレン酸との反応で生じる有機化合物を酸化剤を用いて酸化する、セレンの回収方法。
This is a method for recovering selenium from an acidic solution containing selenious acid by reduction and precipitation,
A method for recovering selenium, comprising the steps of: continuously or intermittently adding acetone to the acidic solution; and oxidizing an organic compound produced by a reaction between the acetone and the selenious acid with an oxidizing agent.
前記酸性液の液温を70℃以上に加温し、前記酸性液中のセレン濃度1g/Lに対してアセトンを0.4mL/L以下の量だけ、1分以上の間隔をとりつつ間歇的に添加する、請求項1に記載のセレンの回収方法。 The method for recovering selenium according to claim 1, wherein the temperature of the acidic solution is raised to 70°C or higher, and acetone is added intermittently at intervals of 1 minute or more in an amount of 0.4 mL/L or less per 1 g/L of selenium concentration in the acidic solution. 前記アセトンを0.4mL/L以下の量だけ、30分以上の間隔をとりつつ間歇的に添加する、請求項2に記載のセレンの回収方法。 The method for recovering selenium according to claim 2, wherein the acetone is added intermittently at intervals of 30 minutes or more in an amount of 0.4 mL/L or less. 前記酸性液へのアセトンの添加において、一回のアセトンの添加量を段階的に減少させる、請求項1~3のいずれか一項に記載のセレンの回収方法。 The method for recovering selenium according to any one of claims 1 to 3, wherein the amount of acetone added at one time is gradually reduced when adding acetone to the acidic solution. 前記酸性液中の亜セレン酸の濃度がセレン濃度として25g/L以下に達した以降は、前記酸性液中のセレン濃度1g/Lに対してアセトンを0.04mL/L以下の量だけ間歇的に添加する、請求項4に記載のセレンの回収方法。 The method for recovering selenium according to claim 4, wherein after the concentration of selenious acid in the acidic solution reaches 25 g/L or less as a selenium concentration, acetone is intermittently added in an amount of 0.04 mL/L or less per 1 g/L of selenium concentration in the acidic solution. 前記酸性液にアセトンを間歇的に添加し、且つ、前記アセトンの毎回の添加後に前記酸化剤を添加する、請求項1~5のいずれか一項に記載のセレンの回収方法。 The method for recovering selenium according to any one of claims 1 to 5, wherein acetone is intermittently added to the acidic solution, and the oxidizing agent is added after each addition of the acetone. 前記セレンを還元沈殿した後の前記酸性液に対し、二酸化硫黄を吹き込んで過剰な酸化剤を分解し、残存セレンを沈殿回収する、請求項1~6のいずれか一項に記載のセレンの回収方法。 The method for recovering selenium according to any one of claims 1 to 6, in which sulfur dioxide is blown into the acidic liquid after the selenium has been reduced and precipitated to decompose the excess oxidizing agent and recover the remaining selenium by precipitation. 前記酸化剤は、ケトカルボン酸を酸化させる酸化剤である、請求項1~7のいずれか一項に記載のセレンの回収方法。 The method for recovering selenium according to any one of claims 1 to 7, wherein the oxidizing agent is an oxidizing agent that oxidizes a ketocarboxylic acid. 前記ケトカルボン酸を酸化させる酸化剤は、過酸化水素、酸素、次亜塩素酸及びオゾンのいずれか一種以上である、請求項8に記載のセレンの回収方法。 The method for recovering selenium according to claim 8, wherein the oxidizing agent for oxidizing the ketocarboxylic acid is at least one of hydrogen peroxide, oxygen, hypochlorous acid, and ozone. 前記過酸化水素の前記酸性液への添加量は、一回のアセトンの添加量の0.03体積倍以上である、請求項9に記載のセレンの回収方法。 The method for recovering selenium according to claim 9, wherein the amount of hydrogen peroxide added to the acidic solution is at least 0.03 times the volume of the amount of acetone added at one time.
JP2022026097A 2022-02-22 2022-02-22 How to recover selenium Active JP7664873B2 (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
JP2022026097A JP7664873B2 (en) 2022-02-22 2022-02-22 How to recover selenium

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
JP2022026097A JP7664873B2 (en) 2022-02-22 2022-02-22 How to recover selenium

Publications (2)

Publication Number Publication Date
JP2023122414A JP2023122414A (en) 2023-09-01
JP7664873B2 true JP7664873B2 (en) 2025-04-18

Family

ID=87798923

Family Applications (1)

Application Number Title Priority Date Filing Date
JP2022026097A Active JP7664873B2 (en) 2022-02-22 2022-02-22 How to recover selenium

Country Status (1)

Country Link
JP (1) JP7664873B2 (en)

Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2015077553A (en) 2013-10-16 2015-04-23 三菱重工業株式会社 Waste water treatment method and waste water treatment equipment
CN106542506A (en) 2016-12-08 2017-03-29 湖南水口山有色金属集团有限公司 A kind of method that selenium is reclaimed from heavy tellurium waste liquid
US20170158535A1 (en) 2014-07-14 2017-06-08 Wageningen Universiteit Process for recovering elemental selenium from wastewater
JP2018109207A (en) 2016-12-28 2018-07-12 Jx金属株式会社 Method of recovering selenium
JP2019077902A (en) 2017-10-20 2019-05-23 Jx金属株式会社 Method for removing selenium from acidic solution containing the same
JP2019147718A (en) 2018-02-27 2019-09-05 Jx金属株式会社 Method for recovering tellurium
JP2019214485A (en) 2018-06-11 2019-12-19 Jx金属株式会社 Method of recovering selenium
JP2020063484A (en) 2018-10-17 2020-04-23 Jx金属株式会社 Manufacturing method of selenium
JP2023071113A (en) 2021-11-10 2023-05-22 Jx金属株式会社 Selenium recovery method

Patent Citations (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP2015077553A (en) 2013-10-16 2015-04-23 三菱重工業株式会社 Waste water treatment method and waste water treatment equipment
US20170158535A1 (en) 2014-07-14 2017-06-08 Wageningen Universiteit Process for recovering elemental selenium from wastewater
CN106542506A (en) 2016-12-08 2017-03-29 湖南水口山有色金属集团有限公司 A kind of method that selenium is reclaimed from heavy tellurium waste liquid
JP2018109207A (en) 2016-12-28 2018-07-12 Jx金属株式会社 Method of recovering selenium
JP2019077902A (en) 2017-10-20 2019-05-23 Jx金属株式会社 Method for removing selenium from acidic solution containing the same
JP2019147718A (en) 2018-02-27 2019-09-05 Jx金属株式会社 Method for recovering tellurium
JP2019214485A (en) 2018-06-11 2019-12-19 Jx金属株式会社 Method of recovering selenium
JP2020063484A (en) 2018-10-17 2020-04-23 Jx金属株式会社 Manufacturing method of selenium
JP2023071113A (en) 2021-11-10 2023-05-22 Jx金属株式会社 Selenium recovery method

Also Published As

Publication number Publication date
JP2023122414A (en) 2023-09-01

Similar Documents

Publication Publication Date Title
CA2636122C (en) Process of leaching gold
JP4642796B2 (en) Gold leaching method
AU2007205792B2 (en) Method for leaching gold
JPWO1998058089A1 (en) Precious metal refining method
JP7198079B2 (en) Method for treating acidic liquids containing precious metals, selenium and tellurium
JPS5952218B2 (en) Method for recovering gold from copper electrolytic slime
JP7005384B2 (en) How to collect tellurium
JP6810887B2 (en) Separation and recovery methods for selenium, tellurium, and platinum group elements
JP7337209B2 (en) Iridium recovery method
JP7198036B2 (en) Selenium production method
JP7664873B2 (en) How to recover selenium
JP2019214485A (en) Method of recovering selenium
ZA200501592B (en) Method for the recovery of metals using chloride leaching and extraction
JP6835577B2 (en) How to collect valuables
JP7808528B2 (en) Method for recovering ruthenium and iridium
JP6967937B2 (en) How to collect selenium
JP2021023851A (en) Method of treating solution containing seleno sulfate
JP2018044200A (en) Treatment method for acidic hydrochloric acid containing metal
JP2018044201A (en) Treatment method for acidic hydrochloric acid containing metal
JP7247050B2 (en) Method for treating selenosulfuric acid solution
JP6882110B2 (en) Method for recovering precipitates containing platinum group elements
JP2024031675A (en) Ruthenium and iridium recovery method
JP7853840B2 (en) Selenium recovery methods
JP6882095B2 (en) Method for recovering precipitates containing platinum group elements
JP6964408B2 (en) How to collect selenium

Legal Events

Date Code Title Description
A621 Written request for application examination

Free format text: JAPANESE INTERMEDIATE CODE: A621

Effective date: 20240626

A977 Report on retrieval

Free format text: JAPANESE INTERMEDIATE CODE: A971007

Effective date: 20250228

TRDD Decision of grant or rejection written
A01 Written decision to grant a patent or to grant a registration (utility model)

Free format text: JAPANESE INTERMEDIATE CODE: A01

Effective date: 20250311

A61 First payment of annual fees (during grant procedure)

Free format text: JAPANESE INTERMEDIATE CODE: A61

Effective date: 20250408

R150 Certificate of patent or registration of utility model

Ref document number: 7664873

Country of ref document: JP

Free format text: JAPANESE INTERMEDIATE CODE: R150