• Title/Summary/Keyword: ammonium polyvanadate

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Precipitation Behavior of Ammonium Vanadate from Solution Containing Vanadium (바나듐 함유 수용액의 암모늄바나데이트 침전거동 고찰)

  • Yoon, Ho-Sung;Chae, Sujin;Kim, Chul-Joo;Chung, Kyeong Woo;Kim, Minseuk
    • Resources Recycling
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    • v.28 no.5
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    • pp.42-50
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    • 2019
  • In this study, the precipitation reaction of vanadium and ammonium chloride in aqueous solution was investigated in order to recover vanadium. Ammonium metavanadate having a crystal structure of [$NH_4VO_3$] was precipitated from aqueous solution containing vanadium at pH 9.2 ~ 9.4, and ammonium polyvanadate having a crystal structure of [$(NH_4)_2V_6O_{16}$] was precipitated when the pH of the aqueous solution containing vanadium was adjusted with sulfuric acid. Ammonium polyvanadate [$(NH_4)_2V_6O_{16}$] precipitated at a temperature of $80{\sim}90^{\circ}C$ and pH 2, and at a temperature of $40^{\circ}C$ and pH 6 ~ 8 of aqueous solution. In the acidic region of aqueous solution pH 2, the vanadium content of the aqueous solution should be at least 3,000 mg/L and the precipitation temperature should be maintained at $80^{\circ}C$ or higher in order to obtain a precipitation ratio of 99% or more. When the ammonium vanadate was precipitated in the alkaline region, the vanadium content was more than 10,000 mg/L and the precipitation temperature was maintained at $40^{\circ}C$ to increase the precipitation ratio. Aluminum was not precipitated regardless of the vanadium content and pH of the aqueous solution. However, the iron component reacts with ammonium chloride to precipitate into ammonium jarosite. Therefore, Fe component must be preferentially removed in order to increase the recovery of vanadium.

Effects of Vanadate Solution Property on the Precipitation of Ammonium (Meta, Poly)Vanadate (바나데이트 수용액 특성이 암모늄(메타, 폴리)바나데이트 침전에 미치는 영향)

  • Ho-Sung Yoon;Seo Jin Heo;Yujin Park;Rina Kim;Chul-Joo Kim;Kyeong Woo Chung;Hong In Kim
    • Resources Recycling
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    • v.32 no.3
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    • pp.26-37
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    • 2023
  • Good control of the solution pH and temperature is required to recover vanadium from the water leaching solution of vanadium ore after sodium roasting. However, such adjustments could lead to aluminum-vanadium and sodium-vanadium co-precipitation, which greatly affects the efficiency of vanadium recovery. In this study, a process that can increase the efficiency of vanadium recovery as ammonium metavanadate [NH4VO3] and ammonium polyvanadate [(NH4)2V6O16·H2O] was investigated by examining the characteristics of vanadium-containing aqueous solutions during precipitation. The aluminum content of vanadium-containing water leaching solutions has a great effect on the loss of vanadium when the pH of the aqueous solution is adjusted to 9. Therefore, a process to minimize aluminum leaching is also required. In this study, ~99% or more of vanadium present in vanadium-containing aqueous solutions was precipitated and recovered as NH4VO3 by adding 3 equivalents of ammonium chloride relative to the vanadium content at pH 9 and room temperature. (NH4)2V6O16·H2O was precipitated from the aluminum-vanadium coprecipitates generated during the pH-adjustment of the aqueous solutions to 9 by dissolving the coprecipitate in the solutions at pH 2.5 and controlling their sodium content to 2,000 mg/L or less. Approximately, 98% or more of the available (NH4)2V6O16·H2O could be precipitated and recovered from a solution with a vanadium content of 2,200 mg/L and a sodium content of 1,875 mg/L at pH 2.5 by adding approximately 3 equivalents of ammonium chloride relative to the vanadium content at 95℃ or higher. The overall process could precipitate and recover, approximately 91% or more of the total vanadium in the water leaching solution as NH4VO3 and (NH4)2V6O16·H2O.

Effect of Precipitation Temperature and Solution pH on the Precipitation of Ammonium Metavanadate (침전온도 및 수용액 pH가 암모늄메타바나데이트 침전반응에 미치는 영향)

  • Heo, Seo-Jin;Kim, Rina;Chung, Kyeong Woo;Jeon, Ho-Seok;Kim, Chul-Joo;Yoon, Ho-Sung
    • Resources Recycling
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    • v.30 no.6
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    • pp.3-11
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    • 2021
  • In this study, the effect of the solubility of ammonium metavanadate and the decomposition ratio of ammonium ions on a precipitation reaction-the precipitation of ammonium metavanadate by adding ammonium chloride to a sodium vanadate solution-was investigated. As the precipitation temperature and pH increased, the decomposition ratio of ammonium ions increased, and the decomposition ratio was greater than 81% at 45 ℃ and pH 9.3. This was approximately four times higher than that at pH 8. The result of the precipitation reaction, in view of these two factors that significantly influence the precipitation reaction, was that the precipitation yield increased as the temperature increased. However, the effect of temperature was not significant above 35 ℃. A kinetic study of the precipitation reaction revealed that the activation energy of the reaction was 42.3 kJ/mol. Therefore, considering the solubility of ammonium metavanadate, the lower the temperature, the better the vanadium recovery yield. Additionally, considering the decomposition of ammonium ions, the lower the pH of the aqueous solution, the more advantageous. However, at pH 8 or less, sodium polyvanadate is precipitated and the purity of vanadium oxide may reduce.

Separation of Vanadium and Tungsten from Spent SCR DeNOX Catalyst by Ion-exchange Column (SCR 탈질 폐촉매로부터 이온교환칼럼을 이용한 바나듐과 텅스텐의 분리)

  • Heo, Seo-Jin;Jeon, Jong-Hyuk;Kim, Rina;Kim, Chul-Joo;Chung, Kyeong Woo;Jeon, Ho-Seok;Yoon, Ho-Sung
    • Resources Recycling
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    • v.30 no.4
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    • pp.54-63
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    • 2021
  • Vanadium and tungsten can be obtained by separating/recovering the leaching solution from a spent SCR DeNOX catalyst using the soda roasting-water leaching process. Therefore, in this study, the adsorption/desorption mechanism of vanadium and tungsten in an ion-exchange column was investigated using Lewatit MonoPlus MP 600, a strong basic anion exchange resin. The operating conditions for the separation of vanadium and tungsten in the ion-exchange column was intended to present. By conducting a continuous adsorption experiment in a pH 8.5 solution, the adsorption capacity of vanadium and tungsten was found to be 44.75 and 64.92 mg/(g of resin), respectively, which showed that the adsorption capacity of tungsten was larger than that of vanadium because of the difference in ion charge. Vanadium has a higher affinity for MP 600 than tungsten. Consequently, as the vanadium-containing solution is eluted through the ion exchange resin onto which tungsten is adsorbed, the adsorbed tungsten is exchanged with vanadium and desorbed. A continuous experiment was performed with a solution of vanadium and tungsten prepared at the same concentration as the spent SCR DeNOX catalyst leachate. The adsorption capacity of vanadium was found to be 48.72 mg/(g of resin) and 80% of the supplied vanadium was adsorbed; in contrast, almost no tungsten was adsorbed. Therefore, vanadium and tungsten were separated effectively. The ion exchange resin was treated with 2 M HCl at 15 mL/h, and 97.7% of the vanadium(99% purity) could be desorbed. After desorption, NH4Cl was added to precipitate ammonium polyvanadate at 90℃ and recover 93% of the vanadium.