CN114380344A - A kind of preparation method of alumina modified soda lime glass microbead filter material - Google Patents

A kind of preparation method of alumina modified soda lime glass microbead filter material Download PDF

Info

Publication number
CN114380344A
CN114380344A CN202011134704.XA CN202011134704A CN114380344A CN 114380344 A CN114380344 A CN 114380344A CN 202011134704 A CN202011134704 A CN 202011134704A CN 114380344 A CN114380344 A CN 114380344A
Authority
CN
China
Prior art keywords
soda
lime glass
filter material
solution
alumina
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.)
Pending
Application number
CN202011134704.XA
Other languages
Chinese (zh)
Inventor
孟玉杰
赵鹏
郝晨捷
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.)
Tianjin University
Original Assignee
Tianjin University
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 Tianjin University filed Critical Tianjin University
Priority to CN202011134704.XA priority Critical patent/CN114380344A/en
Publication of CN114380344A publication Critical patent/CN114380344A/en
Pending legal-status Critical Current

Links

Images

Classifications

    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/001Processes for the treatment of water whereby the filtration technique is of importance
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/28Treatment of water, waste water, or sewage by sorption
    • C02F1/281Treatment of water, waste water, or sewage by sorption using inorganic sorbents

Landscapes

  • Chemical & Material Sciences (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Organic Chemistry (AREA)
  • Inorganic Chemistry (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

The invention discloses a preparation method of an alumina modified soda-lime glass bead filter material, which comprises the following steps: screening the obtained soda-lime glass microsphere raw material by a screen with a specific mesh number, sequentially and repeatedly cleaning the raw material by using deionized water, ethanol and acetone, and then carrying out acid washing by using a human-eating acid solution to remove organic impurities on the surface; adding an aluminum chloride solution and a sodium hydroxide solution, baking the mixture in an oven for 24 hours, and putting the baked mixture into a muffle furnace for high-temperature calcination to obtain the modified soda-lime-glass bead filter material attached with the alumina, wherein the modified soda-lime-glass bead filter material has better removal effect on negative electric pollutants such as micro-plastics and escherichia coli in water. The alumina modified soda-lime glass bead filter material obtained by the invention is more convenient in approach and cheaper in price, is more beneficial to removing micro-plastics in water, and can improve the treatment efficiency of the filter and the quality of the effluent.

Description

一种氧化铝改性钠钙玻璃微珠滤料的制备方法A kind of preparation method of alumina modified soda lime glass microbead filter material

技术领域technical field

本发明属于环保材料制备及饮用水处理领域,更具体的说,是涉及一种氧化铝改性钠钙玻璃微珠滤料的制备方法。The invention belongs to the field of environmental protection material preparation and drinking water treatment, and in particular relates to a preparation method of an alumina modified soda lime glass microbead filter material.

背景技术Background technique

在水饮用水净化与废水处理的工业流程中,过滤工艺的好坏往往决定了一个水厂的处理效率与出水品质。过滤,一般是指以石英砂等粒状滤料层截留水中杂质,从而使水变得澄清的工艺流程。过滤不仅能去除水中的悬浮物从而降低浊度,还能降低BOD、COD、重金属离子及油脂。近年来水质性缺水状况日益严重,且水质标准日益提升,传统石英砂滤料在使用过程中逐渐暴露出本身所固有的一些缺陷,例如表面带负电、表面空隙少、比表面积小、孔隙率小等。其次,国家对节能减排、绿色循环可持续经济的发展以及环境治理要求的的逐步提高,而石英砂滤料的开采和加工属于高污染行业,导致近年来石英砂的价格也在不断攀升。因此,传统的石英砂生产加工工艺已经不能满足现阶段的节能减排要求。In the industrial process of drinking water purification and wastewater treatment, the quality of the filtration process often determines the treatment efficiency and effluent quality of a water plant. Filtration generally refers to the process of retaining water impurities with a granular filter material layer such as quartz sand, thereby making the water clarified. Filtration can not only remove suspended solids in water to reduce turbidity, but also reduce BOD, COD, heavy metal ions and grease. In recent years, the water quality shortage has become more and more serious, and the water quality standards have been improved. The traditional quartz sand filter gradually exposed some inherent defects in the use process, such as negative surface charge, less surface voids, small specific surface area, and porosity. Small wait. Secondly, the country has gradually increased the requirements for energy conservation and emission reduction, the development of green circular sustainable economy and environmental governance, and the mining and processing of quartz sand filter materials are highly polluting industries, resulting in the price of quartz sand has been rising in recent years. Therefore, the traditional production and processing technology of quartz sand can no longer meet the requirements of energy saving and emission reduction at this stage.

另一方面,微塑料作为一种新型污染物,广泛分布在自然环境中。自美国研究人员在瓶装水中发现微塑料之后,2018年10月22日欧洲联合肠胃病学周的学会上发布最新研究,首次确认人体内发现了多达9种不同种类的微塑料,由此世界范围内社会各界开始集中关注微塑料问题,2019年世界卫生组织发表了名为《饮用水中的微塑料》的报告。传统的水处理工艺能够处理70%以上的大粒径微塑料,而过滤环节发挥着不可取代的作用。但无论是石英砂滤料,或者无烟煤、陶瓷等其它类型的滤料,其zeta电位都为负值,而微塑料的zeta电位也为负值,由于电性相同,在过滤过程中对于粒径特别小的微塑料很难起到截留的作用。而除微塑料以外,其他常见的污染物如细菌、抗生素、油脂等大部分物质的zeta电位亦为负值。根据DLVO理论,当提高滤料的zeta电位时,更有利于在过滤过程中吸附水中的污染物,从而提高出水水质。On the other hand, as a new type of pollutant, microplastics are widely distributed in the natural environment. Since American researchers found microplastics in bottled water, the latest research released at the Society of the European Joint Gastroenterology Week on October 22, 2018 confirmed for the first time that as many as 9 different types of microplastics have been found in the human body. In 2019, the World Health Organization published a report titled "Microplastics in Drinking Water". The traditional water treatment process can process more than 70% of the large-sized microplastics, and the filtration process plays an irreplaceable role. However, whether it is quartz sand filter media, or other types of filter media such as anthracite, ceramics, etc., the zeta potential is negative, and the zeta potential of microplastics is also negative. Very small microplastics are difficult to retain. In addition to microplastics, the zeta potential of most other common pollutants such as bacteria, antibiotics, and oils is also negative. According to the DLVO theory, when the zeta potential of the filter material is increased, it is more conducive to adsorb pollutants in the water during the filtration process, thereby improving the quality of the effluent.

发明内容SUMMARY OF THE INVENTION

本发明的目的是为了克服现有技术中的不足,针对现有过滤技术中传统石英砂滤料表面带负电、表面空隙少、比表面积小、孔隙率小的缺陷,以及使用成本逐年增加的现状,提出一种氧化铝改性钠钙玻璃微珠滤料的制备方法,采用此方法获取氧化铝改性钠钙玻璃微珠滤料途径更加方便,价格更加便宜,更有利于去除水中微塑料,能够提升滤池的处理效率,提高出水水质。The purpose of the present invention is to overcome the deficiencies in the prior art, aiming at the defects of negative charge on the surface of the traditional quartz sand filter material, few surface voids, small specific surface area and small porosity in the existing filtration technology, and the current situation that the use cost increases year by year. , proposes a preparation method of alumina-modified soda-lime glass microbead filter material. Using this method to obtain alumina-modified soda-lime glass microbead filter material is more convenient, cheaper, and more conducive to removing microplastics in water. It can improve the treatment efficiency of the filter tank and improve the effluent quality.

本发明的目的是通过以下技术方案实现的。The object of the present invention is achieved through the following technical solutions.

本发明氧化铝改性钠钙玻璃微珠滤料的制备方法,将钠钙玻璃微珠原料,经过表面预处理清洁之后,将氧化铝附着在表面,实现钠钙玻璃微珠滤料的带电功能化,从而制成特定目数的改性钠钙玻璃微珠滤料。The preparation method of the alumina-modified soda-lime glass microbead filter material of the invention comprises the following steps: after the soda-lime glass microbead raw material is subjected to surface pretreatment and cleaning, the alumina is attached to the surface to realize the charging function of the soda-lime glass microbead filter material. The modified soda-lime glass microbead filter material of specific mesh is made.

具体包括以下步骤:Specifically include the following steps:

(1)钠钙玻璃微珠表面预处理(1) Surface pretreatment of soda lime glass beads

通过特定目数的筛网筛选出一定量的钠钙玻璃微珠原料,使用优级纯的无水乙醇反复清洗上述原料5-6次;将清洗好的钠钙玻璃微珠原料依次放入盛有去离子水、乙醇、丙酮的烧杯中各超声10min;将经过超声清洗的玻璃微珠原料放入“食人酸”溶液,然后在95℃下水浴酸洗2小时;水浴酸洗完成之后用去离子水将玻璃微珠上残留的酸液反复冲洗干净,之后放入无水乙醇中保存备用;A certain amount of soda-lime glass microbead raw materials are screened through a screen with a specific mesh number, and the above-mentioned raw materials are repeatedly washed with excellent grade pure anhydrous ethanol for 5-6 times; Ultrasonic for 10min each in a beaker with deionized water, ethanol, and acetone; put the raw glass beads cleaned by ultrasonic into the "cannibal acid" solution, and then pickled in a water bath at 95°C for 2 hours; The acid solution remaining on the glass beads was repeatedly rinsed with deionized water, and then placed in anhydrous ethanol for future use;

(2)钠钙玻璃微珠改性处理(2) Modification of soda lime glass beads

称取步骤(1)预处理后的钠钙玻璃微珠,放入烘箱中烘干备用;配置足量氯化铝溶液与氢氧化钠溶液,加入钠钙玻璃微珠中搅拌均匀,再次放入烘箱烘24小时;为确保滤料受热均匀,在加热前期每隔一小时搅拌一次,加热24小时后取出滤料;重复上述操作一次;最后,向滤料加入氯化铝溶液和氢氧化钠溶液,搅拌均匀;之后,置入马弗炉中,烘制一定时间后取出;待滤料冷却后,用自来水冲洗,以去除表面粘附不牢的涂层物;用蒸馏水冲洗三遍,烘干待用,得到氧化铝改性钠钙玻璃微珠滤料。Weigh the pretreated soda-lime glass beads in step (1), put them into an oven to dry for later use; configure a sufficient amount of aluminum chloride solution and sodium hydroxide solution, add them into the soda-lime glass beads, stir evenly, and put them in again. Bake in an oven for 24 hours; in order to ensure that the filter material is heated evenly, stir every one hour in the early stage of heating, and take out the filter material after 24 hours of heating; repeat the above operation once; finally, add aluminum chloride solution and sodium hydroxide solution to the filter material , stir evenly; after that, put it in the muffle furnace, and take it out after baking for a certain period of time; after the filter material is cooled, rinse it with tap water to remove the coating that is not firmly adhered to the surface; rinse it with distilled water three times, and dry it. Standby to obtain alumina-modified soda-lime glass microbead filter material.

步骤(1)中所述钠钙玻璃微珠的粒径为20-40目,所述无水乙醇的体积分数为99.8%,所述丙酮的体积分数为99.5%,所述“食人酸”溶液由浓硫酸和双氧水构成,浓硫酸和双氧水的体积比为7:3。In step (1), the particle size of the soda-lime glass microbeads is 20-40 mesh, the volume fraction of the absolute ethanol is 99.8%, the volume fraction of the acetone is 99.5%, and the "cannibal acid" The solution is composed of concentrated sulfuric acid and hydrogen peroxide, and the volume ratio of concentrated sulfuric acid and hydrogen peroxide is 7:3.

步骤(2)中氯化铝溶液的浓度为3mol/L,氢氧化钠溶液的浓度为10mol/L,氯化铝溶液和氢氧化钠溶液的用量比例为20:1;预处理后的钠钙玻璃微珠放入50℃烘箱中烘干备用,氯化铝溶液与氢氧化钠溶液,加入氯化铝溶液与氢氧化钠溶液搅拌均匀后的钠钙玻璃微珠放入100℃-120℃烘箱烘24小时,马弗炉温度设置240℃-550℃。In step (2), the concentration of aluminum chloride solution is 3mol/L, the concentration of sodium hydroxide solution is 10mol/L, and the consumption ratio of aluminum chloride solution and sodium hydroxide solution is 20:1; Put the glass microbeads into a 50°C drying oven for later use, add aluminum chloride solution and sodium hydroxide solution, add aluminum chloride solution and sodium hydroxide solution and stir the soda-lime glass microbeads into a 100°C-120°C oven Bake for 24 hours, and set the muffle furnace temperature to 240°C-550°C.

与现有技术相比,本发明的技术方案所带来的有益效果是:Compared with the prior art, the beneficial effects brought by the technical solution of the present invention are:

本发明实现了表面正电吸附点位附着以及滤料粒径的精确控制。与传统石英砂滤料相比,滤料价格更加低廉,表面孔隙和沟壑较少,且由于其表面的正电吸附点位,根据DLVO理论,此种滤料在保持原有过滤性能的同时能有效去除水中微塑料及其它负电污染物,兼具经济价值和环保意义。The invention realizes the attachment of the surface positive electro-adsorption point and the precise control of the particle size of the filter material. Compared with the traditional quartz sand filter material, the price of the filter material is lower, the surface pores and ravines are less, and due to the positive adsorption points on its surface, according to the DLVO theory, this filter material can maintain the original filtration performance while maintaining the original filter performance. Effectively remove microplastics and other negatively charged pollutants in water, which has both economic value and environmental protection significance.

附图说明Description of drawings

图1是本发明实施例1步骤二中钠钙玻璃微珠氧化铝改性后的SEM图片;Fig. 1 is the SEM picture after modification of soda-lime glass microbead alumina in step 2 of Example 1 of the present invention;

图2是本发明实施例1步骤二中钠钙玻璃微珠氧化铝改性后的能谱图片;Fig. 2 is the energy spectrum picture after modification of soda lime glass microbead alumina in step 2 of Example 1 of the present invention;

图3是本发明实施例1步骤二中钠钙玻璃微珠氧化铝改性后的zeta电位测试结果。Fig. 3 is the test result of zeta potential after modification of alumina of soda lime glass microbeads in step 2 of Example 1 of the present invention.

具体实施方式Detailed ways

下面结合附图和实施例对本发明作进一步的描述。提供该实施例是为了更好的理解,绝不是为了限制本发明。The present invention will be further described below with reference to the accompanying drawings and embodiments. This example is provided for better understanding and is by no means intended to limit the present invention.

本发明氧化铝改性钠钙玻璃微珠滤料的制备方法,通过大量的实验探究,将钠钙玻璃微珠原料,经过表面预处理清洁之后,将氧化铝附着在表面,实现钠钙玻璃微珠滤料的带电功能化,从而成功制成特定目数的在表面附着氧化铝吸附位点的改性钠钙玻璃微珠滤料。具体包括以下步骤:The preparation method of the alumina-modified soda-lime glass microbead filter material of the present invention is based on a large number of experiments. The charged functionalization of the bead filter material has successfully made the modified soda-lime glass microbead filter material with a specific mesh number of alumina adsorption sites attached to the surface. Specifically include the following steps:

步骤一,钠钙玻璃微珠表面预处理Step 1, Soda-lime glass microbead surface pretreatment

通过特定目数的筛网筛选出一定量的钠钙玻璃微珠原料,使用优级纯(GR)的无水乙醇反复清洗上述原料5-6次;将清洗好的钠钙玻璃微珠原料依次放入盛有去离子水、乙醇、丙酮的烧杯中各超声10min;将经过超声清洗的玻璃微珠原料放入“食人酸”溶液,然后在95℃下水浴酸洗2小时;水浴酸洗完成之后用去离子水将玻璃微珠上残留的酸液反复冲洗干净,之后放入无水乙醇中保存备用。该步骤的主要目的是清洗掉钠钙玻璃微珠表面的有机杂质。A certain amount of soda-lime glass microbead raw materials are screened through a screen with a specific mesh number, and the above-mentioned raw materials are repeatedly washed 5-6 times with excellent grade pure (GR) absolute ethanol; the cleaned soda-lime glass microbead raw materials are sequentially Put it into a beaker containing deionized water, ethanol, and acetone and sonicate for 10 minutes each; put the ultrasonically cleaned glass microbead raw material into the "cannibal acid" solution, and then pickle it in a water bath for 2 hours at 95 °C; pickle it in a water bath After completion, the residual acid solution on the glass microbeads was repeatedly rinsed with deionized water, and then placed in absolute ethanol for future use. The main purpose of this step is to wash away the organic impurities on the surface of the soda lime glass microbeads.

其中,采用从厂家购得的廉价钠钙玻璃微珠作为原材料,粒径范围在20目至40目之间,堆积体积为200ml,根据实验需求使用均质玻璃微珠或非均质玻璃微珠,并采用无水乙醇对酸洗后的钠钙玻璃微珠原料进行保存,尽可能隔绝空气中的杂质对玻璃珠表面电位可能带来的影响。所述无水乙醇的体积分数为99.8%,所述丙酮的体积分数为99.5%,所述“食人酸”溶液由浓硫酸和双氧水构成,浓硫酸和双氧水的体积比为7:3。Among them, the cheap soda-lime glass microbeads purchased from the manufacturer were used as raw materials, the particle size ranged from 20 mesh to 40 mesh, and the stacking volume was 200ml. Homogeneous glass microbeads or heterogeneous glass microbeads were used according to the experimental requirements , and use absolute ethanol to preserve the raw material of soda-lime glass microbeads after pickling, so as to isolate the possible influence of impurities in the air on the surface potential of glass beads as much as possible. The volume fraction of the absolute ethanol is 99.8%, the volume fraction of the acetone is 99.5%, and the "cannibal acid" solution is composed of concentrated sulfuric acid and hydrogen peroxide, and the volume ratio of concentrated sulfuric acid and hydrogen peroxide is 7:3.

步骤二,钠钙玻璃微珠改性处理Step 2, Soda-lime glass microbead modification treatment

称取步骤一预处理后的钠钙玻璃微珠,放入50℃烘箱中烘干备用;配置足量氯化铝(AlCl3)溶液与氢氧化钠(NaOH)溶液,加入钠钙玻璃微珠中搅拌均匀,再次放入100℃-120℃烘箱烘24小时;为确保滤料受热均匀,在加热前期每隔一小时搅拌一次,加热24小时后取出滤料;重复上述操作一次;最后,向滤料加入氯化铝(AlCl3)溶液和氢氧化钠(NaOH)溶液,搅拌均匀;之后,置入马弗炉中240℃-550℃烘制一定时间(6-12h)后取出;待滤料冷却后,用自来水缓慢冲洗,以去除表面粘附不牢的涂层物;用蒸馏水冲洗三遍,烘干待用,得到氧化铝改性钠钙玻璃微珠滤料。Weigh the pretreated soda-lime glass beads in step 1, put them into a 50°C oven to dry for later use; configure a sufficient amount of aluminum chloride (AlCl 3 ) solution and sodium hydroxide (NaOH) solution, add soda-lime glass beads Stir evenly, put it into the oven at 100°C-120°C again for 24 hours; in order to ensure that the filter material is heated evenly, stir it every one hour in the early stage of heating, and take out the filter material after 24 hours of heating; repeat the above operation once; Add aluminum chloride (AlCl 3 ) solution and sodium hydroxide (NaOH) solution to the filter material, stir evenly; after that, put it in a muffle furnace at 240°C-550°C and bake for a certain period of time (6-12h), then take out; to be filtered After the material is cooled, it is slowly rinsed with tap water to remove the coating that is not firmly adhered to the surface; rinsed three times with distilled water, and dried for use to obtain alumina-modified soda-lime glass microbead filter material.

其中,氯化铝溶液的浓度为3mol/L,氢氧化钠溶液的浓度为10mol/L,氯化铝溶液和氢氧化钠溶液的用量比例为20:1,其目的在于当氢氧化钠(NaOH)溶液少量时,氯化铝(AlCl3)与氢氧化钠(NaOH)发生如下化学反应:AlCl3+3NaOH=3NaCl+Al(OH)3↓。之后在高温环境下发生2Al(OH)3=Al2O3+3H2O的反应,从而实现氧化铝在钠钙玻璃微珠表面的附着。而当氢氧化钠(NaOH)溶液过量时,无法正常生成氢氧化铝沉淀,而是发生AlCl3+4NaOH=3NaCl+NaAlO2+2H2O的反应,不利于之后高温环境下氧化铝的生成与附着。氧化铝在中性水环境中的zeta电位为正值,而钠钙玻璃微珠在中性水环境中的zeta电位为负值,当氧化铝附着在钠钙玻璃微珠表面之后,在负电位的玻璃微珠表面构建正电位的吸附电位,从而提高对负电污染物的吸附效果。Wherein, the concentration of aluminum chloride solution is 3mol/L, the concentration of sodium hydroxide solution is 10mol/L, and the consumption ratio of aluminum chloride solution and sodium hydroxide solution is 20:1, and its purpose is to act as sodium hydroxide (NaOH) ) solution, the following chemical reaction occurs between aluminum chloride (AlCl 3 ) and sodium hydroxide (NaOH): AlCl 3 +3NaOH=3NaCl+Al(OH) 3 ↓. Then, the reaction of 2Al(OH) 3 =Al 2 O 3 +3H 2 O occurs in a high temperature environment, so as to realize the adhesion of alumina on the surface of soda-lime glass microbeads. When the sodium hydroxide (NaOH) solution is excessive, the aluminum hydroxide precipitation cannot be formed normally, but the reaction of AlCl 3 +4NaOH=3NaCl+NaAlO 2 +2H2O occurs, which is not conducive to the formation and adhesion of alumina in the subsequent high temperature environment. The zeta potential of alumina in neutral water environment is positive, while the zeta potential of soda-lime glass beads in neutral water environment is negative. The surface of the glass microbeads builds a positive adsorption potential, thereby improving the adsorption effect of negatively charged pollutants.

通过本发明方法制备氧化铝改性钠钙玻璃微珠滤料后,使用SEM及能谱分析进行表征,从而验证氧化铝是否附着在钠钙玻璃微珠表面,并使用CADzeta电位仪对改性前后的钠钙玻璃微珠滤料进行zeta电位的测定,观察滤料表面电位性质的变化。After the alumina-modified soda-lime glass microbead filter material is prepared by the method of the present invention, it is characterized by SEM and energy spectrum analysis, so as to verify whether the alumina is attached to the surface of the soda-lime glass microbeads. The zeta potential of the soda lime glass microbead filter material was measured, and the change of the surface potential properties of the filter material was observed.

(1)使用SEM及能谱分析测定改性钠钙玻璃微珠表面成分。(1) The surface composition of modified soda-lime glass microbeads was determined by SEM and energy spectrum analysis.

取步骤二改性处理后的钠钙玻璃微珠滤料,喷金制样,放入槽中,抽真空,调节电压、对比度与亮度,使用扫描电子显微镜寻找合适区域进行拍照,X射线进行普通能谱扫描,采用X射线能谱分析检测方法分析获取组成样品材料的各种元素的浓度。其中,真空达到5*10-3Pa,进行点扫描时电压要达到20kv。Take the modified soda-lime glass microbead filter material in step 2, spray gold to prepare samples, put it into the tank, vacuumize, adjust the voltage, contrast and brightness, use a scanning electron microscope to find a suitable area to take pictures, and X-ray for ordinary Energy spectrum scanning, using X-ray energy spectrum analysis and detection method to analyze and obtain the concentration of various elements that make up the sample material. Among them, the vacuum should reach 5*10 -3 Pa, and the voltage should reach 20kv during point scanning.

扫描电子显微镜(Scanning Electron Micrograph,简称SEM),利用二次电子信号成像来观察样品的表面形态,也就是用极狭窄的电子束去扫描样品,通过电子束与样品的相互作用产生各种效应,二次电子能够产生样品表面放大的形貌。这个像是在样品被扫描时按时序建立起来的,即用逐点成像的方法获得放大的图像。电子显微技术最常用的方法就是X射线能谱分析检测(X-ray Energy Dispersive Spectrum,简称EDS)。该方法具有成分分析功能。首先通过自动定性分析鉴别样品中所含的元素,再通过半定量分析,利用X射线强度获取组成样品材料的各种元素的浓度。Scanning Electron Micrograph (SEM) uses secondary electron signal imaging to observe the surface morphology of the sample, that is, to scan the sample with a very narrow electron beam, and produce various effects through the interaction between the electron beam and the sample. Secondary electrons can produce an enlarged topography of the sample surface. This image is established in chronological order as the sample is scanned, ie a magnified image is obtained by point-by-point imaging. The most commonly used method of electron microscopy is X-ray Energy Dispersive Spectrum (EDS). The method has a component analysis function. First, the elements contained in the sample are identified by automatic qualitative analysis, and then the concentration of various elements that make up the sample material is obtained by using the X-ray intensity by semi-quantitative analysis.

(2)使用ZetaCAD固体表面Zeta电位分析仪测定改性前后滤料的zeta电位。(2) Zeta potential of filter media before and after modification was measured by ZetaCAD solid surface Zeta potential analyzer.

取适量步骤一预处理后的钠钙玻璃微珠滤料样品,装入zetaCAD样品填充柱中,通入氯化钠电解液,在加入混合磷酸盐溶液,控制ph为7,此时读取改性前钠钙玻璃微珠滤料的zeta电位。Take an appropriate amount of the soda-lime glass microbead filter material sample pretreated in step 1, put it into the zetaCAD sample packing column, pass sodium chloride electrolyte, add mixed phosphate solution, control the pH to 7, and read the change at this time. Zeta potential of soda-lime glass microbead filter media before sex.

同理,取适量步骤二处理后的改性钠钙玻璃微珠滤料样品,装入zetaCAD样品填充柱中,通入氯化钠电解液,在加入混合磷酸盐溶液,控制ph为7,此时读取改性后钠钙玻璃微珠滤料的zeta电位。In the same way, take an appropriate amount of modified soda-lime glass microbead filter material samples treated in step 2, put them into the zetaCAD sample packed column, pass sodium chloride electrolyte, add mixed phosphate solution, and control the pH to be 7. When reading the zeta potential of the modified soda-lime glass microbead filter material.

其中,所述样品填充柱的规格为直径1.45cm、长度1.8cm,所述氯化钠电解液的浓度0.019mol/L,其电导率为2.67mS/cm,所述混合磷酸盐溶液的浓度为0.025mol/L,导致其电导率上升至3.4mS/cm。改性前后的钠钙玻璃微珠都不具有导电性,需要通过喷金制样增强样品导电性,从而提高SEM的拍摄效果。Wherein, the specifications of the sample packed column are 1.45cm in diameter and 1.8cm in length, the concentration of the sodium chloride electrolyte is 0.019mol/L, the conductivity is 2.67mS/cm, and the concentration of the mixed phosphate solution is 0.025mol/L, resulting in its conductivity rising to 3.4mS/cm. The soda-lime glass microbeads before and after modification do not have conductivity, and it is necessary to enhance the conductivity of the sample by spraying gold to improve the SEM photographing effect.

ZetaCAD固体表面Zeta电位分析仪是直接测定流动电位/流动电流的Zeta电位分析仪,帮助科研人眼在化学于材料科学领域内改善和调整表面特征。适用于沉积的大颗粒、纤维、和平坦的表面,或在一个压力梯度下电解液科研透过的曲面胶或中空纤维样品,包括聚合物、纺织、陶瓷、玻璃等,对不同形状和尺寸的固体及粉末材料均适用。ZetaCAD Solid Surface Zeta Potential Analyzer is a Zeta Potential Analyzer that directly measures flowing potential/flowing current, helping researchers improve and adjust surface features in the fields of chemistry and materials science. Suitable for deposition of large particles, fibers, and flat surfaces, or curved glue or hollow fiber samples through electrolyte research under a pressure gradient, including polymers, textiles, ceramics, glass, etc. Both solid and powder materials are suitable.

实施例1:Example 1:

步骤一:使用30-32目筛网筛选出堆积体积为200ml的钠钙玻璃微珠,使用优级纯(GR)99.8%的无水乙醇反复清洗上述原料5-6次;将清洗好的钠钙玻璃微珠原料依次放入盛有去离子水、乙醇、丙酮的烧杯中各超声10min;将经过超声清洗的玻璃微珠原料放入“食人酸”溶液(浓硫酸和双氧水的体积比为7:3),然后在95℃下水浴酸洗2小时;水浴酸洗完成之后用去离子水将玻璃微珠上残留的酸液反复冲洗干净,之后放入无水乙醇中保存备用。Step 1: Use a 30-32 mesh screen to screen out soda-lime glass microbeads with a stacking volume of 200ml, and use the excellent grade pure (GR) 99.8% absolute ethanol to repeatedly wash the above raw materials 5-6 times; The raw materials of calcium glass microbeads are placed in a beaker containing deionized water, ethanol and acetone in turn for 10 minutes each; 7:3), and then pickled in a water bath for 2 hours at 95°C; after the pickling in a water bath, the residual acid solution on the glass beads was repeatedly rinsed with deionized water, and then placed in anhydrous ethanol for later use.

步骤二:称取30g预处理后的钠钙玻璃微珠,放入烘箱(50℃)中烘干备用;配置氯化铝(AlCl3)溶液3mol/L,氢氧化钠(NaOH)溶液10mol/L,加入钠钙玻璃微珠中搅拌均匀,再次放入烘箱(100℃)烘24小时;为确保滤料受热均匀,在加热前期每个一小时搅拌一次,加热24小时后取出滤料;重复上述操作一次;最后,向滤料加入适量氯化铝(AlCl3)溶液和氢氧化钠(NaOH)溶液,用量比例为20:1,搅拌均匀;之后,置入240℃马弗炉中,烘制6小时后取出;待滤料冷却后,用自来水缓慢冲洗,以去除表面粘附不牢的涂层物;用蒸馏水冲洗三遍,烘干待用,得到氧化铝改性钠钙玻璃微珠滤料。Step 2: Weigh 30 g of pretreated soda-lime glass microbeads, put them in an oven (50° C.) to dry for later use; configure aluminum chloride (AlCl 3 ) solution 3mol/L, sodium hydroxide (NaOH) solution 10mol/L L, add soda-lime glass microbeads and stir evenly, then put it into the oven (100°C) again to bake for 24 hours; in order to ensure that the filter material is heated evenly, stir once every hour in the early stage of heating, and take out the filter material after heating for 24 hours; repeat The above operation was performed once; finally, an appropriate amount of aluminum chloride (AlCl 3 ) solution and sodium hydroxide (NaOH) solution were added to the filter material, and the dosage ratio was 20:1, and stirred evenly; Take it out after 6 hours of preparation; after the filter material is cooled, slowly rinse with tap water to remove the coating that is not firmly adhered to the surface; rinse with distilled water three times, and dry for use to obtain alumina-modified soda-lime glass beads filter material.

步骤三:取适量步骤二处理后的样品,喷金制样,放入槽中,抽真空达到5*10-3Pa,调节电压达到20kv、对比度与亮度,使用扫描电子显微镜寻找合适区域进行拍照,如图1所示,X射线进行普通能谱扫描,采用X射线能谱分析检测方法分析获取组成样品材料的各种元素的浓度,如图2所示。Step 3: Take an appropriate amount of the sample processed in Step 2, spray gold to prepare the sample, put it into the tank, vacuumize to 5*10 -3 Pa, adjust the voltage to 20kv, contrast and brightness, and use a scanning electron microscope to find a suitable area to take pictures , as shown in Figure 1, X-rays are scanned by ordinary energy spectrum, and the concentration of various elements that make up the sample material is obtained by using the X-ray energy spectrum analysis and detection method, as shown in Figure 2.

步骤四:取适量步骤二处理后的样品,直接填充至1.45cm直径和长度约1.8cm的柱子,通入氯化钠电解液,电解溶液为质量分数为0.13%NaCl(0.019mol/L),其初始电导率2.67mS/cm。因需要控制pH值为7之间,加入混合磷酸盐(0.025mol/L)导致其电导率上升至3.4mS/cm,此时读取改性后钠钙玻璃微珠滤料的zeta电位,如图3所示。Step 4: Take an appropriate amount of the sample processed in step 2, directly fill it into a column with a diameter of 1.45cm and a length of about 1.8cm, and pass into the sodium chloride electrolyte, and the electrolyte solution is a mass fraction of 0.13%NaCl (0.019mol/L), Its initial conductivity is 2.67mS/cm. Due to the need to control the pH value between 7, adding mixed phosphate (0.025mol/L) causes its conductivity to rise to 3.4mS/cm, and then read the zeta potential of the modified soda-lime glass microbead filter material, such as shown in Figure 3.

实施例2:Example 2:

步骤一:使用20-22目筛网筛选出堆积体积为200ml的钠钙玻璃微珠,使用优级纯(GR)99.8%的无水乙醇反复清洗上述原料5-6次;将清洗好的钠钙玻璃微珠原料依次放入盛有去离子水、乙醇、丙酮的烧杯中各超声10min;将经过超声清洗的玻璃微珠原料放入“食人酸”溶液(浓硫酸和双氧水的体积比为7:3),然后在95℃下水浴酸洗2小时;水浴酸洗完成之后用去离子水将玻璃微珠上残留的酸液反复冲洗干净,之后放入无水乙醇中保存备用。Step 1: Use a 20-22 mesh screen to screen out soda-lime glass microbeads with a stacking volume of 200ml, and use the excellent grade pure (GR) 99.8% absolute ethanol to repeatedly wash the above raw materials for 5-6 times; The raw materials of calcium glass microbeads are placed in a beaker containing deionized water, ethanol and acetone in turn for 10 minutes each; 7:3), and then pickled in a water bath for 2 hours at 95°C; after the pickling in a water bath, the residual acid solution on the glass beads was repeatedly rinsed with deionized water, and then placed in anhydrous ethanol for later use.

步骤二:称取30g预处理后的钠钙玻璃微珠,放入烘箱(50℃)中烘干备用;配置氯化铝(AlCl3)溶液3mol/L,氢氧化钠(NaOH)溶液10mol/L,加入钠钙玻璃微珠中搅拌均匀,再次放入烘箱(110℃)烘24小时;为确保滤料受热均匀,在加热前期每个一小时搅拌一次,加热24小时后取出滤料;重复上述操作一次;最后,向滤料加入适量氯化铝(AlCl3)溶液和氢氧化钠(NaOH)溶液,用量比例为20:1,搅拌均匀;之后,置入350℃马弗炉中,烘制8小时后取出;待滤料冷却后,用自来水缓慢冲洗,以去除表面粘附不牢的涂层物;用蒸馏水冲洗三遍,烘干待用,得到氧化铝改性钠钙玻璃微珠滤料。Step 2: Weigh 30 g of pretreated soda-lime glass microbeads, put them in an oven (50° C.) to dry for later use; configure aluminum chloride (AlCl 3 ) solution 3mol/L, sodium hydroxide (NaOH) solution 10mol/L L, add soda-lime glass microbeads and stir evenly, and then put it into the oven (110°C) to bake for 24 hours; in order to ensure that the filter material is heated evenly, stir once every hour in the early stage of heating, and take out the filter material after heating for 24 hours; repeat The above operations were performed once; finally, an appropriate amount of aluminum chloride (AlCl 3 ) solution and sodium hydroxide (NaOH) solution were added to the filter material, and the dosage ratio was 20:1, and stirred evenly; Take out after 8 hours of preparation; after the filter material is cooled, slowly rinse with tap water to remove the coating that is not firmly adhered to the surface; rinse with distilled water three times, and dry for use to obtain alumina-modified soda-lime glass microbeads filter material.

步骤三:取适量步骤二处理后的样品,喷金制样,放入槽中,抽真空达到5*10-3Pa,调节电压达到20kv、对比度与亮度,使用扫描电子显微镜寻找合适区域进行拍照,X射线进行普通能谱扫描,采用X射线能谱分析检测方法分析获取组成样品材料的各种元素的浓度。Step 3: Take an appropriate amount of the sample processed in Step 2, spray gold to prepare the sample, put it into the tank, vacuumize to 5*10 -3 Pa, adjust the voltage to 20kv, contrast and brightness, and use a scanning electron microscope to find a suitable area to take pictures , X-ray scans the ordinary energy spectrum, and uses the X-ray energy spectrum analysis and detection method to analyze and obtain the concentration of various elements that make up the sample material.

步骤四:取适量步骤二处理后的样品,直接填充至1.45cm直径和长度约1.8cm的柱子,通入氯化钠电解液,电解溶液为质量分数为0.13%NaCl(0.019mol/L),其初始电导率2.67mS/cm。因需要控制pH值为7之间,加入混合磷酸盐(0.025mol/L)导致其电导率上升至3.4mS/cm,此时读取改性后钠钙玻璃微珠滤料的zeta电位。Step 4: Take an appropriate amount of the sample processed in step 2, directly fill it into a column with a diameter of 1.45cm and a length of about 1.8cm, and pass into the sodium chloride electrolyte, and the electrolyte solution is a mass fraction of 0.13%NaCl (0.019mol/L), Its initial conductivity is 2.67mS/cm. Due to the need to control the pH value between 7, adding mixed phosphate (0.025mol/L) causes its conductivity to rise to 3.4mS/cm, and then read the zeta potential of the modified soda-lime glass microbead filter material.

实施例3:Example 3:

步骤一:使用20-22目筛网筛选出堆积体积为200ml的钠钙玻璃微珠,使用优级纯(GR)99.8%的无水乙醇反复清洗上述原料5-6次;将清洗好的钠钙玻璃微珠原料依次放入盛有去离子水、乙醇、丙酮的烧杯中各超声10min;将经过超声清洗的玻璃微珠原料放入“食人酸”溶液(浓硫酸和双氧水的体积比为7:3),然后在95℃下水浴酸洗2小时;水浴酸洗完成之后用去离子水将玻璃微珠上残留的酸液反复冲洗干净,之后放入无水乙醇中保存备用。Step 1: Use a 20-22 mesh screen to screen out soda-lime glass microbeads with a stacking volume of 200ml, and use the excellent grade pure (GR) 99.8% absolute ethanol to repeatedly wash the above raw materials for 5-6 times; The raw materials of calcium glass microbeads are placed in a beaker containing deionized water, ethanol and acetone in turn for 10 minutes each; 7:3), and then pickled in a water bath for 2 hours at 95°C; after the pickling in a water bath, the residual acid solution on the glass beads was repeatedly rinsed with deionized water, and then placed in anhydrous ethanol for later use.

步骤二:称取30g预处理后的钠钙玻璃微珠,放入烘箱(50℃)中烘干备用;配置氯化铝(AlCl3)溶液3mol/L,氢氧化钠(NaOH)溶液10mol/L,加入钠钙玻璃微珠中搅拌均匀,再次放入烘箱(120℃)烘24小时;为确保滤料受热均匀,在加热前期每个一小时搅拌一次,加热24小时后取出滤料;重复上述操作一次;最后,向滤料加入适量氯化铝(AlCl3)溶液和氢氧化钠(NaOH)溶液,用量比例为20:1,搅拌均匀;之后,置入550℃马弗炉中,烘制12小时后取出;待滤料冷却后,用自来水缓慢冲洗,以去除表面粘附不牢的涂层物;用蒸馏水冲洗三遍,烘干待用,得到氧化铝改性钠钙玻璃微珠滤料。Step 2: Weigh 30 g of pretreated soda-lime glass microbeads, put them in an oven (50° C.) to dry for later use; configure aluminum chloride (AlCl 3 ) solution 3mol/L, sodium hydroxide (NaOH) solution 10mol/L L, add soda-lime glass microbeads and stir evenly, then put it into the oven (120°C) to bake for 24 hours; in order to ensure that the filter material is heated evenly, stir once every hour in the early stage of heating, and take out the filter material after 24 hours of heating; repeat The above operation was performed once; finally, an appropriate amount of aluminum chloride (AlCl 3 ) solution and sodium hydroxide (NaOH) solution were added to the filter material, and the dosage ratio was 20:1, and stirred evenly; Take it out after 12 hours of preparation; after the filter material is cooled, slowly rinse with tap water to remove the coating that is not firmly adhered to the surface; rinse with distilled water three times, and dry for use to obtain alumina-modified soda-lime glass microbeads filter material.

步骤三:取适量步骤二处理后的样品,喷金制样,放入槽中,抽真空达到5*10-3Pa,调节电压达到20kv、对比度与亮度,使用扫描电子显微镜寻找合适区域进行拍照,X射线进行普通能谱扫描,采用X射线能谱分析检测方法分析获取组成样品材料的各种元素的浓度。Step 3: Take an appropriate amount of the sample processed in Step 2, spray gold to prepare the sample, put it into the tank, vacuumize to 5*10 -3 Pa, adjust the voltage to 20kv, contrast and brightness, and use a scanning electron microscope to find a suitable area to take pictures , X-ray scans the ordinary energy spectrum, and uses the X-ray energy spectrum analysis and detection method to analyze and obtain the concentration of various elements that make up the sample material.

步骤四:取适量步骤二处理后的样品,直接填充至1.45cm直径和长度约1.8cm的柱子,通入氯化钠电解液,电解溶液为质量分数为0.13%NaCl(0.019mol/L),其初始电导率2.67mS/cm。因需要控制pH值为7之间,加入混合磷酸盐(0.025mol/L)导致其电导率上升至3.4mS/cm,此时读取改性前钠钙玻璃微珠滤料的zeta电位。Step 4: Take an appropriate amount of the sample processed in step 2, directly fill it into a column with a diameter of 1.45cm and a length of about 1.8cm, and pass into the sodium chloride electrolyte, and the electrolyte solution is a mass fraction of 0.13%NaCl (0.019mol/L), Its initial conductivity is 2.67mS/cm. Due to the need to control the pH value between 7, the addition of mixed phosphate (0.025mol/L) caused its conductivity to rise to 3.4mS/cm. At this time, the zeta potential of the soda-lime glass microbead filter material before modification was read.

尽管上面结合附图对本发明的功能及工作过程进行了描述,但本发明并不局限于上述的具体功能和工作过程,上述的具体实施方式仅仅是示意性的,而不是限制性的,本领域的普通技术人员在本发明的启示下,在不脱离本发明宗旨和权利要求所保护的范围情况下,还可以做出很多形式,这些均属于本发明的保护之内。Although the functions and working process of the present invention have been described above in conjunction with the accompanying drawings, the present invention is not limited to the above-mentioned specific functions and working processes. Under the inspiration of the present invention, those of ordinary skill in the art can also make many forms without departing from the scope of the present invention and the protection scope of the claims, which all belong to the protection of the present invention.

Claims (4)

1.一种氧化铝改性钠钙玻璃微珠滤料的制备方法,其特征在于,将钠钙玻璃微珠原料,经过表面预处理清洁之后,将氧化铝附着在表面,实现钠钙玻璃微珠滤料的带电功能化,从而制成特定目数的改性钠钙玻璃微珠滤料。1. a preparation method of alumina-modified soda-lime glass microbead filter material, is characterized in that, with soda-lime glass microbead raw material, after surface pretreatment cleaning, alumina is attached to the surface, realizes soda-lime glass microbeads. The charged functionalization of the bead filter material can make the modified soda-lime glass microbead filter material with a specific mesh number. 2.根据权利要求1所述的氧化铝改性钠钙玻璃微珠滤料的制备方法,其特征在于,具体包括以下步骤:2. the preparation method of alumina modified soda-lime glass microbead filter material according to claim 1, is characterized in that, specifically comprises the following steps: (1)钠钙玻璃微珠表面预处理(1) Surface pretreatment of soda lime glass beads 通过特定目数的筛网筛选出一定量的钠钙玻璃微珠原料,使用优级纯的无水乙醇反复清洗上述原料5-6次;将清洗好的钠钙玻璃微珠原料依次放入盛有去离子水、乙醇、丙酮的烧杯中各超声10min;将经过超声清洗的玻璃微珠原料放入“食人酸”溶液,然后在95℃下水浴酸洗2小时;水浴酸洗完成之后用去离子水将玻璃微珠上残留的酸液反复冲洗干净,之后放入无水乙醇中保存备用;A certain amount of soda-lime glass microbead raw materials are screened through a screen with a specific mesh number, and the above-mentioned raw materials are repeatedly washed with excellent grade pure anhydrous ethanol for 5-6 times; Ultrasonic for 10min each in a beaker with deionized water, ethanol, and acetone; put the raw glass beads cleaned by ultrasonic into the "cannibal acid" solution, and then pickled in a water bath at 95°C for 2 hours; The acid solution remaining on the glass beads was repeatedly rinsed with deionized water, and then placed in anhydrous ethanol for future use; (2)钠钙玻璃微珠改性处理(2) Modification of soda lime glass beads 称取步骤(1)预处理后的钠钙玻璃微珠,放入烘箱中烘干备用;配置足量氯化铝溶液与氢氧化钠溶液,加入钠钙玻璃微珠中搅拌均匀,再次放入烘箱烘24小时;为确保滤料受热均匀,在加热前期每隔一小时搅拌一次,加热24小时后取出滤料;重复上述操作一次;最后,向滤料加入氯化铝溶液和氢氧化钠溶液,搅拌均匀;之后,置入马弗炉中,烘制一定时间后取出;待滤料冷却后,用自来水冲洗,以去除表面粘附不牢的涂层物;用蒸馏水冲洗三遍,烘干待用,得到氧化铝改性钠钙玻璃微珠滤料。Weigh the pretreated soda-lime glass beads in step (1), put them into an oven to dry for later use; configure a sufficient amount of aluminum chloride solution and sodium hydroxide solution, add them into the soda-lime glass beads, stir evenly, and put them in again. Bake in an oven for 24 hours; in order to ensure that the filter material is heated evenly, stir every one hour in the early stage of heating, and take out the filter material after 24 hours of heating; repeat the above operation once; finally, add aluminum chloride solution and sodium hydroxide solution to the filter material , stir evenly; after that, put it in the muffle furnace, and take it out after baking for a certain period of time; after the filter material is cooled, rinse it with tap water to remove the coating that is not firmly adhered to the surface; rinse it with distilled water three times, and dry it. Standby to obtain alumina-modified soda-lime glass microbead filter material. 3.根据权利要求2所述的氧化铝改性钠钙玻璃微珠滤料的制备方法,其特征在于,步骤(1)中所述钠钙玻璃微珠的粒径为20-40目,所述无水乙醇的体积分数为99.8%,所述丙酮的体积分数为99.5%,所述“食人酸”溶液由浓硫酸和双氧水构成,浓硫酸和双氧水的体积比为7:3。3. The preparation method of alumina-modified soda-lime glass microbead filter material according to claim 2, wherein the particle size of the soda-lime glass microbeads described in step (1) is 20-40 mesh, so The volume fraction of the anhydrous ethanol is 99.8%, the volume fraction of the acetone is 99.5%, the "cannibal acid" solution is composed of concentrated sulfuric acid and hydrogen peroxide, and the volume ratio of concentrated sulfuric acid and hydrogen peroxide is 7:3. 4.根据权利要求2所述的氧化铝改性钠钙玻璃微珠滤料的制备方法,其特征在于,步骤(2)中氯化铝溶液的浓度为3mol/L,氢氧化钠溶液的浓度为10mol/L,氯化铝溶液和氢氧化钠溶液的用量比例为20:1;预处理后的钠钙玻璃微珠放入50℃烘箱中烘干备用,氯化铝溶液与氢氧化钠溶液,加入氯化铝溶液与氢氧化钠溶液搅拌均匀后的钠钙玻璃微珠放入100℃-120℃烘箱烘24小时,马弗炉温度设置240℃-550℃。4. the preparation method of alumina modified soda lime glass microbead filter material according to claim 2, is characterized in that, in step (2), the concentration of aluminum chloride solution is 3mol/L, and the concentration of sodium hydroxide solution It is 10mol/L, and the dosage ratio of aluminum chloride solution and sodium hydroxide solution is 20:1; the pretreated soda-lime glass beads are placed in a 50 ℃ oven to dry for use, and aluminum chloride solution and sodium hydroxide solution are used. , the soda-lime glass microbeads after adding aluminum chloride solution and sodium hydroxide solution and stirring evenly are placed in an oven at 100°C-120°C for 24 hours, and the temperature of the muffle furnace is set at 240°C-550°C.
CN202011134704.XA 2020-10-21 2020-10-21 A kind of preparation method of alumina modified soda lime glass microbead filter material Pending CN114380344A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202011134704.XA CN114380344A (en) 2020-10-21 2020-10-21 A kind of preparation method of alumina modified soda lime glass microbead filter material

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202011134704.XA CN114380344A (en) 2020-10-21 2020-10-21 A kind of preparation method of alumina modified soda lime glass microbead filter material

Publications (1)

Publication Number Publication Date
CN114380344A true CN114380344A (en) 2022-04-22

Family

ID=81192966

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202011134704.XA Pending CN114380344A (en) 2020-10-21 2020-10-21 A kind of preparation method of alumina modified soda lime glass microbead filter material

Country Status (1)

Country Link
CN (1) CN114380344A (en)

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115518459A (en) * 2022-08-25 2022-12-27 上海凯工石油装备科技有限公司 Production process of green glass filter material

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101301548A (en) * 2008-01-25 2008-11-12 山东建筑大学 A modified filter material with zeolite as carrier and its preparation method
CN106512551A (en) * 2016-12-12 2017-03-22 浙江工业大学 Amino-functionalized regenerated glass filter material for water treatment and preparation and application thereof
KR20170057581A (en) * 2015-11-17 2017-05-25 한국과학기술연구원 Absorbing medium using water-treatment sludge and method for fabricating the same
CN110559741A (en) * 2019-08-30 2019-12-13 天津大学 Preparation method of spherical glass filter material with charged surface

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101301548A (en) * 2008-01-25 2008-11-12 山东建筑大学 A modified filter material with zeolite as carrier and its preparation method
KR20170057581A (en) * 2015-11-17 2017-05-25 한국과학기술연구원 Absorbing medium using water-treatment sludge and method for fabricating the same
CN106512551A (en) * 2016-12-12 2017-03-22 浙江工业大学 Amino-functionalized regenerated glass filter material for water treatment and preparation and application thereof
CN110559741A (en) * 2019-08-30 2019-12-13 天津大学 Preparation method of spherical glass filter material with charged surface

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
高乃云 等: "氧化铝涂层改性石英砂过滤性能研究", 《中国给水排水》, pages 8 - 10 *

Cited By (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115518459A (en) * 2022-08-25 2022-12-27 上海凯工石油装备科技有限公司 Production process of green glass filter material

Similar Documents

Publication Publication Date Title
CN104627960B (en) A kind of method of changed red mud catalytic methane cracking hydrogen production
CN103691199B (en) The preparation method of composite filter material for seawater purification
CN104388923A (en) Making method of graphene modified titanium oxide metal anticorrosion coating
CN105198048A (en) Three-dimensional electrode filling material and preparation method thereof
CN109433213B (en) Method for selectively dealkalizing red mud and enriching iron
CN111943336A (en) Method for preparing polysilicate aluminum ferric flocculant, polysilicate aluminum ferric flocculant and application thereof
CN110801814A (en) A kind of preparation method of magnetic amino walnut shell biochar novel adsorbent
CN109046229B (en) A kind of lanthanum hydroxide modified hydroxyapatite material and preparation method and application thereof
CN109012671A (en) A kind of preparation method of activated carbon supported ferric oxide solid Fenton reagent
CN112827468A (en) A kind of preparation method and application of fly ash-based defluorination adsorbent
CN114380344A (en) A kind of preparation method of alumina modified soda lime glass microbead filter material
CN100515536C (en) A kind of preparation technology of lipophilic porous ceramic filter material
CN110479221A (en) A kind of preparation method and application of red mud/polypyrrole composite adsorbing material
CN105858822A (en) Red titanium dioxide photoelectrode with wedge-shaped structure and preparing and application of red titanium dioxide photoelectrode
CN106902760B (en) A kind of eggshell load zinc oxide material and its preparation method and application
CN108043400A (en) Au-Bi2MoO6Diatomite composite material and preparation method and application thereof
CN110280313A (en) A kind of three-dimensional structure load TiO2-xThe preparation method of material
CN115282792B (en) Preparation method of polymer-magnetic organometallic framework compound composite separation membrane
CN115025756B (en) A kind of preparation method of modified coal gangue adsorbent
CN114380343A (en) Preparation method of iron oxide modified quartz sand filter material
CN115970636A (en) Coal gangue-based C-A-S-H gel, preparation method and application
CN109081555A (en) A kind of diaphragm filter press sludge dewatering agent
CN114984904A (en) Preparation method of modified volcanic rock and application of modified volcanic rock
CN106957095A (en) For removing composite modified activated carbon electrodes of copper ion and preparation method thereof in water removal
CN102642895B (en) A kind of lead dioxide electrode, preparation method and application in processing active dye

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
WD01 Invention patent application deemed withdrawn after publication
WD01 Invention patent application deemed withdrawn after publication

Application publication date: 20220422