CN104532002A - Lead-containing glass resourceful treatment method - Google Patents
Lead-containing glass resourceful treatment method Download PDFInfo
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Abstract
Description
技术领域technical field
本发明涉及含铅玻璃的资源化处理方法,属于废弃物资源化处理领域。The invention relates to a resource treatment method for lead-containing glass, and belongs to the field of waste resource treatment.
技术背景technical background
含铅玻璃是指含有二氧化硅等玻璃形成物以及较高含量氧化铅的玻璃。由于其具有良好的光学性能、导电性能、防辐射性能及可加工性能等,被广泛用于制造电真空玻璃、低温封接玻璃、防辐射玻璃、光学玻璃、高折射微珠玻璃及艺术器皿玻璃等产品。阴极射线管(CRT)作为重要的含铅玻璃产品,被广泛地应用在电视机、计算机显示器、示波器等电子电器设备上。CRT玻壳是显示器的重要组成部分,约占总重量的50﹪。CRT玻壳主要分为屏玻璃和锥玻璃,其中锥玻璃含铅量约22~28﹪。目前我国电视机社会保有量约5.5亿台,其中绝大多数为CRT电视机,计算机CRT显示器的保有量也已超过4000万台,并且大量电子电器产品已进入淘汰报废高峰期。产生的大量含铅玻璃如若不进行适当处理处置,直接丢弃不仅造成铅资源的浪费,还会对人体健康和生态环境构成潜在威胁。Leaded glass refers to glass containing glass formers such as silica and a relatively high content of lead oxide. Because of its good optical performance, electrical conductivity, radiation protection performance and processability, etc., it is widely used in the manufacture of electric vacuum glass, low temperature sealing glass, radiation protection glass, optical glass, high refraction bead glass and art utensil glass and other products. Cathode ray tube (CRT), as an important leaded glass product, is widely used in electronic and electrical equipment such as televisions, computer monitors, and oscilloscopes. The CRT glass bulb is an important part of the display, accounting for about 50% of the total weight. CRT glass bulbs are mainly divided into screen glass and cone glass, of which the lead content of cone glass is about 22-28%. At present, there are about 550 million TV sets in my country, the vast majority of which are CRT TV sets, and the number of computer CRT monitors has exceeded 40 million sets, and a large number of electronic and electrical products have entered the peak period of elimination and scrapping. If a large amount of lead-containing glass is not properly disposed of, it will not only cause a waste of lead resources, but also pose a potential threat to human health and the ecological environment.
目前世界各国对于高含铅玻璃均没有良好的处理处置方法。使用废含铅玻璃进行资源化产品开发是可行的,存在的主要问题是资源利用率低,只是将玻璃中的铅从一种产品转移到另一产品中,重金属危害问题未得到彻底解决。目前我国铅的生产原料主要是高品位的方铅矿,由于受资源条件限制,每年需进口大量铅精矿原料,而且铅冶炼一般采用烧结-鼓风炉传统冶炼工艺,生产过程中会产生大量二氧化硫和铅尘,对环境污染严重。因此将废含铅玻璃中的铅提取出来,可能成为今后的研究热点和发展趋势。但是目前铅的提取方法存在一些技术瓶颈和环境问题,难以实现工业化,亟待开发高效、低能、清洁的铅提取工艺。At present, countries all over the world do not have good treatment and disposal methods for high lead-containing glass. It is feasible to use waste lead-containing glass to develop resource-based products. The main problem is that the resource utilization rate is low, and the lead in glass is only transferred from one product to another, and the problem of heavy metal hazards has not been completely resolved. At present, the raw material for lead production in my country is mainly high-grade galena. Due to resource constraints, a large amount of lead concentrate raw materials need to be imported every year, and lead smelting generally adopts the traditional sintering-blast furnace smelting process, which will produce a large amount of sulfur dioxide and Lead dust is a serious environmental pollution. Therefore, extracting lead from waste lead-containing glass may become a research hotspot and development trend in the future. However, there are some technical bottlenecks and environmental problems in the current lead extraction methods, and it is difficult to achieve industrialization. It is urgent to develop an efficient, low-energy, and clean lead extraction process.
2008年,吴国清等人从材料分类识别、材料的无害化处理、材料分离及再利用的角度报道了《含CRT类显示器回收处理技术研究》。同年,海尔集团技术研发中心尹风福等人报道了《废旧显示器的环保处理技术》,以及其合作伙伴青岛新天地研发出了CRT综合利用工艺,建设了相应的处置和回收工厂,但其技术核心限于CRT的拆解和分类,并未涉及从CRT中提取铅进行再利用的工业化生产方法。In 2008, Wu Guoqing and others reported "Research on Recycling Technology of Displays Containing CRT" from the perspectives of material classification and identification, material harmless treatment, material separation and reuse. In the same year, Yin Fengfu of Haier Group Technology R&D Center and others reported "Environmental Protection Treatment Technology of Waste Displays", and its partner Qingdao Xintiandi developed a CRT comprehensive utilization process and built a corresponding disposal and recycling plant, but its technical core is limited to CRT. The dismantling and sorting of CRT does not involve the industrial production method of extracting lead from CRT for reuse.
公开号为CN101613802A的中国专利提供了一种废旧含铅玻璃回收铅同时生产环保建材的工艺与配套设备,能够以废旧含铅玻璃为原材料,采用真空碳热还原工艺回收其中的铅并制备泡沫玻璃。但因该工艺方法步骤短,只能同时回收铅和相应化工产品泡沫玻璃,且该方法需在1000℃下反应数小时,故所需设备要求高、能耗大、污染大,因此不利于工业化生产。The Chinese patent with the publication number CN101613802A provides a process and supporting equipment for recycling lead from waste leaded glass and simultaneously producing environmentally friendly building materials. It can use waste leaded glass as raw material to recover lead in vacuum carbon thermal reduction process and prepare foam glass . However, due to the short steps of this process, only lead and the corresponding chemical product foam glass can be recovered at the same time, and this method needs to be reacted at 1000 ° C for several hours, so the required equipment is high, energy consumption is large, and pollution is large, so it is not conducive to industrialization. Production.
发明内容Contents of the invention
针对以上存在的问题,本发明的目的在于提供含铅玻璃的资源化处理方法,本方法流程短,成本低,能完全利用铅和二氧化硅,铅和二氧化硅回收率高。In view of the above existing problems, the object of the present invention is to provide a method for recycling lead-containing glass. This method has a short process flow, low cost, can fully utilize lead and silicon dioxide, and has a high recovery rate of lead and silicon dioxide.
本发明采用的技术方案如下:含铅玻璃的资源化处理方法,其特征在于,包括以下几个步骤:The technical scheme that the present invention adopts is as follows: the resource processing method of lead-containing glass, it is characterized in that, comprises the following several steps:
1)含铅玻璃的破碎。将含铅玻璃放入球磨机内破碎至粒度为0.1-1.5mm;1) Breakage of leaded glass. Put the leaded glass into the ball mill and crush it to a particle size of 0.1-1.5mm;
2)加碱还原焙烧。将破碎后的含铅玻璃粉末与碳粉和碱混合,然后用水制团造粒,放入高温炉内焙烧,焙烧温度为300-600℃,焙烧时间为2-6小时;2) Alkali reduction roasting. Mix the crushed lead-containing glass powder with carbon powder and alkali, then granulate it with water, put it into a high-temperature furnace for roasting, the roasting temperature is 300-600°C, and the roasting time is 2-6 hours;
3)水洗回收铅。将焙烧后物料加入纯水浆化,焙烧后物料与纯水的质量比为1:5-10,水洗时间1-5小时,水洗温度为70-100℃,水洗后用100-300目滤布过滤,滤渣即为粗铅;3) Wash and recover lead. Add the roasted material to pure water for slurry, the mass ratio of the roasted material to pure water is 1:5-10, the washing time is 1-5 hours, the washing temperature is 70-100°C, and the 100-300 mesh filter cloth is used after washing Filtration, the filter residue is crude lead;
4)二氧化硅的回收。将水洗过滤液加入酸回调pH为0.5-4.5,在70-99℃反应1-5小时,然后过滤,滤渣经过洗涤后焙烧,焙烧时间1-5小时,焙烧温度500-1000℃即可得到二氧化硅。4) Recovery of silica. Add acid to the water-washed filtrate to adjust the pH to 0.5-4.5, react at 70-99°C for 1-5 hours, then filter, wash the filter residue and roast for 1-5 hours at a roasting temperature of 500-1000°C to obtain di silicon oxide.
所述步骤2中含铅玻璃粉末、碳粉、碱的质量比为1:0.5-1.5:0.5-1.0,碱为氢氧化钠、氢氧化钡、氢氧化钾中的至少一种。In the step 2, the mass ratio of lead-containing glass powder, carbon powder, and alkali is 1:0.5-1.5:0.5-1.0, and the alkali is at least one of sodium hydroxide, barium hydroxide, and potassium hydroxide.
所述步骤4中酸为硫酸、盐酸、硝酸、醋酸中的至少一种,酸的浓度为5-10mol/l。In the step 4, the acid is at least one of sulfuric acid, hydrochloric acid, nitric acid and acetic acid, and the concentration of the acid is 5-10mol/l.
所述粗铅经过熔炼-电解精炼得到铅板。The crude lead is obtained through smelting-electrolytic refining to obtain a lead plate.
所述洗涤至洗涤水电导率<200us/cm。The washing is performed until the conductivity of the washing water is less than 200 us/cm.
本发明的原理在于:含铅玻璃是指含有二氧化硅等玻璃形成物以及较高含量氧化铅的玻璃,其铅含量15-30%,主要为氧化铅和二氧化铅,剩余物质主要为二氧化硅,将含铅玻璃破碎后加入碱和碳粉焙烧,碱与二氧化硅形成硅酸盐,破坏了玻璃结构,从而将玻璃网状结构里面包裹的铅的氧化物解离出来,而碳粉在高温下能将铅的氧化物还原成粗铅,再将焙烧物经过水洗,硅酸盐溶解于水,经过过滤滤渣即为粗铅,粗铅在经过熔炼-电解精炼得到高纯度铅板,而硅酸钠加入酸回调pH至酸性得到硅酸沉淀,硅酸经过焙烧脱水得到二氧化硅。The principle of the present invention is that lead-containing glass refers to glass containing glass-formers such as silicon dioxide and glass with relatively high content of lead oxide. The lead content is 15-30%, mainly lead oxide and lead dioxide, and the remaining substances are mainly di Silicon oxide, after crushing the lead-containing glass, adding alkali and carbon powder to roast, the alkali and silicon dioxide form silicate, which destroys the glass structure, thereby dissociating the lead oxide wrapped in the glass network structure, while the carbon The powder can reduce the lead oxide to crude lead at high temperature, and then the roasted product is washed with water, the silicate is dissolved in water, and the filter residue is filtered to become crude lead. The crude lead is smelted-electrolytic refining to obtain high-purity lead plate , and sodium silicate is added with acid to adjust the pH to acidity to obtain silicic acid precipitation, and silicic acid is roasted and dehydrated to obtain silica.
本发明的有益效果是:流程短,成本低,能完全利用铅和二氧化硅,铅和二氧化硅回收率高。The invention has the beneficial effects of short process, low cost, full utilization of lead and silicon dioxide, and high recovery rate of lead and silicon dioxide.
具体实施方式Detailed ways
实施例1Example 1
1)含铅玻璃的破碎。将含铅玻璃放入球磨机内破碎至粒度为1.2mm;1) Breakage of leaded glass. Put the leaded glass into a ball mill and crush it to a particle size of 1.2mm;
2)加碱还原焙烧。将破碎后的含铅玻璃粉末与碳粉和氢氧化钠混合,然后用水制团造粒,含铅玻璃粉末、碳粉、氢氧化钠的质量比为1:1.2:0.8,放入高温炉内焙烧,焙烧温度为550℃,焙烧时间为4小时;2) Alkali reduction roasting. Mix the crushed lead-containing glass powder with carbon powder and sodium hydroxide, and then granulate with water. The mass ratio of lead-containing glass powder, carbon powder and sodium hydroxide is 1:1.2:0.8, and put it into a high-temperature furnace Roasting, the firing temperature is 550°C, and the firing time is 4 hours;
3)水洗回收铅。将焙烧后物料加入纯水浆化,焙烧后物料与纯水的质量比为1:8,水洗时间3小时,水洗温度为95℃,水洗后用250目滤布过滤,滤渣即为粗铅;3) Wash and recover lead. The roasted material is added into pure water to slurry, the mass ratio of the roasted material to pure water is 1:8, the washing time is 3 hours, the washing temperature is 95°C, and after washing, it is filtered with a 250-mesh filter cloth, and the filter residue is crude lead;
4)二氧化硅的回收。将水洗过滤液加入硫酸回调pH为3.5,硫酸的浓度为7.5mol/l。在95℃反应4小时,然后过滤,滤渣经过洗涤后焙烧,洗涤至洗涤水电导率180us/cm,焙烧时间3小时,焙烧温度850℃即可得到二氧化硅。4) Recovery of silica. Add sulfuric acid to the washed filtrate to adjust the pH to 3.5, and the concentration of sulfuric acid is 7.5mol/l. React at 95°C for 4 hours, then filter, wash and roast the filter residue until the conductivity of the washing water is 180us/cm, roast for 3 hours, and roast at a temperature of 850°C to obtain silicon dioxide.
所述粗铅经过熔炼-电解精炼得到铅板。The crude lead is obtained through smelting-electrolytic refining to obtain a lead plate.
最终铅和二氧化硅的回收率分别是99.6%、97.1%。The final recoveries of lead and silica were 99.6%, 97.1%, respectively.
实施例2Example 2
1)含铅玻璃的破碎。将含铅玻璃放入球磨机内破碎至粒度为0.7mm;1) Breakage of leaded glass. Put the leaded glass into the ball mill and crush it to a particle size of 0.7mm;
2)加碱还原焙烧。将破碎后的含铅玻璃粉末与碳粉和氢氧化钾混合,然后用水制团造粒,含铅玻璃粉末、碳粉、氢氧化钾的质量比为1:0.95:0.9,放入高温炉内焙烧,焙烧温度为550℃,焙烧时间为3.5小时;2) Alkali reduction roasting. Mix the crushed lead-containing glass powder with carbon powder and potassium hydroxide, and then granulate with water. The mass ratio of lead-containing glass powder, carbon powder and potassium hydroxide is 1:0.95:0.9, and put it into a high-temperature furnace Roasting, the firing temperature is 550°C, and the firing time is 3.5 hours;
3)水洗回收铅。将焙烧后物料加入纯水浆化,焙烧后物料与纯水的质量比为1:8,水洗时间4小时,水洗温度为100℃,水洗后用200目滤布过滤,滤渣即为粗铅;3) Wash and recover lead. The roasted material is added into pure water for slurrying, the mass ratio of the roasted material to pure water is 1:8, the washing time is 4 hours, the washing temperature is 100°C, and after washing, it is filtered with a 200-mesh filter cloth, and the filter residue is crude lead;
4)二氧化硅的回收。将水洗过滤液加入盐酸回调pH为2.5,盐酸的浓度为8.5mol/l。在97℃反应5小时,然后过滤,滤渣经过洗涤后焙烧,洗涤至洗涤水电导率150us/cm,焙烧时间3小时,焙烧温度850℃即可得到二氧化硅。4) Recovery of silica. Add hydrochloric acid to the washed filtrate to adjust the pH to 2.5, and the concentration of hydrochloric acid is 8.5mol/l. React at 97°C for 5 hours, then filter, wash and roast the filter residue until the conductivity of the washing water is 150us/cm, roast for 3 hours, and roast at a temperature of 850°C to obtain silicon dioxide.
所述粗铅经过熔炼-电解精炼得到铅板。The crude lead is obtained through smelting-electrolytic refining to obtain a lead plate.
最终铅和二氧化硅的回收率分别是99.3%、97.8%。The final recoveries of lead and silica were 99.3%, 97.8%, respectively.
实施例3Example 3
1)含铅玻璃的破碎。将含铅玻璃放入球磨机内破碎至粒度为0.7mm;1) Breakage of leaded glass. Put the leaded glass into the ball mill and crush it to a particle size of 0.7mm;
2)加碱还原焙烧。将破碎后的含铅玻璃粉末与碳粉和氢氧化钾混合,然后用水制团造粒,含铅玻璃粉末、碳粉、氢氧化钾的质量比为1:0.95:0.85,放入高温炉内焙烧,焙烧温度为550℃,焙烧时间为2.5小时;2) Alkali reduction roasting. Mix the crushed lead-containing glass powder with carbon powder and potassium hydroxide, and then granulate with water. The mass ratio of lead-containing glass powder, carbon powder and potassium hydroxide is 1:0.95:0.85, and put it into a high-temperature furnace Roasting, the firing temperature is 550°C, and the firing time is 2.5 hours;
3)水洗回收铅。将焙烧后物料加入纯水浆化,焙烧后物料与纯水的质量比为1:6,水洗时间4小时,水洗温度为90℃,水洗后用250目滤布过滤,滤渣即为粗铅;3) Wash and recover lead. The roasted material is added into pure water to make a slurry, the mass ratio of the roasted material to pure water is 1:6, the washing time is 4 hours, and the washing temperature is 90°C. After washing, filter with a 250-mesh filter cloth, and the filter residue is crude lead;
4)二氧化硅的回收。将水洗过滤液加入盐酸回调pH为2.5,盐酸的浓度为8.5mol/l。在90℃反应4小时,然后过滤,滤渣经过洗涤后焙烧,洗涤至洗涤水电导率150us/cm,焙烧时间3小时,焙烧温度850℃即可得到二氧化硅。4) Recovery of silica. Add hydrochloric acid to the washed filtrate to adjust the pH to 2.5, and the concentration of hydrochloric acid is 8.5mol/l. React at 90°C for 4 hours, then filter, wash and roast the filter residue until the conductivity of the washing water is 150us/cm, roast for 3 hours, and roast at a temperature of 850°C to obtain silicon dioxide.
所述粗铅经过熔炼-电解精炼得到铅板。The crude lead is obtained through smelting-electrolytic refining to obtain a lead plate.
最终铅和二氧化硅的回收率分别是99.5%、98.1%。The final recoveries of lead and silica were 99.5%, 98.1%, respectively.
实施例4Example 4
1)含铅玻璃的破碎。将含铅玻璃放入球磨机内破碎至粒度为0.5mm;1) Breakage of leaded glass. Put the leaded glass into the ball mill and crush it to a particle size of 0.5mm;
2)加碱还原焙烧。将破碎后的含铅玻璃粉末与碳粉和氢氧化钠混合,然后用水制团造粒,含铅玻璃粉末、碳粉、氢氧化钾的质量比为1:0.78:0.9,放入高温炉内焙烧,焙烧温度为450℃,焙烧时间为3.5小时;2) Alkali reduction roasting. Mix the crushed lead-containing glass powder with carbon powder and sodium hydroxide, and then granulate with water. The mass ratio of lead-containing glass powder, carbon powder and potassium hydroxide is 1:0.78:0.9, and put it into a high-temperature furnace Roasting, the calcination temperature is 450°C, and the calcination time is 3.5 hours;
3)水洗回收铅。将焙烧后物料加入纯水浆化,焙烧后物料与纯水的质量比为1:8,水洗时间4小时,水洗温度为85℃,水洗后用200目滤布过滤,滤渣即为粗铅;3) Wash and recover lead. The roasted material is added into pure water for slurrying, the mass ratio of the roasted material to pure water is 1:8, the washing time is 4 hours, and the washing temperature is 85°C. After washing, filter with a 200-mesh filter cloth, and the filter residue is crude lead;
4)二氧化硅的回收。将水洗过滤液加入硝酸回调pH为2.5,硝酸的浓度为8.5mol/l。在97℃反应5小时,然后过滤,滤渣经过洗涤后焙烧,洗涤至洗涤水电导率100us/cm,焙烧时间3小时,焙烧温度950℃即可得到二氧化硅。4) Recovery of silica. Nitric acid is added to the water-washed filtrate to adjust the pH to 2.5, and the concentration of nitric acid is 8.5 mol/l. React at 97°C for 5 hours, then filter, wash the filter residue and then roast until the conductivity of the washing water is 100us/cm, roast for 3 hours, and roast at a temperature of 950°C to obtain silicon dioxide.
所述粗铅经过熔炼-电解精炼得到铅板。The crude lead is obtained through smelting-electrolytic refining to obtain a lead plate.
最终铅和二氧化硅的回收率分别是99.7%、96.8%。The final recoveries of lead and silicon dioxide were 99.7%, 96.8%, respectively.
以上所述仅为本发明的较佳实施例而已,并不用以限制本发明,凡在本发明的精神和原则之内所作的任何修改、等同替换和改进等,均应包含在本发明的保护范围之内。The above descriptions are only preferred embodiments of the present invention, and are not intended to limit the present invention. Any modifications, equivalent replacements and improvements made within the spirit and principles of the present invention should be included in the protection of the present invention. within range.
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Cited By (6)
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CN105112682A (en) * | 2015-07-08 | 2015-12-02 | 东北大学 | Non-noxious treatment method for waste electronic lead-containing glass |
CN108751672A (en) * | 2018-07-25 | 2018-11-06 | 广东新生环保科技股份有限公司 | A kind of flint glass retracting device and its method |
US10184162B2 (en) * | 2016-03-24 | 2019-01-22 | Hellatron S.p.A. | Hydrothermal process for the treatment of lead glass with recovery of lead metal, soluble and insoluble silicates and silica |
US10337114B2 (en) * | 2016-03-24 | 2019-07-02 | E.V.H. S.r.l. | Process for the treatment of end-of-life cathode-ray tubes |
CN112194145A (en) * | 2020-09-23 | 2021-01-08 | 广西大学 | Industrial production and preparation method of ultra-high purity silicon dioxide powder material |
WO2025052815A1 (en) * | 2023-09-08 | 2025-03-13 | Agc株式会社 | Method for producing glass, mixture, dried product, and glass |
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- 2014-11-21 CN CN201410675107.6A patent/CN104532002A/en active Pending
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
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CN105112682A (en) * | 2015-07-08 | 2015-12-02 | 东北大学 | Non-noxious treatment method for waste electronic lead-containing glass |
US10184162B2 (en) * | 2016-03-24 | 2019-01-22 | Hellatron S.p.A. | Hydrothermal process for the treatment of lead glass with recovery of lead metal, soluble and insoluble silicates and silica |
US10337114B2 (en) * | 2016-03-24 | 2019-07-02 | E.V.H. S.r.l. | Process for the treatment of end-of-life cathode-ray tubes |
CN108751672A (en) * | 2018-07-25 | 2018-11-06 | 广东新生环保科技股份有限公司 | A kind of flint glass retracting device and its method |
CN112194145A (en) * | 2020-09-23 | 2021-01-08 | 广西大学 | Industrial production and preparation method of ultra-high purity silicon dioxide powder material |
WO2025052815A1 (en) * | 2023-09-08 | 2025-03-13 | Agc株式会社 | Method for producing glass, mixture, dried product, and glass |
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