JP5636769B2 - Manufacturing method and equipment that generate corrosive gas such as ruthenium tetroxide - Google Patents
Manufacturing method and equipment that generate corrosive gas such as ruthenium tetroxide Download PDFInfo
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Description
本発明は、四酸化ルテニウムなどの腐食性ガスが発生する製造方法において、反応終点を安全かつ正確に測定することができる製造方法に関する。 The present invention relates to a production method in which a reaction end point can be measured safely and accurately in a production method in which a corrosive gas such as ruthenium tetroxide is generated.
白金族金属を含む溶液からルテニウムを分離回収する方法として、ルテニウムの揮発性を利用した酸化蒸留方法が知られている。白金族金属のうち、ルテニウム(Ru)とオスミウム(Os)の酸化物は揮発性を有するので他の白金族金属から蒸留して分離することができる。例えば特公平01−30896号公報(特許文献1)には、白金族金属を含む溶液に臭素酸ナトリウムを加えてルテニウム等を四酸化物にし、これを蒸留して分離回収する方法が記載されている。 As a method for separating and recovering ruthenium from a solution containing a platinum group metal, an oxidative distillation method using the volatility of ruthenium is known. Of the platinum group metals, ruthenium (Ru) and osmium (Os) oxides are volatile and can be separated from other platinum group metals by distillation. For example, Japanese Patent Publication No. 01-30896 (Patent Document 1) describes a method in which sodium bromate is added to a solution containing a platinum group metal to form ruthenium or the like into a tetraoxide, and this is distilled and separated and recovered. Yes.
さらに、ルテニウムの酸化蒸留法について、蒸留した四酸化ルテニウムを臭素酸ナトリウム溶液を入れたトラップ槽に導入して白金等のミストを捕集すると共に四酸化ルテニウムの還元を防止し収率を高める方法が知られている(特開2006−161096号公報:特許文献2)。また、ルテニウムの酸化蒸留法をルテニウム含有スクラップからルテニウムを回収する方法に適用することも知られている(特開2009−203486号公報:特許文献3)。 Furthermore, about the oxidative distillation method of ruthenium, a method of introducing distilled ruthenium tetroxide into a trap tank containing a sodium bromate solution to collect mist such as platinum and preventing the reduction of ruthenium tetroxide to increase the yield. Is known (Japanese Patent Laid-Open No. 2006-161096: Patent Document 2). It is also known to apply ruthenium oxidative distillation to a method of recovering ruthenium from ruthenium-containing scrap (Japanese Patent Laid-Open No. 2009-203486: Patent Document 3).
従来、ルテニウムの酸化蒸留法において、酸化蒸留反応の終点は原料溶液量や蒸留温度などの反応条件に基づいて経験的に判定し、あるいは酸化反応槽や回収槽の溶液の色変化が落着いた様子を目視観察して判断していた。 Conventionally, in the ruthenium oxidative distillation method, the end point of the oxidative distillation reaction is determined empirically based on the reaction conditions such as the amount of the raw material solution and the distillation temperature, or the color change of the solution in the oxidation reaction tank and the recovery tank has settled Was determined by visual observation.
しかし、反応時間を経験的に定めると、反応元液中のルテニウムの量が変動した場合などに対応できず、また反応槽や回収槽の溶液の色変化の目視確認では微少な変化が分かり難く、また作業者による誤差も大きいなどの問題があった。 However, if the reaction time is determined empirically, it cannot cope with the case where the amount of ruthenium in the reaction source solution fluctuates, and minute changes are difficult to see by visual confirmation of the color change of the solution in the reaction tank and recovery tank. In addition, there were problems such as large errors caused by workers.
一方、酸化蒸留によって発生する四酸化ルテニウム蒸気は非常に不安定な腐食性ガスであるため、反応槽で四酸化ルテニウム量などを測定すると器具の腐食が進み、信頼性ある測定を長期間行うことが難しく、また回収槽での測定ではルテニウム回収液に不純物が混入する問題があり、このため従来は客観的な反応制御が難しかった。 On the other hand, since ruthenium tetroxide vapor generated by oxidative distillation is a very unstable corrosive gas, when measuring the amount of ruthenium tetroxide in the reaction vessel, the corrosion of the instrument proceeds, and reliable measurement should be performed for a long time. In addition, there is a problem that impurities are mixed in the ruthenium recovery liquid in the measurement in the recovery tank, and thus it has been difficult to control objective reaction conventionally.
本発明は、四酸化ルテニウムなどのような腐食性ガスの生成を伴う製造方法について、反応終点を安全かつ正確に測定することができ、作業員の経験や目視に頼らずに客観的に反応を制御することができる製造方法を提供する。 The present invention can measure the reaction end point safely and accurately for a production method involving the generation of a corrosive gas such as ruthenium tetroxide, and objectively reacts without relying on the experience or visual observation of workers. A production method that can be controlled is provided.
本発明は、腐食性の四酸化ルテニウムガスが発生する塩化ルテニウム酸溶液の製造において、以下の構成を有する塩化ルテニウム酸溶液の製造方法および製造装置に関する。
〔1〕白金族金属を含む塩酸酸性溶液に臭素酸ナトリウムを添加して四酸化ルテニウムを酸化蒸留させ、該四酸化ルテニウムを塩酸に吸収させて塩化ルテニウム酸溶液を回収する方法において、塩酸による吸収工程から排出される副生ガスをアルカリ溶液に吸収させ、このアルカリ溶液の酸化還元電位の電位変化率を測定し、該電位変化率について一定値以下の定常状態が継続することによって酸化蒸留の反応終点とすることを特徴とする塩化ルテニウム酸溶液の製造方法。
〔2〕上記[1]の方法において、副生ガスを水酸化ナトリウム溶液に吸収させ、該水酸化ナトリウム溶液の酸化還元電位の電位変化率を測定する塩化ルテニウム酸溶液の製造方法。
〔3〕上記[1]または上記[2]の方法において、電位変化率が0.5mV/min以下の定常状態が30分継続した段階を反応終点とする塩化ルテニウム酸溶液の製造方法。
〔4〕白金族金属を含む塩酸酸性溶液に臭素酸ナトリウムを添加して四酸化ルテニウムを酸化蒸留させる反応槽、四酸化ルテニウム蒸留ガスを塩酸に吸収させて塩化ルテニウム酸溶液を回収する回収槽、回収槽から排出される副生ガスをアルカリ溶液に吸収させる吸収槽、この吸収槽に装着された酸化還元電位計、反応槽で発生したガスを回収槽に導入する手段および回収槽から排出される副生ガスを吸収槽に導入する手段を有し、アルカリ溶液の酸化還元電位の電位変化率を測定し、該電位変化率について一定値以下の定常状態が継続することによって蒸留の反応終点とすることを特徴とする塩化ルテニウム酸溶液の製造装置。
The present invention relates to a method and an apparatus for producing a ruthenium chloride solution having the following configuration in the production of a ruthenium chloride solution in which corrosive ruthenium tetroxide gas is generated .
[1] In a method in which sodium bromate is added to an acidic hydrochloric acid solution containing a platinum group metal to oxidatively distill ruthenium tetroxide, and the ruthenium tetroxide is absorbed by hydrochloric acid to recover the ruthenium chloride solution. The by-product gas discharged from the process is absorbed in an alkaline solution, and the potential change rate of the oxidation-reduction potential of the alkaline solution is measured, and the steady state of a certain value or less continues with respect to the potential change rate. A method for producing a ruthenic acid chloride solution, characterized by having an end point.
[2] A method for producing a ruthenium chloride solution in which the by-product gas is absorbed in a sodium hydroxide solution and the potential change rate of the oxidation-reduction potential of the sodium hydroxide solution is measured in the method of [1].
[3] A method for producing a ruthenium chloride solution in which the reaction end point is a stage in which a steady state having a potential change rate of 0.5 mV / min or less continues for 30 minutes in the method [1] or [2] above.
[4] A reaction tank in which sodium bromate is added to an acidic hydrochloric acid solution containing a platinum group metal to oxidatively distill ruthenium tetroxide, a recovery tank in which ruthenium tetroxide distillation gas is absorbed into hydrochloric acid to recover the ruthenium chloride solution, An absorption tank that absorbs by-product gas discharged from the recovery tank into the alkali solution, a redox potentiometer attached to the absorption tank, a means for introducing the gas generated in the reaction tank into the recovery tank, and a discharge tank It has means for introducing by-product gas into the absorption tank, measures the potential change rate of the oxidation-reduction potential of the alkaline solution , and sets the end point of the distillation reaction by continuing a steady state below a certain value for the potential change rate. An apparatus for producing a ruthenic acid chloride solution.
本発明の製造方法は、生成した腐食性の四酸化ルテニウムガスに代えて、副生ガスによる経時変化に基づいて反応終点を把握するので、腐食性ガスによる測定器具の劣化の問題が無く、客観的に反応終点を判断することができる。
Since the production method of the present invention grasps the reaction end point based on the change over time due to the by-product gas instead of the generated corrosive ruthenium tetroxide gas , there is no problem of deterioration of the measuring instrument due to the corrosive gas, and the objective. Thus, the end point of the reaction can be judged .
本発明の製造方法によれば、白金族金属からルテニウムを分離回収する製造方法において、臭素酸ナトリウムによってルテニウムを酸化して四酸化ルテニウムを蒸留させて分離回収する際に、発生した腐食性ガスの四酸化ルテニウムを塩酸に吸収させると共に、この酸化蒸留工程で副生したガス(主に臭素ガスおよび塩素ガス)をアルカリ溶液に吸収させ、このアルカリ溶液の酸化還元電位の経時変化によって酸化蒸留反応の終点を正確に測定することができる。 According to the production method of the present invention, in the production method for separating and recovering ruthenium from a platinum group metal, when the ruthenium is oxidized by sodium bromate and ruthenium tetroxide is distilled and separated and recovered, the corrosive gas generated While ruthenium tetroxide is absorbed into hydrochloric acid, the gas (mainly bromine gas and chlorine gas) by-produced in this oxidative distillation process is absorbed into an alkali solution, and the oxidation-reduction reaction of the oxidative distillation reaction is caused by the change over time of the redox potential of this alkaline solution. The end point can be accurately measured.
本発明の製造方法は、例えば、酸化蒸留工程で副生したガスを水酸化ナトリウム溶液に吸収させ、この水酸化ナトリウム溶液の電位変化率によって酸化蒸留反応の終点を正確に測定することができる。具体的には、電位変化率が0.5mV/min以下の定常状態が30分継続した段階を反応終点として客観的に判断することができる。 In the production method of the present invention, for example, a gas generated as a by-product in the oxidative distillation step is absorbed in a sodium hydroxide solution, and the end point of the oxidative distillation reaction can be accurately measured by the potential change rate of the sodium hydroxide solution. Specifically, the stage where the steady state where the potential change rate is 0.5 mV / min or less continues for 30 minutes can be objectively determined as the reaction end point.
以下、本発明に係る四酸化ルテニウムガスの発生を伴う塩化ルテニウム酸溶液の製造方法および製造装置について、実施例に基づいて具体的に説明する。
EXAMPLES Hereinafter, the manufacturing method and manufacturing apparatus of a ruthenium chloride solution accompanied by generation of ruthenium tetroxide gas according to the present invention will be specifically described based on examples.
本発明の製造方法は、白金族金属を含む塩酸酸性溶液に臭素酸ナトリウムを添加して四酸化ルテニウムを酸化蒸留させ、該四酸化ルテニウムを塩酸に吸収させて塩化ルテニウム酸溶液を回収する方法において、塩酸による吸収工程から排出される副生ガスをアルカリ溶液に吸収させ、このアルカリ溶液の酸化還元電位の電位変化率を測定し、該電位変化率について一定値以下の定常状態が継続することによって酸化蒸留の反応終点とすることを特徴とする塩化ルテニウム酸溶液の製造方法である。
The production method of the present invention is a method in which sodium bromate is added to an acidic hydrochloric acid solution containing a platinum group metal to oxidatively distill ruthenium tetroxide, and the ruthenium tetroxide is absorbed into hydrochloric acid to recover the ruthenium chloride solution. By absorbing the by-product gas discharged from the absorption step with hydrochloric acid into the alkaline solution, measuring the potential change rate of the oxidation-reduction potential of the alkaline solution, and continuing the steady state below a certain value for the potential change rate A method for producing a ruthenic acid chloride solution characterized in that the reaction end point of oxidative distillation is used.
本発明に係る製造装置は、白金族金属を含む塩酸酸性溶液に臭素酸ナトリウムを添加して四酸化ルテニウムを酸化蒸留させる反応槽、四酸化ルテニウム蒸留ガスを塩酸に吸収させて塩化ルテニウム酸溶液を回収する回収槽、回収槽から排出される副生ガスをアルカリ溶液に吸収させる吸収槽、この吸収槽に装着された酸化還元電位計、反応槽で発生したガスを回収槽に導入する手段および回収槽から排出される副生ガスを吸収槽に導入する手段を有し、アルカリ溶液の酸化還元電位の電位変化率を測定し、該電位変化率について一定値以下の定常状態が継続することによって蒸留の反応終点とすることを特徴とする塩化ルテニウム酸溶液の製造装置である。
The production apparatus according to the present invention includes a reaction vessel in which sodium bromate is added to an acidic hydrochloric acid solution containing a platinum group metal to oxidatively distill ruthenium tetroxide, and ruthenium tetroxide distillation gas is absorbed into hydrochloric acid to produce a ruthenic acid chloride solution. Recovery tank for recovery, absorption tank for absorbing by-product gas discharged from the recovery tank, an oxidation-reduction potentiometer attached to the absorption tank, means for introducing the gas generated in the reaction tank into the recovery tank, and recovery It has a means for introducing by-product gas discharged from the tank into the absorption tank, measures the potential change rate of the oxidation-reduction potential of the alkaline solution, and distills by continuing the steady state below a certain value for the potential change rate. An apparatus for producing a ruthenium chloride solution characterized by having the reaction end point of
〔装置構成〕
白金族金属含有溶液からルテニウムを分離回収する蒸留装置の構成例を図1に示す。
図示するように、反応槽10はマントルヒータに設置されており、反応槽10には白金(Pt)およびルテニウム(Ru)を含有する白金族金属を含有する塩酸酸性溶液(元液)が入っている。この元液に水酸化ナトリウム(NaOH)を加えてpHを約1に調整する。pH調整した元液に酸化剤の臭素酸ナトリウム溶液(NaBr03)を加えて、約80℃に加熱する。元液中のルテニウムは臭素酸ナトリウムによって酸化され、揮発性の四酸化ルテニウム(RuO4)になり蒸留ガスを生じる。同時に臭素ガス(Br2)が副生する。
〔Device configuration〕
A configuration example of a distillation apparatus for separating and recovering ruthenium from a platinum group metal-containing solution is shown in FIG.
As shown in the figure, the reaction vessel 10 is installed in a mantle heater, and the reaction vessel 10 contains a hydrochloric acid acidic solution (original solution) containing a platinum group metal containing platinum (Pt) and ruthenium (Ru). Yes. Sodium hydroxide (NaOH) is added to the original solution to adjust the pH to about 1. A sodium bromate solution (NaBr0 3 ) as an oxidizing agent is added to the pH-adjusted original solution and heated to about 80 ° C. Ruthenium in the original solution is oxidized by sodium bromate and becomes volatile ruthenium tetroxide (RuO 4 ), producing a distillation gas. At the same time, bromine gas (Br 2 ) is by-produced.
反応槽10には回収槽11が接続している。図示する装置例では回収槽11が三段に設けられている。回収槽11には塩酸(HCl)が入っており、蒸留したRuO4ガスは回収槽11に導入され、この塩酸に吸収されて塩化ルテニウム酸溶液(H2RuCl6)になり、回収される。回収槽11では塩素ガス(Cl2)が副生する。反応槽10において副生したガス(主にBr2)はRuO4ガスと共に回収槽11に導入されるが、酸性であるので塩酸には殆ど吸収されずに回収槽11において副生したガス(主にCl2)と共に槽外に排出される。 A recovery tank 11 is connected to the reaction tank 10. In the illustrated apparatus example, the collection tanks 11 are provided in three stages. The recovery tank 11 contains hydrochloric acid (HCl), and the distilled RuO 4 gas is introduced into the recovery tank 11 and is absorbed by the hydrochloric acid to become a ruthenic acid chloride solution (H 2 RuCl 6 ) and recovered. Chlorine gas (Cl 2 ) is by-produced in the recovery tank 11. The gas (mainly Br 2 ) produced as a by-product in the reaction tank 10 is introduced into the recovery tank 11 together with the RuO 4 gas. And Cl 2 ).
回収槽11には吸収槽12が接続している。図示する装置例では吸収槽12が二段に設けられている。吸収槽12には水酸化ナトリウム(NaOH)溶液が入っている。回収槽11から排出された副生ガスは吸収槽12に導入され、NaOH溶液に吸収される。二段目の吸収槽12にはNaOH溶液(吸収液)の酸化還元電位を測定するORP計16が設置されている。
An absorption tank 12 is connected to the collection tank 11. In the illustrated apparatus example, the absorption tank 12 is provided in two stages. The absorption tank 12 contains a sodium hydroxide (NaOH) solution. By-product gas discharged from the recovery tank 11 is introduced into the absorption tank 12 and absorbed by the NaOH solution. An
二段目の吸収槽12には空槽13が接続しており、さらに空槽13に流量計14を経由して吸気ポンプ15が接続している。反応槽10から回収槽11、吸収槽12、空槽13、および流量計14に至る経路は吸気ポンプ15によって吸引されており、RuO4蒸留ガスおよび副生ガスは吸引されて各槽に導入され、また吸気ポンプ15によって流量が制御される。さらに空槽13では吸引されたガス中のミストなどが捕集される。
An
〔電位測定〕
回収槽11から排出された副生ガスは吸収槽12に導入され、NaOH溶液に吸収される。副生ガスを吸収したNaOH溶液の酸化還元電位がORP計16によって測定され、その経時変化、例えば、電位変化率が次式によって測定される。
[Potential measurement]
By-product gas discharged from the recovery tank 11 is introduced into the absorption tank 12 and absorbed by the NaOH solution. The oxidation-reduction potential of the NaOH solution that has absorbed the by-product gas is measured by the
〔ΔE/Δt〕n=(En−En-1)/(tn−tn-1)
式中、ΔEは電位変化量、Δtは単位時間、Enはn測定時の電位、En-1は(n-1)測定時の電位、tnはn測定時、tn-1は(n-1)測定時。
[ΔE / Δt] n = (E n −E n−1 ) / (t n −t n−1 )
Wherein, Delta] E is the potential variation, Delta] t time units, E n is the potential at the n measurements, E n-1 is (n-1) measured at a potential, at t n is n measurements, t n-1 is (n-1) During measurement.
この電位変化率が基準以下であって、この基準以下の電位変化率が30分継続すれば酸化蒸留反応は終了したものと判断することができる。電位変化率の具体的な数値および定常状態の継続時間は装置構成の具体的な条件によって定めればよい。 If this potential change rate is below the reference and the potential change rate below this reference continues for 30 minutes, it can be determined that the oxidative distillation reaction has ended. The specific numerical value of the potential change rate and the duration of the steady state may be determined according to specific conditions of the device configuration.
以下の実施例では、電位変化率の基準を0.5mV/min以下、定常状態の継続時間を30分以上としている。
(イ)電位変化率0.5mV/min以下
電位変化率(単位時間あたりの電位変化)がこの値にまで低下すると、反応槽内では茶色蒸気の発生がほぼ観測されなくなり、つまり四酸化ルテニウムの生成反応が落ち着く。
(ロ)継続時間を30分以上
電位変化率0.5mV/min以下の状態が30分以上経過すると、回収槽の色変化も観察されなくなり、また酸化還元電位も上昇せず、電位変化率はほぼ0 mV/minになり、四酸化ルテニウム蒸気および副生成ガス(臭素ガスと塩素ガス)が発生しなくなる。なお、流速が遅い場合は回収槽の変化が長時間持続するが、RuO4は生成しなくなるので、この経過時間によって反応終点とみなすことができる。また、酸化還元電位の測定値がばらつくことによってその変化率がばらついても、電位変化率が0.5mV/min以下になってから30分後であればその誤差範囲をカバーすることができる。
In the following examples, the reference for the potential change rate is 0.5 mV / min or less, and the duration of the steady state is 30 minutes or more.
(B) Potential change rate of 0.5 mV / min or less When the potential change rate (potential change per unit time) drops to this value, brown vapor is hardly observed in the reaction vessel, that is, ruthenium tetroxide The production reaction settles down.
(B) When the state of the potential change rate of 0.5 mV / min or less for 30 minutes or longer has elapsed for 30 minutes or longer, no color change in the recovery tank is observed, the oxidation-reduction potential does not rise, and the potential change rate is It becomes almost 0 mV / min, and ruthenium tetroxide vapor and by-product gases (bromine gas and chlorine gas) are not generated. Note that when the flow rate is slow, the change in the recovery tank lasts for a long time, but RuO 4 is no longer generated, and can be regarded as the reaction end point based on this elapsed time. Moreover, even if the change rate varies due to variations in the measured value of the oxidation-reduction potential, the error range can be covered 30 minutes after the potential change rate becomes 0.5 mV / min or less.
以下、本発明を実施例によって示す。
(イ)図1に示した蒸留装置を用いてルテニウムの酸化蒸留を行なった。
(ロ)図1の装置において、吸収槽12(2本目)(内液は4N NaOH水溶液)の酸化還元電位変化をORP計(vs Ag/AgCl)を用いて測定した。
(ハ)電位変化率=(電位変化)/(経過時間) の計算により、単位時間あたりの電位変化(mV/min)を算出した。
(ニ)Ru回収量は、反応終了後に溶液のRu濃度をICP-AESを用いて測定して求めた。
Ru回収率=(Ru回収量)/(反応前の元液中のRu量) の計算により、Ru回収率(%)を算出した。
The present invention will now be illustrated by examples.
(I) Ruthenium was oxidatively distilled using the distillation apparatus shown in FIG.
(B) In the apparatus of FIG. 1, the oxidation-reduction potential change of the absorption tank 12 (second) (inner solution is 4N NaOH aqueous solution) was measured using an ORP meter (vs Ag / AgCl).
(C) The potential change per unit time (mV / min) was calculated by calculating the rate of potential change = (potential change) / (elapsed time).
(D) The amount of Ru recovered was determined by measuring the Ru concentration of the solution using ICP-AES after the reaction was completed.
The Ru recovery rate (%) was calculated by calculating Ru recovery rate = (Ru recovery amount) / (Ru amount in the original solution before reaction).
〔実施例1〕
Ru(濃度23g/L)および白金族金属(Pt,Pd,Rh,Ir)を含む塩酸性溶液(pH マイナス1)にNaOH水溶液を加えてpH1に調整し、酸化剤NaBrO3を過剰量(RuがRuO4に酸化されるのに必要な当量の5倍量)添加して、マントルヒーターで80℃に加熱した反応槽内で撹拌し、吸引ポンプを用いて流速1L/minで吸引しながら反応させた。反応槽10で発生したRuO4蒸気を含むガスは、回収槽11(6N HCl水溶液)に導いてHCl溶液に吸収させ、塩化ルテニウム酸(H2RuCl6)溶液として回収した。回収槽11の排ガスを吸収槽12(4N NaOH水溶液)に導いて副生成ガス(Br2およびCl2)を吸収させた。この吸収槽12(2本目)のNaOH水溶液の酸化還元電位を5分おきに測定した。
電位変化率が0.5mV/min以下になってから30分経過した時点で、反応槽10の茶色蒸気発生はほぼなくなり、吸収槽12(2本目)の色変化もそれ以上は観測されなくなり、電位変化率もほぼ0mV/minに落ち着いたので、反応を終了した。その結果、Ruの回収率は99.2%であった。
[Example 1]
A hydrochloric acid solution (pH minus 1) containing Ru (concentration 23 g / L) and platinum group metals (Pt, Pd, Rh, Ir) is adjusted to
When 30 minutes have passed since the potential change rate became 0.5 mV / min or less, the generation of brown vapor in the reaction tank 10 almost disappeared, and no more color change in the absorption tank 12 (second) was observed. Since the potential change rate also settled at approximately 0 mV / min, the reaction was terminated. As a result, the recovery rate of Ru was 99.2%.
〔実施例2〕
吸引ポンプの流速を4L/minにした以外は実施例1と同様に行なった。
電位変化率が0.5mV/min以下になってから30分経過した時点で、反応槽10の茶色蒸気発生はほぼなくなり、吸収槽12(2本目)の色変化もそれ以上は観測されなくなり、電位変化率もほぼ0mV/minに落ち着いたので、反応を終了した。その結果、Ruの回収率は99.3%であった。
[Example 2]
The same operation as in Example 1 was performed except that the flow rate of the suction pump was changed to 4 L / min.
When 30 minutes have passed since the potential change rate became 0.5 mV / min or less, the generation of brown vapor in the reaction tank 10 almost disappeared, and no more color change in the absorption tank 12 (second) was observed. Since the potential change rate also settled at approximately 0 mV / min, the reaction was terminated. As a result, the recovery rate of Ru was 99.3%.
〔実施例3〕
吸引ポンプの流速を6L/minにした以外は実施例1と同様に行なった。
電位変化率が0.5mV/min以下になってから30分経過した時点で、反応槽10の茶色蒸気発生はほぼなくなり、吸収槽12(2本目)の色変化もそれ以上は観測されなくなり、電位変化率もほぼ0mV/minに落ち着いたので、反応を終了した。その結果、Ruの回収率は99.1%であった。
Example 3
The same procedure as in Example 1 was performed except that the flow rate of the suction pump was changed to 6 L / min.
When 30 minutes have passed since the potential change rate became 0.5 mV / min or less, the generation of brown vapor in the reaction tank 10 almost disappeared, and no more color change in the absorption tank 12 (second) was observed. Since the potential change rate also settled at approximately 0 mV / min, the reaction was terminated. As a result, the recovery rate of Ru was 99.1%.
〔実施例4〕
吸引ポンプの流速を10L/minにした以外は実施例1と同様に行なった。
電位変化率が0.5mV/min以下になってから30分経過した時点で、反応槽10の茶色蒸気発生はほぼなくなり、吸収槽12(2本目)の色変化もそれ以上は観測されなくなり、電位変化率もほぼ0mV/minに落ち着いたので、反応を終了した。その結果、Ruの回収率は99.8%であった。
Example 4
The same operation as in Example 1 was performed except that the flow rate of the suction pump was set to 10 L / min.
When 30 minutes have passed since the potential change rate became 0.5 mV / min or less, the generation of brown vapor in the reaction tank 10 almost disappeared, and no more color change in the absorption tank 12 (second) was observed. Since the potential change rate also settled at approximately 0 mV / min, the reaction was terminated. As a result, the recovery rate of Ru was 99.8%.
〔比較例1〕
実施例2の流速4L/minの条件で、反応を加熱開始から60分で停止した。このときの吸収槽12(2本目)の電位変化率は1.8mV/minであり、酸化還元電位はまだ上昇中で、吸収槽12の色変化もまだ落ち着いていなかった。また、反応槽10でも茶色蒸気がまだ少し発生していた。このときのRuの回収率は92.1%であった。
[Comparative Example 1]
The reaction was stopped in 60 minutes from the start of heating under the conditions of the flow rate of 4 L / min in Example 2. The potential change rate of the absorption tank 12 (second) at this time was 1.8 mV / min, the oxidation-reduction potential was still rising, and the color change of the absorption tank 12 was not yet settled. Further, a little brown vapor was still generated in the reaction vessel 10. The recovery rate of Ru at this time was 92.1%.
実施例1〜実施例4の結果を図2〜図4に示す。
図2はNaOH溶液の酸化還元電位グラフ、図3は図2に基づく電位変化率のグラフ、図4は電位変化率の拡大図であり状態変化を示すグラフである。
The results of Examples 1 to 4 are shown in FIGS.
2 is a graph showing the oxidation-reduction potential of the NaOH solution, FIG. 3 is a graph of the potential change rate based on FIG. 2, and FIG. 4 is an enlarged view of the potential change rate and showing the state change.
図2に示すように、実施例1は加熱時間180分で酸化還元電位は定常になり、実施例2〜実施例4では加熱時間60分で酸化還元電位は定常になっている。この経時変化を図3の電位変化率によってみると、実施例1〜実施例4の何れにおいても、電位変化率が0.5mV/min以下になってから30分経過すると電位変化がほぼ0mV/minに落ち着いている。この電位変化の状態を反応槽および回収槽の状態と対比してみると、図4に示すように、電位変化率が0.5mV/min以下になってから30分経過すると、反応槽10の蒸気発生はなくなり、吸収槽12のHCl溶液は薄黄色透明で変わらず、酸化蒸留反応が終了していることが確認できる。 As shown in FIG. 2, in Example 1, the redox potential becomes steady at a heating time of 180 minutes, and in Examples 2 to 4, the redox potential becomes steady at a heating time of 60 minutes. Looking at the change with time in terms of the potential change rate in FIG. 3, in any of Examples 1 to 4, the potential change is almost 0 mV / 30 minutes after 30 minutes have passed since the potential change rate became 0.5 mV / min or less. settled in min. When comparing the state of this potential change with the state of the reaction tank and the recovery tank, as shown in FIG. 4, after 30 minutes have passed since the potential change rate became 0.5 mV / min or less, Vapor generation disappears, and the HCl solution in the absorption tank 12 is light yellow and transparent, and it can be confirmed that the oxidative distillation reaction has been completed.
10−反応槽、11−回収槽、12−吸収槽、13−空槽、14−流量計、15−吸気ポンプ、16−ORP計 10-reaction tank, 11-recovery tank, 12-absorption tank, 13-empty tank, 14-flow meter, 15-intake pump, 16-ORP meter
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