CN104801308A - A kind of NiFe2O4/TiO2/sepiolite composite photocatalyst and its preparation method - Google Patents
A kind of NiFe2O4/TiO2/sepiolite composite photocatalyst and its preparation method Download PDFInfo
- Publication number
- CN104801308A CN104801308A CN201510233949.0A CN201510233949A CN104801308A CN 104801308 A CN104801308 A CN 104801308A CN 201510233949 A CN201510233949 A CN 201510233949A CN 104801308 A CN104801308 A CN 104801308A
- Authority
- CN
- China
- Prior art keywords
- tio
- sepiolite
- nife
- film
- composite photocatalyst
- 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.)
- Granted
Links
Landscapes
- Catalysts (AREA)
Abstract
一种NiFe2O4/TiO2/海泡石复合光催化剂,成分包括海泡石、TiO2和NiFe2O4,海泡石为载体,TiO2以膜的形式包裹在海泡石表面,NiFe2O4以颗粒的形式负载在TiO2表面。本发明还提供所述NiFe2O4/TiO2/海泡石复合光催化剂的制备方法。本发明将TiO2以膜的形式包裹在海泡石表面,NiFe2O4以颗粒的形式负载在TiO2表面,NiFe2O4以颗粒的形式负载在TiO2膜表面,不会遮住全部的TiO2膜,而是和TiO2形成一个符合效应,将海泡石作为载体,可进一步提高催化剂的吸附能力,从而使得本催化剂同时拥有吸附效果好、光催化活性高、能够回收和重复利用的优点,而且拓展了光响应范围,本催化剂不仅在紫外光区的催化活性得到提高,而且响应波长从紫外光区移至可见光区,从而能够提高太阳光的利用率。
A NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst, the composition includes sepiolite, TiO 2 and NiFe 2 O 4 , sepiolite is used as a carrier, TiO 2 is wrapped on the surface of sepiolite in the form of a film, NiFe 2 O 4 is supported on the surface of TiO 2 in the form of particles. The invention also provides a preparation method of the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst. In the present invention, TiO 2 is wrapped on the surface of sepiolite in the form of film, NiFe 2 O 4 is loaded on the surface of TiO 2 in the form of particles, and NiFe 2 O 4 is loaded on the surface of TiO 2 film in the form of particles, which will not cover all TiO 2 film, but with TiO 2 to form a coincidence effect, using sepiolite as a carrier, can further improve the adsorption capacity of the catalyst, so that the catalyst has good adsorption effect, high photocatalytic activity, and can be recycled and reused In addition, the photoresponse range is expanded. This catalyst not only improves the catalytic activity in the ultraviolet region, but also shifts the response wavelength from the ultraviolet region to the visible region, thereby improving the utilization rate of sunlight.
Description
技术领域technical field
本发明涉及光催化氧化法技术领域,具体地说涉及一种NiFe2O4/TiO2/海泡石复合光催化剂及其制备方法。The invention relates to the technical field of photocatalytic oxidation, in particular to a NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst and a preparation method thereof.
背景技术Background technique
光催化氧化法技术,是近二十几年来应用于废水领域的一种新型高效的工业废水处理技术。光催化氧化法技术中常用的光催化剂是纳米TiO2,它用于废水处理,是环保技术的一个新突破。纳米TiO2光催化剂在紫外光的照射下,能产生氧化和还原能力较强的电子-空穴对,能有效降解造纸废水中的氯代酚类、卤代烃类、二恶英、各种有机酸等,且除净度高、降解速度快、无二次污染,使用周期长、适用的污染物广,达到一次性降解污染物的目的,所以对它的研究十分广泛。Photocatalytic oxidation technology is a new type of high-efficiency industrial wastewater treatment technology that has been applied in the field of wastewater for more than 20 years. The photocatalyst commonly used in photocatalytic oxidation technology is nano-TiO 2 , which is used for wastewater treatment and is a new breakthrough in environmental protection technology. Under the irradiation of ultraviolet light, the nano- TiO2 photocatalyst can generate electron-hole pairs with strong oxidation and reduction capabilities, which can effectively degrade chlorinated phenols, halogenated hydrocarbons, dioxins, various Organic acids, etc., and have high cleanliness, fast degradation speed, no secondary pollution, long service life, wide range of applicable pollutants, and achieve the purpose of one-time degradation of pollutants, so its research is very extensive.
目前,TiO2作为光催化剂在实际应用过程中存在一些不足之处,例如:TiO2的光催化剂量子效率低,选择吸附性差,固化条件苛刻,易凝聚、易失活,而且光谱响应范围在紫外光区,太阳光谱中可见光部分不能有效利用,这些都限制了TiO2的工业应用。针对TiO2作为光催化剂存在的不足,目前国内外对TiO2光催化剂主要进行两个方面的改性研究:一是开发TiO2负载型光催化剂;二是通过掺杂对TiO2进行改性,使其在实际应用中得到更好地利用。At present, TiO 2 has some shortcomings in the practical application process as a photocatalyst, such as: the photocatalyst quantum efficiency of TiO 2 is low, the selective adsorption is poor, the curing conditions are harsh, easy to condense, easy to deactivate, and the spectral response range is in the ultraviolet In the light region, the visible part of the solar spectrum cannot be effectively utilized, which limits the industrial application of TiO2 . In view of the shortcomings of TiO 2 as a photocatalyst, there are currently two main researches on the modification of TiO 2 photocatalysts at home and abroad: one is to develop TiO 2 supported photocatalysts; the other is to modify TiO 2 by doping, make it better used in practical applications.
在TiO2负载型光催化剂研究领域中,有研究人员开发出TiO2/海泡石负载型光催化剂,这种催化剂是在海泡石表面包裹TiO2,海泡石为含水镁铝硅酸盐粘土矿物,价格便宜,来源广泛,是一种具有更大比表面积的多孔介质材料,可以提高对有机污染物的吸附效果。海泡石晶体结构中存在大量微孔道,是由无数平行管状孔道组合,其比表面积大,海泡石吸附性质受到其晶体结构的制约。海泡石表面电荷是由其表面的Si-O键和Al-O键发生水解破裂,既能成为酸,也能作为碱,破键水解产生的R-OH上的羟基(-OH),故其具有两性,这些表面反应使海泡石表面带电荷。改性作用主要是使海泡石在水溶液中的结构电荷和表面电荷发生改变,从而改变海泡石的带电性和吸附活性。In the field of TiO 2 supported photocatalyst research, some researchers have developed a TiO 2 / sepiolite supported photocatalyst, which is a catalyst coated with TiO 2 on the surface of sepiolite, which is a hydrous magnesium aluminum silicate Clay minerals are cheap and widely sourced. They are porous media materials with a larger specific surface area, which can improve the adsorption effect on organic pollutants. There are a large number of micropores in the crystal structure of sepiolite, which are composed of countless parallel tubular pores, and its specific surface area is large. The adsorption properties of sepiolite are restricted by its crystal structure. The surface charge of sepiolite is caused by the hydrolysis and rupture of the Si-O bond and Al-O bond on the surface, which can be used as an acid or a base, and the hydroxyl group (-OH) on the R-OH produced by the bond-breaking hydrolysis, so It is amphoteric, and these surface reactions charge the surface of sepiolite. The modification is mainly to change the structural charge and surface charge of sepiolite in aqueous solution, thereby changing the chargeability and adsorption activity of sepiolite.
在通过掺杂对TiO2进行改性领域,有研究人员利用磁性材料对TiO2进行掺杂以形成的复合催化剂,常用的掺杂手法有在Fe3O4或CoFe2O4表面包裹TiO2,这种复合催化剂可增大光吸收范围,光催化活性。另外由于掺杂了磁性材料,有利于催化剂的回收和再利用。In the field of modification of TiO 2 by doping, some researchers use magnetic materials to dope TiO 2 to form a composite catalyst. The commonly used doping method is to wrap TiO 2 on the surface of Fe 3 O 4 or CoFe 2 O 4 , this composite catalyst can increase the range of light absorption and photocatalytic activity. In addition, due to the doping of magnetic materials, it is beneficial to the recovery and reuse of the catalyst.
发明内容Contents of the invention
本发明所要解决的技术问题是提供一种同时拥有吸附效果好、光催化活性高、能够回收和重复利用的优点的NiFe2O4/TiO2/海泡石复合光催化剂。The technical problem to be solved by the present invention is to provide a NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst which has the advantages of good adsorption effect, high photocatalytic activity, and the ability to recycle and reuse.
为了解决上述技术问题,本发明采用如下技术方案:一种NiFe2O4/TiO2/海泡石复合光催化剂,成分包括海泡石、TiO2和NiFe2O4,海泡石为载体,TiO2以膜的形式包裹在海泡石表面,NiFe2O4以颗粒的形式负载在TiO2表面。In order to solve the above technical problems, the present invention adopts the following technical scheme: a NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst, the components include sepiolite, TiO 2 and NiFe 2 O 4 , the sepiolite is the carrier, TiO 2 is wrapped on the surface of sepiolite in the form of film, and NiFe 2 O 4 is loaded on the surface of TiO 2 in the form of particles.
进一步的,其中Ni的含量为1—2wt%、Fe的含量为1.9—3.8wt%、Ti的含量为12—18wt%,余分为海泡石。NiFe2O4/TiO2/海泡石复合光催化剂的各组分含量在此范围内时,其催化效果较好。Further, the content of Ni is 1-2wt%, the content of Fe is 1.9-3.8wt%, the content of Ti is 12-18wt%, and the rest is sepiolite. When the content of each component of the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst is within this range, its catalytic effect is better.
进一步的,Ni的含量为1.5wt%、Fe的含量为2.8wt%、Ti的含量为15wt%,余分为海泡石。Further, the content of Ni is 1.5wt%, the content of Fe is 2.8wt%, the content of Ti is 15wt%, and the rest is sepiolite.
本发明还提供所述的NiFe2O4/TiO2/海泡石复合光催化剂的制备方法,包括以下步骤:The present invention also provides a preparation method of the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst, comprising the following steps:
(1)海泡石的预处理(1) Pretreatment of sepiolite
将海泡石粉碎成末,置于浓度为5—15%的稀硝酸中浸泡15—24h,过滤、用水漂洗至中性后烘干,然后在400—500℃的温度下煅烧2—4h,用水漂洗并将漂浮于水体中上部位的海泡石过滤出来,干燥后筛取粒径为100—125目的海泡石粉末作为载体;Pulverize sepiolite into powder, soak in dilute nitric acid with a concentration of 5-15% for 15-24 hours, filter, rinse with water until neutral, dry, and then calcinate at 400-500°C for 2-4 hours, Rinse with water and filter out the sepiolite floating in the upper part of the water body, and sieve the sepiolite powder with a particle size of 100-125 mesh as a carrier after drying;
(2)TiO2溶胶的制备(2) Preparation of TiO 2 sol
室温下,按体积份,将15—20的钛酸丁酯充分溶解于40—50的无水乙醇中,然后加入5—6的乙酰丙酮,得到溶液A,将0.75—1.0的蒸馏水和20—25的无水乙醇充分混合后得到溶液B,在不断搅拌的条件下将溶液B逐渐加入到溶液A中,然后用浓硝酸或浓盐酸将pH值调至4—5,搅拌l—2h,加入1—1.5的聚乙二醇,然后在40—65℃的条件下搅拌l—1.5h,得到黄色透明的TiO2溶胶,将TiO2溶胶在室温下陈化12—15h;At room temperature, in parts by volume, fully dissolve 15-20% butyl titanate in 40-50% absolute ethanol, then add 5-6% acetylacetone to obtain solution A, mix 0.75-1.0% distilled water and 20- 25% of absolute ethanol is fully mixed to obtain solution B, gradually add solution B to solution A under the condition of constant stirring, then adjust the pH value to 4-5 with concentrated nitric acid or concentrated hydrochloric acid, stir for 1-2h, add 1-1.5 polyethylene glycol, then stirred at 40-65°C for 1-1.5h to obtain a yellow and transparent TiO 2 sol, and aged the TiO 2 sol at room temperature for 12-15h;
(3)在海泡石表面包裹TiO2膜(3) Coating TiO 2 film on the surface of sepiolite
TiO2膜的层数为1—3层,每层TiO2膜的形成方法为:室温下,将海泡石加入到TiO2溶胶中,搅拌至与TiO2溶胶完全混合,然后在70—85℃的条件下烘干,最后在400—500℃的条件下煅烧1—3h,冷却后备用;The number of layers of TiO 2 film is 1-3 layers, and the formation method of each layer of TiO 2 film is as follows: at room temperature, add sepiolite to TiO 2 sol, stir until it is completely mixed with TiO 2 sol, and then in 70-85 Dry under the condition of ℃, and finally calcined under the condition of 400-500℃ for 1-3h, cool down and set aside;
(4)在TiO2膜表面负载NiFe2O4颗粒(4) Loading NiFe 2 O 4 particles on the surface of TiO 2 film
室温下,按重量份,将2.91—5.82的Ni(NO3)2·6H2O和8.08—16.16的Fe(NO3)3·9H2O加入到55.3—63.2的无水乙醇中,搅拌30—60min,用5—20mol/L的NaOH溶液将pH值调至9—10,然后加入包裹有TiO2膜的海泡石,搅拌30—60min,然后在160—180℃的条件下反应18—24h,冷却后进行固液分离、水洗,最后在70—85℃的条件下烘干,即得所述的NiFe2O4/TiO2/海泡石复合光催化剂。At room temperature, in parts by weight, add 2.91-5.82 Ni(NO 3 ) 2 ·6H 2 O and 8.08-16.16 Fe(NO 3 ) 3 ·9H 2 O into 55.3-63.2 absolute ethanol, stir for 30 -60min, adjust the pH value to 9-10 with 5-20mol/L NaOH solution, then add sepiolite wrapped with TiO 2 film, stir for 30-60min, then react at 160-180℃ for 18- After cooling for 24 hours, carry out solid-liquid separation, water washing, and finally dry at 70-85°C to obtain the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst.
为简洁描述起见,以下本发明所述的NiFe2O4/TiO2/海泡石复合光催化剂简称为本催化剂,所述的NiFe2O4/TiO2/海泡石复合光催化剂的制备方法简称为本方法。For the sake of concise description, the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst described in the present invention is referred to as the catalyst for short, and the preparation method of the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst referred to as this method.
本发明的有益效果为:The beneficial effects of the present invention are:
(1)本催化剂将TiO2以膜的形式包裹在海泡石表面,NiFe2O4以颗粒的形式负载在TiO2表面,NiFe2O4以颗粒的形式负载在TiO2膜表面,不会遮住全部的TiO2膜,而是和TiO2形成一个符合效应,将海泡石作为载体,可进一步提高催化剂的吸附能力,从而使得本催化剂同时拥有吸附效果好、光催化活性高、能够回收和重复利用的优点,而且拓展了光响应范围,本催化剂不仅在紫外光区的催化活性得到提高,而且响应波长从紫外光区移至可见光区,从而能够提高太阳光的利用率。(1) In this catalyst, TiO 2 is wrapped on the surface of sepiolite in the form of film, NiFe 2 O 4 is loaded on the surface of TiO 2 in the form of particles, and NiFe 2 O 4 is loaded on the surface of TiO 2 film in the form of particles, which will not Covering all the TiO 2 film, but forming a coincidence effect with TiO 2 , using sepiolite as a carrier can further improve the adsorption capacity of the catalyst, so that the catalyst has good adsorption effect, high photocatalytic activity, and can be recycled And the advantages of repeated use, and expand the photoresponse range, the catalytic activity of the catalyst not only in the ultraviolet region is improved, but also the response wavelength is shifted from the ultraviolet region to the visible region, so that the utilization rate of sunlight can be improved.
(2)本催化剂采用了NiFe2O4,NiFe2O4不但具有磁性作用,易于回收和重复利用,而且NiFe2O4作为催化剂在紫外光下也能够催化降解污染物,其负载在TiO2膜表面,一方面提高本催化剂在紫外光区的降解率,另一方面将光响应范围拓宽至可见光区。(2) This catalyst uses NiFe 2 O 4 . NiFe 2 O 4 not only has magnetic effect, but also is easy to recycle and reuse, and NiFe 2 O 4 as a catalyst can also catalyze and degrade pollutants under ultraviolet light. It is loaded on TiO 2 The surface of the membrane, on the one hand, improves the degradation rate of the catalyst in the ultraviolet region, and on the other hand, broadens the photoresponse range to the visible region.
(3)本方法是以水热法将NiFe2O4合成负载在TiO2膜表面,水热法的特点是能够制备出纯度较高、分散性好、晶形好的纳米颗粒,这样就使得NiFe2O4以纳米颗粒的形态非常均匀地负载在TiO2膜表面,而且由于在水热反应之前采用的是强制水解生成Ni(OH)2和Fe(OH)3,没有添加水解抑制剂和表面活性剂,从而保证在随后的水热反应中NiFe2O4不易以膜的形式存在,而是以颗粒状态分布在TiO2膜表面。(3) This method uses a hydrothermal method to synthesize and load NiFe 2 O 4 on the surface of the TiO 2 film. The hydrothermal method is characterized by the ability to prepare nanoparticles with high purity, good dispersibility, and good crystal shape, which makes NiFe 2 O 4 is very uniformly loaded on the surface of TiO 2 film in the form of nanoparticles, and since Ni(OH) 2 and Fe(OH) 3 are generated by forced hydrolysis before the hydrothermal reaction, no hydrolysis inhibitor and surface Active agent, so as to ensure that NiFe 2 O 4 is not easy to exist in the form of film in the subsequent hydrothermal reaction, but is distributed on the surface of TiO 2 film in particle state.
(4)本方法在海泡石的预处理过程中对海泡石进行煅烧,可以将海泡石表面及内部孔隙中的杂质变成气态物质去除,从而增大海泡石比表面积和孔隙率,提高海泡石的表面积和吸附能力,有利于TiO2的负载,提高光催化性能。(4) this method calcines the sepiolite in the pretreatment process of the sepiolite, the impurities in the sepiolite surface and internal pores can be changed into gaseous substances and removed, thereby increasing the sepiolite specific surface area and porosity, Increasing the surface area and adsorption capacity of sepiolite is beneficial to the loading of TiO2 and improves the photocatalytic performance.
(5)本方法在TiO2溶胶的制备过程中,钛酸四丁酯与蒸馏水发生水解反应生成TiO2溶胶,由于钛酸丁酯的水解十分剧烈,所以加入乙酰丙酮作为它的抑制剂,乙酰丙酮与钛酸丁酯形成配位体,使大量的水不能去除,这些配位体阻止了水解反应进行,和TiO2进一步的聚合,从而形成稳定的胶体溶液。(5) In the preparation process of TiO2 sol in this method, tetrabutyl titanate and distilled water undergo hydrolysis reaction to generate TiO2 sol. Since the hydrolysis of butyl titanate is very violent, acetylacetone is added as its inhibitor, acetylacetone Acetone and butyl titanate form ligands, so that a large amount of water cannot be removed, and these ligands prevent the hydrolysis reaction from proceeding, and the further polymerization of TiO2 , thus forming a stable colloidal solution.
(6)本方法在海泡石表面包裹TiO2膜的过程中包裹了1—3层TiO2膜,随着TiO2膜层数的增加,催化效果会越来越好,当TiO2膜层数超过3层时,催化效果变差。(6) This method wraps 1-3 layers of TiO 2 films in the process of wrapping TiO 2 films on the surface of sepiolite. As the number of TiO 2 film layers increases, the catalytic effect will become better and better. When the TiO 2 film layers When the number exceeds 3 layers, the catalytic effect becomes poor.
附图说明Description of drawings
图1是本发明实施例1所得的NiFe2O4/TiO2/海泡石复合光催化剂的扫描电镜图。Fig. 1 is a scanning electron micrograph of the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst obtained in Example 1 of the present invention.
图2是现有TiO2/海泡石负载型光催化剂和本发明实施例1所得的NiFe2O4/TiO2/海泡石复合光催化剂的固体紫外-可见光谱图。Fig. 2 is a solid ultraviolet-visible spectrum diagram of the existing TiO 2 /sepiolite supported photocatalyst and the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst obtained in Example 1 of the present invention.
图3是海泡石和本发明实施例1所得的NiFe2O4/TiO2/海泡石复合光催化剂的红外光谱图。Fig. 3 is an infrared spectrogram of sepiolite and the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst obtained in Example 1 of the present invention.
图4是以本发明实施例1所得的NiFe2O4/TiO2/海泡石复合光催化剂光催化降解亚甲基蓝溶液的降解效率图。Fig. 4 is a diagram showing the photocatalytic degradation of methylene blue solution by NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst obtained in Example 1 of the present invention.
具体实施方式Detailed ways
下面结合实施例对本发明作进一步描述:The present invention will be further described below in conjunction with embodiment:
实施例1Example 1
一种NiFe2O4/TiO2/海泡石复合光催化剂,成分包括海泡石、TiO2和NiFe2O4,海泡石为载体,TiO2以膜的形式包裹在海泡石表面,NiFe2O4以颗粒的形式负载在TiO2表面,其中Ni的含量为1.5wt%、Fe的含量为2.8wt%、Ti的含量为15wt%,余分为海泡石。A NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst, the composition includes sepiolite, TiO 2 and NiFe 2 O 4 , sepiolite is used as a carrier, TiO 2 is wrapped on the surface of sepiolite in the form of a film, NiFe 2 O 4 is supported on the surface of TiO 2 in the form of particles, in which the content of Ni is 1.5wt%, that of Fe is 2.8wt%, that of Ti is 15wt%, and the rest is sepiolite.
上述NiFe2O4/TiO2/海泡石复合光催化剂的制备方法,包括以下步骤:The preparation method of the above-mentioned NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst comprises the following steps:
(1)海泡石的预处理(1) Pretreatment of sepiolite
将海泡石粉碎成末,置于浓度为5%的稀硝酸中浸泡20h,过滤、用水漂洗至中性后烘干,然后置于马弗炉中在400℃的温度下煅烧4h,用水漂洗并将漂浮于水体中上部位的海泡石过滤出来,干燥后筛取粒径为100目的海泡石粉末作为载体;Grind sepiolite into powder, soak in dilute nitric acid with a concentration of 5% for 20 hours, filter, rinse with water until neutral, then dry, then place in a muffle furnace for calcination at 400°C for 4 hours, rinse with water And the sepiolite floating in the middle and upper parts of the water body is filtered out, and after drying, the sepiolite powder with a particle size of 100 meshes is sieved as a carrier;
(2)TiO2溶胶的制备(2) Preparation of TiO 2 sol
室温下,按体积份,将18的钛酸丁酯充分溶解于40的无水乙醇中,然后加入5.5的乙酰丙酮,得到溶液A,将0.88的蒸馏水和25的无水乙醇充分混合后得到溶液B,在不断搅拌的条件下将溶液B逐渐加入到溶液A中,然后用浓硝酸将pH值调至4,搅拌(80r/min)1.5h,加入1.2的聚乙二醇,然后在52℃的条件下搅拌(100r/min)lh,得到黄色透明的TiO2溶胶,将TiO2溶胶在室温下陈化12h;At room temperature, in parts by volume, fully dissolve 18% butyl titanate in 40% absolute ethanol, then add 5.5% acetylacetone to obtain solution A, and fully mix 0.88% distilled water and 25% absolute ethanol to obtain a solution B. Gradually add solution B to solution A under constant stirring, then adjust the pH value to 4 with concentrated nitric acid, stir (80r/min) for 1.5h, add 1.2 polyethylene glycol, and then Under the condition of stirring (100r/min) 1h, obtain yellow transparent TiO sol, by TiO sol aging 12h at room temperature;
(3)在海泡石表面包裹TiO2膜(3) Coating TiO 2 film on the surface of sepiolite
TiO2膜的层数为2层,每层TiO2膜的形成方法为:室温下,将海泡石加入到TiO2溶胶中,搅拌(80r/min)1.2h令海泡石与TiO2溶胶完全混合,然后在70℃的条件下烘干,烘干过程采用先水浴蒸至近干,再用干燥箱烘干,最后置于马弗炉中在500℃的条件下煅烧1h,冷却后备用;The number of layers of TiO 2 film is 2 layers, and the formation method of each layer of TiO 2 film is: at room temperature, add sepiolite to TiO 2 sol, stir (80r/min) for 1.2h to make sepiolite and TiO 2 sol Mix completely, and then dry at 70°C. During the drying process, steam in a water bath to nearly dryness, then dry in a drying oven, and finally place it in a muffle furnace for calcination at 500°C for 1 hour, and cool it for later use;
(4)在TiO2膜表面负载NiFe2O4颗粒(4) Loading NiFe 2 O 4 particles on the surface of TiO 2 film
室温下,按重量份,将4.37的Ni(NO3)2·6H2O和12.12的Fe(NO3)3·9H2O加入到59的无水乙醇中,磁力搅拌(120r/min)45min,用5mol/L的NaOH溶液将pH值调至9,然后加入包裹有TiO2膜的海泡石,搅拌(100r/min)30min,然后在180℃的条件下反应21h,冷却后进行固液分离、水洗,最后在70℃的条件下烘干,即得所述的NiFe2O4/TiO2/海泡石复合光催化剂。At room temperature, in parts by weight, add 4.37% Ni(NO 3 ) 2 ·6H 2 O and 12.12% Fe(NO 3 ) 3 ·9H 2 O to 59% absolute ethanol, magnetically stir (120r/min) for 45min , use 5mol/L NaOH solution to adjust the pH value to 9, then add sepiolite wrapped with TiO 2 film, stir (100r/min) for 30min, then react at 180°C for 21h, after cooling, solid-liquid Separation, washing with water, and finally drying at 70° C. to obtain the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst.
实施例2Example 2
一种NiFe2O4/TiO2/海泡石复合光催化剂,成分包括海泡石、TiO2和NiFe2O4,海泡石为载体,TiO2以膜的形式包裹在海泡石表面,NiFe2O4以颗粒的形式负载在TiO2表面,其中Ni的含量为1wt%、Fe的含量为1.9wt%、Ti的含量为12wt%,余分为海泡石。A NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst, the composition includes sepiolite, TiO 2 and NiFe 2 O 4 , sepiolite is used as a carrier, TiO 2 is wrapped on the surface of sepiolite in the form of a film, NiFe 2 O 4 is supported on the surface of TiO 2 in the form of particles, in which the content of Ni is 1wt%, that of Fe is 1.9wt%, that of Ti is 12wt%, and the rest is sepiolite.
上述NiFe2O4/TiO2/海泡石复合光催化剂的制备方法,包括以下步骤:The preparation method of the above-mentioned NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst comprises the following steps:
(1)海泡石的预处理(1) Pretreatment of sepiolite
将海泡石粉碎成末,置于浓度为10%的稀硝酸中浸泡15h,过滤、用水漂洗至中性后烘干,然后置于马弗炉中在450℃的温度下煅烧3h,用水漂洗并将漂浮于水体中上部位的海泡石过滤出来,干燥后筛取粒径为112目的海泡石粉末作为载体;Crush the sepiolite into powder, soak it in dilute nitric acid with a concentration of 10% for 15 hours, filter it, rinse it with water until neutral, then dry it, then put it in a muffle furnace and calcinate it at 450°C for 3 hours, rinse it with water And the sepiolite floating in the upper part of the water body is filtered out, and after drying, the sepiolite powder with a particle size of 112 meshes is sieved as a carrier;
(2)TiO2溶胶的制备(2) Preparation of TiO 2 sol
室温下,按体积份,将15的钛酸丁酯充分溶解于45的无水乙醇中,然后加入5的乙酰丙酮,得到溶液A,将0.75的蒸馏水和20的无水乙醇充分混合后得到溶液B,在不断搅拌的条件下将溶液B逐渐加入到溶液A中,然后用浓硝酸将pH值调至5,搅拌(120r/min)lh,加入1.5的聚乙二醇,然后在65℃的条件下搅拌(80r/min)l.2h,得到黄色透明的TiO2溶胶,将TiO2溶胶在室温下陈化15h;At room temperature, in parts by volume, fully dissolve 15% butyl titanate in 45% absolute ethanol, then add 5% acetylacetone to obtain solution A, and fully mix 0.75% distilled water and 20% absolute ethanol to obtain a solution B. Gradually add solution B to solution A under the condition of constant stirring, then adjust the pH value to 5 with concentrated nitric acid, stir (120r/min) for 1h, add 1.5 polyethylene glycol, and then Under the condition of stirring (80r/min) 1.2h, obtain yellow transparent TiO sol, TiO sol is aged at room temperature for 15h;
(3)在海泡石表面包裹TiO2膜(3) Coating TiO 2 film on the surface of sepiolite
TiO2膜的层数为1层,每层TiO2膜的形成方法为:室温下,将海泡石加入到TiO2溶胶中,搅拌(100r/min)1.5h令海泡石与TiO2溶胶完全混合,然后在80℃的条件下烘干,烘干过程采用先水浴蒸至近干,再用干燥箱烘干,最后置于马弗炉中在450℃的条件下煅烧2h,冷却后备用;The number of layers of TiO 2 film is 1 layer, and the formation method of each layer of TiO 2 film is: at room temperature, add sepiolite to TiO 2 sol, stir (100r/min) for 1.5h to make sepiolite and TiO 2 sol Mix completely, and then dry at 80°C. During the drying process, first steam in a water bath until it is nearly dry, then dry in a drying oven, and finally place it in a muffle furnace for calcination at 450°C for 2 hours, and cool it for later use;
(4)在TiO2膜表面负载NiFe2O4颗粒(4) Loading NiFe 2 O 4 particles on the surface of TiO 2 film
室温下,按重量份,将2.91的Ni(NO3)2·6H2O和8.08的Fe(NO3)3·9H2O加入到55.3的无水乙醇中,磁力搅拌(80r/min)30min,用15mol/L的NaOH溶液将pH值调至10,然后加入包裹有TiO2膜的海泡石,搅拌(120r/min)60min,然后在160℃的条件下反应24h,冷却后进行固液分离、水洗,最后在85℃的条件下烘干,即得所述的NiFe2O4/TiO2/海泡石复合光催化剂。At room temperature, by weight, 2.91 Ni(NO 3 ) 2 ·6H 2 O and 8.08 Fe(NO 3 ) 3 ·9H 2 O were added to 55.3% absolute ethanol, magnetically stirred (80r/min) for 30min , use 15mol/L NaOH solution to adjust the pH value to 10, then add sepiolite wrapped with TiO 2 film, stir (120r/min) for 60min, then react at 160°C for 24h, cool and perform solid-liquid Separation, washing with water, and finally drying at 85° C. to obtain the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst.
实施例3Example 3
一种NiFe2O4/TiO2/海泡石复合光催化剂,成分包括海泡石、TiO2和NiFe2O4,海泡石为载体,TiO2以膜的形式包裹在海泡石表面,NiFe2O4以颗粒的形式负载在TiO2表面,其中Ni的含量为2wt%、Fe的含量为3.8wt%、Ti的含量为18wt%,余分为海泡石。A NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst, the composition includes sepiolite, TiO 2 and NiFe 2 O 4 , sepiolite is used as a carrier, TiO 2 is wrapped on the surface of sepiolite in the form of a film, NiFe 2 O 4 is supported on the surface of TiO 2 in the form of particles, in which the content of Ni is 2wt%, that of Fe is 3.8wt%, that of Ti is 18wt%, and the rest is sepiolite.
上述NiFe2O4/TiO2/海泡石复合光催化剂的制备方法,包括以下步骤:The preparation method of the above-mentioned NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst comprises the following steps:
(1)海泡石的预处理(1) Pretreatment of sepiolite
将海泡石粉碎成末,置于浓度为15%的稀硝酸中浸泡24h,过滤、用水漂洗至中性后烘干,然后置于马弗炉中在500℃的温度下煅烧2h,用水漂洗并将漂浮于水体中上部位的海泡石过滤出来,干燥后筛取粒径为125目的海泡石粉末作为载体;Grind sepiolite into powder, soak in dilute nitric acid with a concentration of 15% for 24 hours, filter, rinse with water until neutral, then dry, then place in a muffle furnace for calcination at 500°C for 2 hours, rinse with water And the sepiolite floating in the middle and upper part of the water body is filtered out, and after drying, the sepiolite powder with a particle size of 125 objects is sieved as a carrier;
(2)TiO2溶胶的制备(2) Preparation of TiO 2 sol
室温下,按体积份,将20的钛酸丁酯充分溶解于50的无水乙醇中,然后加入6的乙酰丙酮,得到溶液A,将1.0的蒸馏水和23的无水乙醇充分混合后得到溶液B,在不断搅拌的条件下将溶液B逐渐加入到溶液A中,然后用浓盐酸将pH值调至4.5,搅拌(100r/min)2h,加入1的聚乙二醇,然后在40℃的条件下搅拌(120r/min)1.5h,得到黄色透明的TiO2溶胶,将TiO2溶胶在室温下陈化13h;At room temperature, in parts by volume, fully dissolve 20% butyl titanate in 50% absolute ethanol, then add 6% acetylacetone to obtain solution A, and fully mix 1.0% distilled water and 23% absolute ethanol to obtain a solution B. Gradually add solution B to solution A under the condition of constant stirring, then adjust the pH value to 4.5 with concentrated hydrochloric acid, stir (100r/min) for 2h, add 1 polyethylene glycol, and then Stirring (120r/min) for 1.5h under the condition to obtain a yellow transparent TiO sol, the TiO sol was aged at room temperature for 13h;
(3)在海泡石表面包裹TiO2膜(3) Coating TiO 2 film on the surface of sepiolite
TiO2膜的层数为3层,每层TiO2膜的形成方法为:室温下,将海泡石加入到TiO2溶胶中,搅拌(120r/min)1h令海泡石与TiO2溶胶完全混合,然后在85℃的条件下烘干,烘干过程采用先水浴蒸至近干,再用干燥箱烘干,最后置于马弗炉中在400℃的条件下煅烧3h,冷却后备用;The number of layers of the TiO 2 film is 3 layers, and the formation method of each layer of TiO 2 film is: at room temperature, add sepiolite to the TiO 2 sol, stir (120r/min) for 1 hour to make the sepiolite and TiO 2 sol completely Mix and then dry at 85°C. During the drying process, first steam in a water bath until nearly dry, then dry in a drying oven, and finally place it in a muffle furnace for calcination at 400°C for 3 hours, and cool it for later use;
(4)在TiO2膜表面负载NiFe2O4颗粒(4) Loading NiFe 2 O 4 particles on the surface of TiO 2 film
室温下,按重量份,将5.82的Ni(NO3)2·6H2O和16.16的Fe(NO3)3·9H2O加入到63.2的无水乙醇中,磁力搅拌(100r/min)60min,用20mol/L的NaOH溶液将pH值调至9,然后加入包裹有TiO2膜的海泡石,搅拌(80r/min)45min,然后在170℃的条件下反应18h,冷却后进行固液分离、水洗,最后在80℃的条件下烘干,即得所述的NiFe2O4/TiO2/海泡石复合光催化剂。At room temperature, in parts by weight, add 5.82 g of Ni(NO 3 ) 2 ·6H 2 O and 16.16 g of Fe(NO 3 ) 3 ·9H 2 O into 63.2 g of absolute ethanol, and magnetically stir (100r/min) for 60 min , use 20mol/L NaOH solution to adjust the pH value to 9, then add sepiolite wrapped with TiO 2 film, stir (80r/min) for 45min, then react at 170°C for 18h, cool and perform solid-liquid Separation, washing with water, and finally drying at 80° C. to obtain the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst.
实施例4Example 4
对本发明实施例1所得的NiFe2O4/TiO2/海泡石复合光催化剂(以下简称为NiFe2O4/TiO2/海泡石)进行电镜扫描、固体紫外-可见光谱图测试和红外光谱测试,测试结果见图1、图2和图3。The NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst (hereinafter referred to as NiFe 2 O 4 /TiO 2 /sepiolite) obtained in Example 1 of the present invention is subjected to electron microscope scanning, solid ultraviolet-visible spectrum test and infrared Spectrum test, the test results are shown in Figure 1, Figure 2 and Figure 3.
图1左侧为本发明实施例1中在海泡石表面包裹TiO2膜后的扫描电镜图,右侧为NiFe2O4/TiO2/海泡石的扫描电镜图,从图1可看出,海泡石经过改性后成片状,表面积大,TiO2在海泡石表面形成了膜,TiO2膜表面负载有颗粒状的NiFe2O4,因此本发明有利于增大比表面积、吸附性能和光催化活性。The left side of Fig. 1 is the scanning electron micrograph after wrapping TiO 2 film on the surface of sepiolite in Example 1 of the present invention, and the right side is the scanning electron micrograph of NiFe 2 O 4 /TiO 2 / sepiolite, as can be seen from Fig. 1 It can be seen that sepiolite becomes flakes after modification, and has a large surface area. TiO 2 forms a film on the surface of sepiolite, and the surface of the TiO 2 film is loaded with granular NiFe 2 O 4 , so the present invention is conducive to increasing the specific surface area. , adsorption performance and photocatalytic activity.
图2中a为现有TiO2/海泡石负载型光催化剂(以下简称为TiO2/海泡石)的固体紫外-可见光谱图,b为NiFe2O4/TiO2/海泡石的固体紫外-可见光谱图,从图2可看出,TiO2具有较宽的禁带宽度(3.2eV),TiO2/海泡石的禁带宽度降低为3.18eV,而NiFe2O4/TiO2/海泡石的禁带宽度进一步降低为2.85eV,表明本发明所得的NiFe2O4/TiO2/海泡石复合光催化剂对可见光具有更好的催化活性,从而提高对可见光的利用效率。从图2中还可看出本发明所得的NiFe2O4/TiO2/海泡石复合光催化剂的光响应范围已扩展至可见光区域。Among Fig. 2, a is the solid ultraviolet-visible spectrum figure of existing TiO 2 /sepiolite supported photocatalyst (hereinafter referred to as TiO 2 / sepiolite), b is NiFe 2 O 4 /TiO 2 / sepiolite Solid ultraviolet-visible spectrum, as can be seen from Figure 2, TiO 2 has a wider band gap (3.2eV), and the band gap of TiO 2 / sepiolite is reduced to 3.18eV, while NiFe 2 O 4 /TiO 2 / The bandgap of sepiolite is further reduced to 2.85eV, indicating that the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst obtained in the present invention has better catalytic activity for visible light, thereby improving the utilization efficiency of visible light . It can also be seen from Fig. 2 that the photoresponse range of the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst obtained in the present invention has been extended to the visible light region.
图3中a为海泡石的红外光谱图,b为NiFe2O4/TiO2/海泡石的红外光谱图,在600-800cm-1时,NiFe2O4/TiO2/海泡石与海泡石的红外光谱图相比较,668cm-1处的吸收峰变弱,755cm-1处的Si-O外吸收峰消失,这是因为NiFe2O4/TiO2/海泡石中的Ti-O的缘故。1029cm-1处的Si-O内的伸缩振动峰强度基本保持不变。3570cm-1处的游离的O-H的吸收峰消失,且535cm-1处的Si-O-Mg的吸收峰减弱,说明海泡石中的镁可能被取代,可能使得Si-O桥倒-Si增多,从而导致孔隙增多,吸附量变大。In Figure 3, a is the infrared spectrum of sepiolite, b is the infrared spectrum of NiFe 2 O 4 /TiO 2 /sepiolite, at 600-800cm -1 , NiFe 2 O 4 /TiO 2 /sepiolite Compared with the infrared spectrum of sepiolite, the absorption peak at 668cm -1 becomes weaker, and the external absorption peak of Si-O at 755cm -1 disappears, this is because the NiFe 2 O 4 /TiO 2 /sepiolite Ti-O's sake. The intensity of the stretching vibration peak within Si-O at 1029 cm remains basically unchanged. The absorption peak of free OH at 3570cm -1 disappears, and the absorption peak of Si-O-Mg at 535cm -1 weakens, indicating that the magnesium in sepiolite may be replaced, which may increase the Si-O bridge inverted -Si , resulting in more pores and larger adsorption capacity.
实施例5Example 5
本发明实施例1所得的NiFe2O4/TiO2/海泡石复合光催化剂的光催化降解亚甲基蓝溶液效果测试Photocatalytic degradation of methylene blue solution effect test of NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst obtained in Example 1 of the present invention
反应起始条件:亚甲基蓝起始浓度50mg/L,催化剂用量0.4g,pH=5,将其在紫外光催化反应器下进行降解实验,降解时间为60min,每隔10min取样进行可见光分光光度计测定其吸光度,测量亚甲基蓝降解效率。测试结果如图4所示,可以看出,本发明实施例1所得的NiFe2O4/TiO2/海泡石复合光催化剂在60min时降解效率即可达到85.56%,而现有的TiO2/海泡石负载型光催化剂和CoFe2O4-TiO2掺杂光催化剂在相同的条件下降解效率一般只能达到70%左右。Reaction initial conditions: the initial concentration of methylene blue is 50mg/L, the amount of catalyst is 0.4g, pH=5, it is subjected to a degradation experiment under the ultraviolet photocatalytic reactor, the degradation time is 60min, and samples are taken every 10min for visible light spectrophotometer measurement Its absorbance measures the methylene blue degradation efficiency. The test results are shown in Figure 4. It can be seen that the degradation efficiency of the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst obtained in Example 1 of the present invention can reach 85.56% in 60 minutes, while the existing TiO 2 The degradation efficiency of sepiolite supported photocatalyst and CoFe 2 O 4 -TiO 2 doped photocatalyst can only reach about 70% under the same conditions.
实施例6Example 6
现有TiO2/海泡石负载型光催化剂、现有CoFe2O4-TiO2掺杂光催化剂和本发明实施例1所得的NiFe2O4/TiO2/海泡石复合光催化剂的光催化降解亚甲基蓝溶液效果比较Photocatalysts of the existing TiO 2 /sepiolite supported photocatalyst, the existing CoFe 2 O 4 -TiO 2 doped photocatalyst and the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst obtained in Example 1 of the present invention Comparison of Catalytic Degradation of Methylene Blue Solution
实验条件:催化剂用量1.0g,亚甲基蓝起始浓度4mg/L,pH=5,并在可见光催化反应器下进行降解实验,降解时间为120min,每隔20min取样进行测定其吸光度,计算亚甲基蓝降解效率,试验结果如表1所示,从表1可以看出本发明实施例1所得的NiFe2O4/TiO2/海泡石复合光催化剂的吸光度和降解率上均明显优于现有TiO2/海泡石负载型光催化剂和现有CoFe2O4-TiO2掺杂光催化剂,这表明本发明NiFe2O4/TiO2/海泡石复合光催化剂在可见光下也具有较好的光催化降解效果,而现有的现有TiO2/海泡石负载型光催化剂和现有CoFe2O4-TiO2掺杂光催化剂在可见光下的光催化降解效果极差,几乎没有响应。Experimental conditions: Catalyst dosage 1.0g, methylene blue initial concentration 4mg/L, pH=5, and the degradation experiment was carried out under the visible light catalytic reactor, the degradation time was 120min, the absorbance was measured by sampling every 20min, and the degradation efficiency of methylene blue was calculated. The test results are shown in Table 1. It can be seen from Table 1 that the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst obtained in Example 1 of the present invention has significantly better absorbance and degradation rate than the existing TiO 2 /Sepiolite composite photocatalyst. Sepiolite supported photocatalyst and existing CoFe 2 O 4 -TiO 2 doped photocatalyst, which shows that the NiFe 2 O 4 /TiO 2 /sepiolite composite photocatalyst of the present invention also has better photocatalysis under visible light However, the existing existing TiO 2 /sepiolite-supported photocatalysts and existing CoFe 2 O 4 -TiO 2 doped photocatalysts have extremely poor photocatalytic degradation effects under visible light, with almost no response.
表1Table 1
应当理解本文所述的例子和实施方式仅为了说明,本领域技术人员可根据它做出各种修改或变化,在不脱离本发明精神实质的情况下,都属于本发明的保护范围。It should be understood that the examples and implementations described herein are for illustration only, and those skilled in the art can make various modifications or changes based on them, all of which belong to the protection scope of the present invention without departing from the spirit of the present invention.
Claims (4)
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201510233949.0A CN104801308B (en) | 2015-05-08 | 2015-05-08 | A kind of NiFe2O4/TiO2/sepiolite composite photocatalyst and its preparation method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN201510233949.0A CN104801308B (en) | 2015-05-08 | 2015-05-08 | A kind of NiFe2O4/TiO2/sepiolite composite photocatalyst and its preparation method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN104801308A true CN104801308A (en) | 2015-07-29 |
| CN104801308B CN104801308B (en) | 2017-03-15 |
Family
ID=53686752
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN201510233949.0A Expired - Fee Related CN104801308B (en) | 2015-05-08 | 2015-05-08 | A kind of NiFe2O4/TiO2/sepiolite composite photocatalyst and its preparation method |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN104801308B (en) |
Cited By (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105562017A (en) * | 2016-01-24 | 2016-05-11 | 上海应用技术学院 | A kind of preparation method of NiFe2O4/SnO2 composite photocatalyst |
| CN106268300A (en) * | 2016-08-26 | 2017-01-04 | 吴伟堂 | A kind of preparation method of air purifying preparation |
| CN107020099A (en) * | 2017-04-25 | 2017-08-08 | 河北工业大学 | The preparation method of load type metal Raney nickel |
| CN109453779A (en) * | 2018-11-21 | 2019-03-12 | 湘潭大学 | A kind of TiO2The preparation method and application of the sepiolite supported type nickel-base catalyst of modification |
| CN109529864A (en) * | 2018-11-14 | 2019-03-29 | 浙江海洋大学 | A kind of α-Fe2O3/Bi2WO6/ shell composite photo-catalyst and preparation method thereof |
| CN109939720A (en) * | 2019-04-18 | 2019-06-28 | 辽宁大学 | A magnetic Ce/N co-doped TiO2/diatomite composite photocatalyst and its preparation method and application |
Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4083709A (en) * | 1977-01-07 | 1978-04-11 | Corning Glass Works | Method for making glass-ceramics with ferrimagnetic surfaces |
| CN102500378A (en) * | 2011-11-03 | 2012-06-20 | 东华大学 | Preparation method for magnetically separable photo-catalyst nanospheres of egg-like structure |
| CN103212393A (en) * | 2013-04-26 | 2013-07-24 | 长江水利委员会长江科学院 | Nano TiO2/montmorillonite composite photocatalytic water treatment material and preparation method thereof |
| CN104128184A (en) * | 2014-06-24 | 2014-11-05 | 安徽理工大学 | A floating type CoFe2O4/TiO2/floating bead composite photocatalyst and its preparation method |
-
2015
- 2015-05-08 CN CN201510233949.0A patent/CN104801308B/en not_active Expired - Fee Related
Patent Citations (4)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US4083709A (en) * | 1977-01-07 | 1978-04-11 | Corning Glass Works | Method for making glass-ceramics with ferrimagnetic surfaces |
| CN102500378A (en) * | 2011-11-03 | 2012-06-20 | 东华大学 | Preparation method for magnetically separable photo-catalyst nanospheres of egg-like structure |
| CN103212393A (en) * | 2013-04-26 | 2013-07-24 | 长江水利委员会长江科学院 | Nano TiO2/montmorillonite composite photocatalytic water treatment material and preparation method thereof |
| CN104128184A (en) * | 2014-06-24 | 2014-11-05 | 安徽理工大学 | A floating type CoFe2O4/TiO2/floating bead composite photocatalyst and its preparation method |
Cited By (10)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| CN105562017A (en) * | 2016-01-24 | 2016-05-11 | 上海应用技术学院 | A kind of preparation method of NiFe2O4/SnO2 composite photocatalyst |
| CN105562017B (en) * | 2016-01-24 | 2018-03-20 | 上海应用技术学院 | A kind of NiFe2O4/SnO2The preparation method of composite photo-catalyst |
| CN106268300A (en) * | 2016-08-26 | 2017-01-04 | 吴伟堂 | A kind of preparation method of air purifying preparation |
| CN107020099A (en) * | 2017-04-25 | 2017-08-08 | 河北工业大学 | The preparation method of load type metal Raney nickel |
| CN107020099B (en) * | 2017-04-25 | 2019-03-22 | 河北工业大学 | The preparation method of load type metal Raney nickel |
| CN109529864A (en) * | 2018-11-14 | 2019-03-29 | 浙江海洋大学 | A kind of α-Fe2O3/Bi2WO6/ shell composite photo-catalyst and preparation method thereof |
| CN109529864B (en) * | 2018-11-14 | 2021-06-18 | 浙江海洋大学 | A kind of α-Fe2O3/Bi2WO6/shell composite photocatalyst and preparation method thereof |
| CN109453779A (en) * | 2018-11-21 | 2019-03-12 | 湘潭大学 | A kind of TiO2The preparation method and application of the sepiolite supported type nickel-base catalyst of modification |
| CN109453779B (en) * | 2018-11-21 | 2021-07-20 | 湘潭大学 | Preparation method and application of a TiO2 modified sepiolite supported nickel-based catalyst |
| CN109939720A (en) * | 2019-04-18 | 2019-06-28 | 辽宁大学 | A magnetic Ce/N co-doped TiO2/diatomite composite photocatalyst and its preparation method and application |
Also Published As
| Publication number | Publication date |
|---|---|
| CN104801308B (en) | 2017-03-15 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| CN104801308B (en) | A kind of NiFe2O4/TiO2/sepiolite composite photocatalyst and its preparation method | |
| CN104128184B (en) | A kind of float type CoFe2O4/TiO2/ float bead composite photochemical catalyst and preparation method thereof | |
| CN106914264B (en) | Preparation method of composite visible light catalyst | |
| CN102335602B (en) | Bismuth tungstate composite photocatalyst, preparation method thereof, and application thereof | |
| CN101537355B (en) | Activated carbon fiber supported iron-doped titanium dioxide photocatalyst and preparation method thereof | |
| CN111229285B (en) | ZnO/TiO 2 /g-C 3 N 4 Composite photocatalyst and preparation method thereof | |
| CN103977780B (en) | Two one-step hydrothermals prepare mesoporous carbon-loaded TiO 2the method of catalysis material | |
| CN110152710B (en) | High-stability TiO2nanobelt-RGO-porous carbon nitride composite photocatalyst and preparation method thereof | |
| CN105854906A (en) | BiOCl-TiO2/diatomite photocatalyst and its preparation method | |
| CN106492885B (en) | A kind of preparation method of GNs/CoPcS/TiO2 photocatalyst | |
| CN110038592A (en) | A kind of Ce2S3/TiO2The preparation method of nanometer sheet compound photochemical catalyst | |
| CN108620113B (en) | Preparation method of nitrogen-doped carbon-cerium composite nanosheet | |
| CN102350354A (en) | Magnetically supported titanium dioxide photocatalyst and preparation method thereof | |
| CN104588004A (en) | Catalyst for ultraviolet photocatalytic degradation of organic pollutants and preparation method thereof | |
| CN108325554A (en) | A kind of pucherite/graphite phase carbon nitride composite material, preparation method and the usage | |
| CN103861593B (en) | A kind of chromium-silver co-doped nano-TiO2 photocatalyst and its preparation method and application | |
| CN102600865B (en) | Photocatalyst for degrading organic dye waste water pollutants and preparation method thereof | |
| CN104324713B (en) | Photocatalyst of a graphene-bismuth titanate composite | |
| CN102302940A (en) | Preparation method of a new photocatalyst S-doped SiO2/TiO2 composite material | |
| CN103657628B (en) | A kind of SnO 2-TiO 2the preparation method of compound nanometer photocatalyst | |
| CN101574668A (en) | Method for preparing composite photocatalyst for photocatalysis degradation of pollutants in waste water under natural light | |
| CN103212409B (en) | A porous carbon material loaded mesoporous TiO2-Ag composite and its preparation process | |
| CN107983336A (en) | A kind of praseodymium doped bismuth tungstate light urges agent and preparation method thereof | |
| CN111298792A (en) | Fe-doped TiO2/diatomite composite photocatalyst and preparation method and application thereof | |
| CN104098134A (en) | A kind of preparation method and application of amorphous layer-coated TiO2 nanotubes |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| C06 | Publication | ||
| PB01 | Publication | ||
| EXSB | Decision made by sipo to initiate substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| C14 | Grant of patent or utility model | ||
| GR01 | Patent grant | ||
| CF01 | Termination of patent right due to non-payment of annual fee |
Granted publication date: 20170315 Termination date: 20190508 |
|
| CF01 | Termination of patent right due to non-payment of annual fee |