Headquarters for Innovative Society-Academic Cooperation, University of Fukui, Bunkyo 3-9-1, Fukui 910-8507, Japan.
Waste Manag. 2013 Aug;33(8):1758-63. doi: 10.1016/j.wasman.2013.04.009. Epub 2013 May 25.
Lead can be recovered from funnel glass of waste cathode ray tubes via reduction melting. While low-temperature melting is necessary for reduced energy consumption, previously proposed methods required high melting temperatures (1400 °C) for the reduction melting. In this study, the reduction melting of the funnel glass was performed at 900-1000 °C using a lab-scale reactor with varying concentrations of Na(2)CO(3) at different melting temperatures and melting times. The optimum Na(2)CO(3) dosage and melting temperature for efficient lead recovery was 0.5 g per 1g of the funnel glass and 1000 °C respectively. By the reduction melting with the mentioned conditions, 92% of the lead in the funnel glass was recovered in 60 min. However, further lead recovery was difficult because the rate of the lead recovery decreased as with the recovery of increasing quantity of the lead from the glass. Thus, the lead remaining in the glass after the reduction melting was extracted with 1M HCl, and the lead recovery improved to 98%.
可以通过还原熔炼从废阴极射线管的漏斗玻璃中回收铅。虽然低温熔炼对于降低能耗是必要的,但以前提出的方法需要高温(1400°C)进行还原熔炼。在这项研究中,使用带有不同浓度的 Na(2)CO(3)的实验室规模反应器,在不同的熔炼温度和时间下,在 900-1000°C 下进行了漏斗玻璃的还原熔炼。对于高效的铅回收,最佳的 Na(2)CO(3)用量和熔炼温度分别为每 1g 漏斗玻璃 0.5g 和 1000°C。在提到的条件下进行还原熔炼,60 分钟内可回收 92%的漏斗玻璃中的铅。然而,由于随着玻璃中铅的回收量增加,铅的回收率降低,因此进一步回收铅变得困难。因此,用 1M HCl 提取还原熔炼后的玻璃中的剩余铅,铅的回收率提高到 98%。