CN105032342A - Preparation method of stratiform bimetallic oxide sorbent capable of effectively removing low-concentrated phosphate radical - Google Patents
Preparation method of stratiform bimetallic oxide sorbent capable of effectively removing low-concentrated phosphate radical Download PDFInfo
- Publication number
- CN105032342A CN105032342A CN201510339972.8A CN201510339972A CN105032342A CN 105032342 A CN105032342 A CN 105032342A CN 201510339972 A CN201510339972 A CN 201510339972A CN 105032342 A CN105032342 A CN 105032342A
- Authority
- CN
- China
- Prior art keywords
- layered
- metal oxide
- dmf
- preparation
- bmimpf
- 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
- Solid-Sorbent Or Filter-Aiding Compositions (AREA)
Abstract
本发明公开了一种有效去除低浓度磷酸根的层状双金属氧化物吸附剂制备方法及其应用。本发明首先在以疏水性离子液体BmimPF6为油相,以N,N-二甲基甲酰胺(DMF)为助溶剂的BmimPF6/DMF/H2O离子液体包水反相无表面活性剂微乳液体系中,采用双微乳液共沉淀法方法制备小粒径超薄层状双金属氢氧化物纳米片前驱体,然后在空气气氛中500℃高温将其煅烧,制备层状双金属氧化物吸附剂。所得层状双金属氧化物的比表面积为107.36~158.46m2/g,孔径为8.56~11.17nm,孔容为0.358~0.468cm3/g;在水介质中能恢复形成粒径为150~200nm、厚度约为5nm、粒径分布均一的层状双金属氢氧化物纳米片;其对低浓度磷酸根的吸附率远高于其前驱体层状双金属氢氧化物和传统共沉淀法制备的大颗粒类水滑石。
The invention discloses a preparation method and application of a layered double metal oxide adsorbent for effectively removing low-concentration phosphate radicals. In the present invention, the BmimPF 6 /DMF/H 2 O ionic liquid water-in-water reversed phase without surfactant is firstly used as the oil phase of the hydrophobic ionic liquid BmimPF 6 and N,N-dimethylformamide (DMF) as the co-solvent In the microemulsion system, the double microemulsion co-precipitation method is used to prepare the small particle size ultra-thin layered double metal hydroxide nanosheet precursor, and then it is calcined at a high temperature of 500 ° C in the air atmosphere to prepare the layered double metal oxide Adsorbent. The specific surface area of the obtained layered double metal oxide is 107.36-158.46m 2 /g, the pore diameter is 8.56-11.17nm, and the pore volume is 0.358-0.468cm 3 /g; it can be recovered in an aqueous medium to form a particle size of 150-200nm , layered double metal hydroxide nanosheets with a thickness of about 5nm and uniform particle size distribution; its adsorption rate for low-concentration phosphate is much higher than that prepared by its precursor layered double hydroxide and traditional co-precipitation method Large particle hydrotalcite.
Description
技术领域:Technical field:
本发明涉及一种有效去除低浓度磷酸根的层状双金属氧化物吸附剂制备方法,以及本发明涉及制备方法所得层状双金属氧化物吸附剂对水体中低浓度磷酸根的吸附应用,属于纳米材料领域。The invention relates to a method for preparing a layered double metal oxide adsorbent that can effectively remove low-concentration phosphate radicals, and the application of the layered double metal oxide adsorbent obtained by the preparation method to adsorb low-concentration phosphate radicals in water bodies, belonging to field of nanomaterials.
背景技术:Background technique:
随着工农业现代化的发展,大量氮、磷等营养物质随污水进入水体,使得近海和湖泊水体出现富营养化,引起藻类及其它浮游生物迅速繁殖,造成水体水质恶化、水生生物大量死亡等后果,不但破坏生态系统,而且产生的毒素会通过食物链威胁人类健康。研究表明磷是水体富营养化的关键控制因素,当其浓度高于0.03mg/L时,水体的富营养化就会导致赤潮或水华发生。因此,有效降低排放废水中磷的含量对抑制水体富营养化、预防赤潮或水华发生具有重要意义。国内外废水除磷的方法主要有生物法、吸附法、化学沉淀法、结晶法和离子交换法、以及生态法等,其中吸附法因其具有设备简单、操作简便、不产生二次污染等优点,倍受青睐,而粘土矿物因其具有独特的层状结构、大的比表面积、良好的吸附和离子交换性能,且储量丰富、价格低廉、对环境无毒无害、容易再生,已作为新型高效的吸附材料在废水除磷领域得到了广泛应用[ZhouJ,YangS,YuJ,ShuZ.Novelhollowmicrospheresofhierarchicalzinc–aluminumlayereddoublehydroxidesandtheirenhancedadsorptioncapacityforphosphateinwater.J.Hazard.Mater.2011,192,1114–1121.]。With the development of industrial and agricultural modernization, a large amount of nutrients such as nitrogen and phosphorus enter the water body with the sewage, causing eutrophication in the water body of the coastal waters and lakes, causing the rapid reproduction of algae and other plankton, resulting in the deterioration of the water quality and the death of a large number of aquatic organisms. Not only will it destroy the ecosystem, but the toxins produced will threaten human health through the food chain. Studies have shown that phosphorus is the key controlling factor of water eutrophication. When its concentration is higher than 0.03mg/L, the eutrophication of water body will lead to red tide or algal bloom. Therefore, it is of great significance to effectively reduce the phosphorus content in the discharged wastewater to inhibit the eutrophication of the water body and prevent the occurrence of red tide or algal bloom. Domestic and foreign wastewater phosphorus removal methods mainly include biological methods, adsorption methods, chemical precipitation methods, crystallization methods, ion exchange methods, and ecological methods, among which the adsorption method has the advantages of simple equipment, easy operation, and no secondary pollution. , is very popular, and clay minerals have been used as a new type because of their unique layered structure, large specific surface area, good adsorption and ion exchange properties, abundant reserves, low price, non-toxic and harmless to the environment, and easy regeneration. Efficient adsorbent materials have been widely used in the field of phosphorus removal from wastewater [ZhouJ, YangS, YuJ, ShuZ.
层状双金属氢氧化物(LayeredDoubleHydroxides,LDH)是一类阴离子粘土,其通式为[M1-x 2+Mx 3+(OH)2]x+(An-)x/n·mH2O,其中M(OH)6八面体共用棱而呈现开放的片层堆积结构,每个八面体单元由六配位的中心金属离子M和位于顶点的OH-形成。由于部分M2+被M3+取代会使片层带结构正电荷,层间存在可交换的阴离子使电荷达到平衡。LDH层间的接合力较弱,夹层空间富有弹性,具有较大的表面积、较高的离子交换容量和优良的热稳定性等特点,对有机和无机阴离子表现出很强的捕获能力。然而LDH在400~800℃煅烧后可产生非化学计量的层状双金属氧化物(LDO),由于LDH的“记忆效应”,煅烧产物LDO在含有污染物的水溶液中发生水合,重新恢复LDH的过程中将阴离子污染物插入层间,因而具有更高的吸附容量[CaiP,ZhengH,WangC,MaH,HuJ,PuY,LiangP.CompetitiveadsorptioncharacteristicsoffluorideandphosphateoncalcinedMg-Al-CO3layereddoublehydroxides.J.Hazard.Mater.2012,213-214,100-108.]。目前LDH和LDO已成功用于排放废水、海水中磷酸银的去除。但是常规法制备所得的LDH粒径较大且形貌不可控,而且使用时容易发生聚集,得到的煅烧产物LDO对污染物的吸附性能并没有得到充分发挥,因此,提高前驱体LDH的表面积、增加吸附位点和吸附容量,对开发高效LDO吸附剂有着重要的意义。Layered double hydroxides (Layered Double Hydroxides, LDH) is a kind of anionic clay, its general formula is [M 1-x 2+ M x 3+ (OH) 2 ] x+ (A n- ) x/n mH 2 O, where the M(OH) 6 octahedra share edges and present an open sheet-packed structure, and each octahedral unit is formed by a six-coordinated central metal ion M and OH- at the apex. Since part of M 2+ is replaced by M 3+ , the sheet will be positively charged, and there are exchangeable anions between the layers to balance the charge. LDH has weak bonding force between layers, elastic interlayer space, large surface area, high ion exchange capacity and excellent thermal stability, and shows strong capture ability for organic and inorganic anions. However, LDH can produce non-stoichiometric layered double metal oxide (LDO) after calcination at 400-800 ° C. Due to the "memory effect" of LDH, the calcined product LDO will be hydrated in the aqueous solution containing pollutants, and the LDH will be restored. During the process, anionic pollutants are intercalated between layers, thus having a higher adsorption capacity [CaiP, ZhengH, WangC, MaH, HuJ, PuY , LiangP. 214, 100-108.]. At present, LDH and LDO have been successfully used for the removal of silver phosphate in wastewater and seawater. However, the LDH prepared by the conventional method has a large particle size and uncontrollable shape, and is prone to aggregation during use, and the obtained calcined product LDO has not fully exerted its adsorption performance on pollutants. Therefore, increasing the surface area of the precursor LDH, Increasing the adsorption sites and adsorption capacity is of great significance for the development of efficient LDO adsorbents.
反相微乳液通常是无数的“微小水滴”分散在连续油相中,形成的各向同性、透明和热力学稳定的分散体系,由水、油、表面活性剂和助表面活性剂等组分以适当比例组成。这些稳定的彼此分离的每一个“微小水滴”都是一个微反应器,拥有很大的界面,其可调的大小不仅能够控制纳米粒子的成核和生长,而且还能控制粒子的大小,被认为是可控制备无机纳米粒子的优良介质。传统反相微乳液中都含有表面活性剂,采用它们制备的无机纳米粒子无一例外地都混有表面活性剂,特别是采用反相微乳液制备LDH时,表面活性剂会以阴离子形式插层到其层间,或吸附在层状材料的表面[HuG,O’HareD.Uniquelayereddoublehydroxidemorphologiesusingreversemicroemulsionsynthesis,J.Am.Chem.Soc.2005,127,17808-17813.],使所得吸附材料使用时会造成二次污染,而且也使吸附材料的再生过程异常繁琐,成本较高。Inverse microemulsion is usually an isotropic, transparent and thermodynamically stable dispersion system formed by numerous "tiny water droplets" dispersed in the continuous oil phase. Appropriate proportion composition. Each of these stable and separated "tiny water droplets" is a microreactor with a large interface, and its adjustable size can not only control the nucleation and growth of nanoparticles, but also control the particle size, which is It is considered to be an excellent medium for the controllable preparation of inorganic nanoparticles. Traditional inverse microemulsions contain surfactants, and the inorganic nanoparticles prepared by them are all mixed with surfactants without exception, especially when LDH is prepared by inverse microemulsions, the surfactants will intercalate in the form of anions Between layers, or adsorbed on the surface of layered materials [HuG, O'HareD. Uniquelayereddoublehydroxidemorphologiesusingreversemicroemulsionsynthesis, J.Am.Chem.Soc.2005, 127, 17808-17813.], so that the resulting adsorption material will cause secondary pollution, and the regeneration process of the adsorption material is extremely cumbersome and costly.
研究表明,在没有表面活性剂存在下,一些三组份体系也可形成微乳液,这类微乳液被称为无表面活性剂微乳液(Surfactant-freeMicroemulsion,SFME)。采用SFME体系制备LDH,不仅可以控制纳米粒子大小、粒径分布范围窄、提高分散性、得到的LDH粒子不存在杂质污染,而且组份简单、操作简便,从根本上解决传统微乳液制备LDH时存在的问题,同时也为制备高效LDO吸附剂提供了新的思路。但是,在以疏水性离子液体BmimPF6为油相,以N,N-二甲基甲酰胺(DMF)为助溶剂的BmimPF6/DMF/H2O离子液体包水反相SFME体系中先制备小粒径超薄LDH纳米片,然后再高温煅烧制备LDO,以及将其用于水体中低浓度磷酸根吸附的相关研究还未见报道。Studies have shown that in the absence of surfactants, some three-component systems can also form microemulsions, which are called surfactant-free microemulsions (SFME). Using the SFME system to prepare LDH can not only control the size of nanoparticles, narrow the particle size distribution range, improve dispersibility, and obtain LDH particles without impurity pollution, but also has simple components and easy operation, which fundamentally solves the problem of traditional microemulsion preparation of LDH. At the same time, it also provides a new idea for the preparation of high-efficiency LDO adsorbents. However, in the BmimPF 6 /DMF/H 2 O ionic liquid water-in-water reversed-phase SFME system with the hydrophobic ionic liquid BmimPF 6 as the oil phase and N,N-dimethylformamide (DMF) as the co-solvent There are no reports on the preparation of LDO by ultrathin LDH nanosheets with small particle size, followed by high-temperature calcination, and its use in the adsorption of low-concentration phosphate in water.
发明内容:Invention content:
针对现有技术的不足以及本领域研究和应用的需求,本发明的目的是提供一种有效去除低浓度磷酸根的层状双金属氧化物吸附剂制备方法。先在以疏水性离子液体BmimPF6为油相,以N,N-二甲基甲酰胺(DMF)为助溶剂的BmimPF6/DMF/H2O离子液体包水反相SFME体系中,以双微乳液共沉淀法方法制备小粒径超薄LDH纳米片,然后再500℃高温煅烧制备得到比表面积大、吸附性能高的层状双金属氧化物吸附剂。In view of the deficiencies of the prior art and the needs of research and application in this field, the purpose of the present invention is to provide a preparation method for a layered double metal oxide adsorbent that can effectively remove low-concentration phosphate. First, in the BmimPF 6 /DMF/H 2 O ionic liquid water-in-water reversed-phase SFME system with the hydrophobic ionic liquid BmimPF 6 as the oil phase and N,N-dimethylformamide (DMF) as the co-solvent, the bis The microemulsion co-precipitation method is used to prepare ultra-thin LDH nanosheets with small particle size, and then calcined at 500 ° C to prepare a layered bimetallic oxide adsorbent with large specific surface area and high adsorption performance.
本发明提供的一种层状双金属氧化物吸附剂的制备方法,是先采用双微乳液共沉淀法制备其前驱体层状双金属氢氧化物,然后再对其进行高温煅烧制备层状双金属氧化物,具体包括以下步骤:The preparation method of a layered double metal oxide adsorbent provided by the present invention is to prepare its precursor layered double metal hydroxide by double microemulsion co-precipitation method, and then perform high-temperature calcination to prepare layered double metal oxide adsorbent. Metal oxides, specifically comprising the following steps:
1)分别称取MgCl2·6H2O和AlCl3·9H2O,加入去离子水,配制总金属离子浓度为0.05~3.0mol/L的MgCl2和AlCl3的混合盐水溶液;向该混合盐溶液中加入N,N-二甲基甲酰胺DMF和疏水性离子液体BmimPF6,其中混合盐水溶液、DMF和BmimPF6的体积比为2~15:30~50:40~70,室温下磁力搅拌30~60min,待溶液由混浊变为透明,制备得到了反相微乳液A;1) Weigh MgCl 2 6H 2 O and AlCl 3 9H 2 O respectively, add deionized water to prepare a mixed salt solution of MgCl 2 and AlCl 3 with a total metal ion concentration of 0.05-3.0 mol/L; Add N,N-dimethylformamide DMF and hydrophobic ionic liquid BmimPF 6 into the salt solution, wherein the volume ratio of the mixed salt solution, DMF and BmimPF 6 is 2-15:30-50:40-70, and the magnetic force at room temperature Stir for 30-60 minutes, wait until the solution turns from turbid to transparent, and prepare the inverse microemulsion A;
2)取一定体积浓度为25%的氨水,向其中加入DMF和BmimPF6,其中25%的氨水、DMF和BmimPF6的体积比为2~15:30~50:40~70,室温下磁力搅拌30~60min,待溶液由混浊变为透明,制备得到了反相微乳液B;2) Take ammonia water with a certain volume concentration of 25%, add DMF and BmimPF 6 into it, wherein the volume ratio of 25% ammonia water, DMF and BmimPF 6 is 2-15:30-50:40-70, stir magnetically at room temperature 30-60min, when the solution turns from cloudy to transparent, the inverse microemulsion B is prepared;
3)在磁力搅拌条件下,将反相微乳液A和反相微乳液B同时滴定,控制pH在9.0~10.0之间,室温搅拌反应12h,之后在25~75℃条件下老化10~24h,所得浆液在10000rpm转速下离心10min,依次用DMF、无水乙醇和去离子水分别洗涤2次,60℃真空下干燥12小时,得前驱体小粒径超薄层状双金属氧化物纳米片;3) Under the condition of magnetic stirring, titrate the inverse microemulsion A and the inverse microemulsion B at the same time, control the pH between 9.0 and 10.0, stir and react at room temperature for 12 hours, and then age at 25 to 75°C for 10 to 24 hours, The resulting slurry was centrifuged at 10,000 rpm for 10 min, washed twice with DMF, absolute ethanol and deionized water in sequence, and dried under vacuum at 60°C for 12 hours to obtain the precursor small particle size ultra-thin layered double metal oxide nanosheets;
4)将步骤3)所得的前驱体小粒径超薄层状双金属氢氧化物纳米片干粉放入马弗炉中,于空气气氛中在500℃条件下煅烧3~8小时,得层状双金属氧化物吸附剂。4) Put the small particle size ultra-thin layered bimetallic hydroxide nanosheet dry powder of the precursor obtained in step 3) into a muffle furnace, and calcinate for 3 to 8 hours at 500°C in an air atmosphere to obtain a layered Bimetallic oxide adsorbents.
步骤1)中MgCl2和AlCl3混合盐溶液中金属离子的总浓度为0.45mol/L,MgCl2和AlCl3的摩尔比为2:1;所述水相为混合盐水溶液的反相微乳液A和水相为氨水溶液的反相微乳液B中水溶液、DMF和BmimPF6的体积比完全相等;步骤3)所得的前驱体小粒径超薄层状双金属氢氧化物纳米片的横向尺寸为10~35nm,平均厚度为0.71nm,由单层层状双金属氢氧化物片组成。In step 1) MgCl 2 and AlCl 3 The total concentration of metal ions in the mixed salt solution is 0.45mol/L, and the mol ratio of MgCl 2 and AlCl 3 is 2:1; the water phase is the inverse microemulsion of the mixed salt solution The volume ratio of aqueous solution, DMF and BmimPF 6 in the inverse microemulsion B that A and aqueous phase are ammonia solution are completely equal; Step 3) the transverse dimension of the precursor small particle diameter ultrathin layered double metal hydroxide nanosheet of gained It is 10-35nm, with an average thickness of 0.71nm, and is composed of single-layer layered double metal hydroxide sheets.
由上述制备方法制备出的层状双金属氧化物比表面积为107.36~158.46m2/g,孔径为8.56~11.17nm,孔容为0.358~0.468cm3/g。The specific surface area of the layered double metal oxide prepared by the above preparation method is 107.36-158.46m 2 /g, the pore diameter is 8.56-11.17nm, and the pore volume is 0.358-0.468cm 3 /g.
由上述制备方法制备所得的层状双金属氧化物吸附剂,在水介质中能恢复形成粒径为150~200nm、厚度约为5nm、粒径分布均一的层状双金属氢氧化物纳米片。The layered double metal oxide adsorbent prepared by the above preparation method can restore and form layered double metal hydroxide nanosheets with a particle size of 150-200 nm, a thickness of about 5 nm, and a uniform particle size distribution in an aqueous medium.
由上述制备方法制备所得的层状双金属氧化物吸附剂,适合于水体中低浓度磷酸根的吸附应用,所述的应用是将层状双金属氧化物吸附剂加入到磷酸根浓度为2mg/L的水溶液中,室温振荡反应5小时。The layered double metal oxide adsorbent prepared by the above preparation method is suitable for the adsorption application of low-concentration phosphate radicals in water bodies. L in aqueous solution, and shaken at room temperature for 5 hours.
本发明与现有技术相比,主要的有益效果和优点在于:Compared with the prior art, the present invention has main beneficial effects and advantages in that:
1)本发明所述的有效去除低浓度磷酸根的层状双金属氧化物吸附剂制备方法,解决了传统共沉淀法制备前驱体LDH时存在的聚集、粒径大、粒径分布范围宽、比表面积小等缺陷,呈现出了粒径小、粒径分布范围窄、比表面积大、片层薄、孔容小等特点,相应地,高温煅烧产物层状双金属氧化物具有比表面积大、吸附性能高的优点。1) The preparation method of the layered double metal oxide adsorbent that effectively removes low-concentration phosphate radicals of the present invention solves the problems of aggregation, large particle size, and wide particle size distribution range when the traditional co-precipitation method is used to prepare the precursor LDH. Defects such as small specific surface area show the characteristics of small particle size, narrow particle size distribution range, large specific surface area, thin sheet, and small pore volume. Correspondingly, the high-temperature calcined product layered bimetallic oxide has a large specific surface area, The advantage of high adsorption performance.
2)本发明所述的制备方法,在制备前驱体LDH时采用的三组份反相微乳液体系组分简单,不含表面活性剂,产物纯化时不存在去除表面活性剂的繁琐过程;前驱体LDH高温煅烧后即可制得层状双金属氧化物吸附剂,因此制备高效层状双金属氧化物吸附剂更加简单环保。2) In the preparation method of the present invention, the components of the three-component inverse microemulsion system used in the preparation of the precursor LDH are simple, do not contain surfactants, and there is no cumbersome process of removing surfactants during product purification; Layered bimetallic oxide adsorbents can be prepared after bulk LDH is calcined at high temperature, so the preparation of high-efficiency layered bimetallic oxide adsorbents is simpler and more environmentally friendly.
3)本发明所采用的反相微乳液体系为离子液体包水反相微乳液,相比于现有微乳液体系,更加符合绿色化学的要求。3) The inverse microemulsion system used in the present invention is water-in-ionic liquid inverse microemulsion, which is more in line with the requirements of green chemistry than the existing microemulsion system.
4)由本发明所述制备方法所得的层状双金属氧化物吸附剂,对水体中低浓度磷酸根的吸附性能大大优于LDH,并且制备方法操作简单、条件温和、成本低。4) The layered bimetallic oxide adsorbent obtained by the preparation method of the present invention has much better adsorption performance on low-concentration phosphate in water than LDH, and the preparation method is simple in operation, mild in conditions and low in cost.
附图说明:Description of drawings:
图1为实施例2、对比例1~3所得样品的XRD衍射图。Fig. 1 is the XRD diffractogram of the samples obtained in Example 2 and Comparative Examples 1-3.
图2为实施例2、对比例1~2所得样品的N2吸附脱附等温线和孔径分布图。Fig. 2 is the N2 adsorption-desorption isotherm and pore size distribution diagram of samples obtained in Example 2 and Comparative Examples 1-2.
图3为实施例2、对比例1~3所得样品的扫描电镜照片。Fig. 3 is the scanning electron micrograph of the samples obtained in Example 2 and Comparative Examples 1-3.
图4为实施例2所得层状双金属氧化物吸附剂的原子力显微镜照片(a)和a图中沿红色直线的横断面分析(b)。Figure 4 is the atomic force microscope photo (a) of the layered double metal oxide adsorbent obtained in Example 2 and the cross-sectional analysis (b) along the red straight line in the figure a.
具体实施方式:Detailed ways:
为进一步理解本发明,下面结合附图和实施例对本发明作进一步说明,但并不以任何方式限制本发明。In order to further understand the present invention, the present invention will be further described below in conjunction with the accompanying drawings and examples, but the present invention is not limited in any way.
实施例1:Example 1:
1)分别称取MgCl2·6H2O和AlCl3·9H2O,加入去离子水,配制总金属离子浓度为0.45mol/L,MgCl2和AlCl3的摩尔浓度比为2:1;向该混合盐溶液中加入N,N-二甲基甲酰胺(DMF)和疏水性离子液体BmimPF6,其中混合盐溶液、DMF和BmimPF6的体积比为4:48:48,室温下磁力搅拌40min,待溶液由混浊变为透明,制备得到了反相微乳液A;1) Weigh MgCl 2 6H 2 O and AlCl 3 9H 2 O respectively, add deionized water to prepare a total metal ion concentration of 0.45mol/L, and a molar concentration ratio of MgCl 2 and AlCl 3 of 2:1; Add N,N-dimethylformamide (DMF) and hydrophobic ionic liquid BmimPF 6 to the mixed salt solution, wherein the volume ratio of the mixed salt solution, DMF and BmimPF 6 is 4:48:48, and stir magnetically for 40 minutes at room temperature , when the solution turns from cloudy to transparent, an inverse microemulsion A is prepared;
2)取一定体积浓度为25%的氨水,向其中加入DMF和BmimPF6,使25%的氨水、DMF和BmimPF6的体积比为4:48:48,室温下磁力搅拌40min,待溶液由混浊变为透明,制备得到了反相微乳液B;2) Take a certain volume concentration of 25% ammonia water, add DMF and BmimPF 6 to it, make the volume ratio of 25% ammonia water, DMF and BmimPF 6 be 4:48:48, stir magnetically at room temperature for 40min, and wait until the solution becomes cloudy Become transparent, and the inverse microemulsion B has been prepared;
3)在磁力搅拌条件下,将反相微乳液A和反相微乳液B同时滴定,控制pH在9.0~10.0之间,室温搅拌反应12h,之后在75℃条件下老化24h,所得浆液在10000rpm转速下离心10min,依次用DMF、无水乙醇和去离子水分别洗涤2次,60℃真空下干燥12小时,得前驱体小粒径超薄层状双金属氧化物纳米片。3) Under the condition of magnetic stirring, titrate the inverse microemulsion A and the inverse microemulsion B at the same time, control the pH between 9.0 and 10.0, stir and react at room temperature for 12 hours, and then age at 75°C for 24 hours, and the obtained slurry is heated at 10000rpm Centrifuge at rotational speed for 10 min, wash with DMF, absolute ethanol and deionized water twice respectively, and dry under vacuum at 60°C for 12 hours to obtain the precursor small particle size ultrathin layered double metal oxide nanosheets.
4)将步骤3)所得的前驱体小粒径超薄层状双金属氢氧化物纳米片干粉放入马弗炉中,于空气气氛中在500℃条件下煅烧5小时,得层状双金属氧化物吸附剂,记为LDOa。4) Put the small particle size ultra-thin layered bimetallic hydroxide nanosheet dry powder of the precursor obtained in step 3) into a muffle furnace, and calcinate it in an air atmosphere at 500°C for 5 hours to obtain a layered bimetallic The oxide adsorbent is denoted as LDO a .
实施例2:Example 2:
1)参照实施例1步骤1)中的方法和制备条件,只改变混合盐溶液、DMF和BmimPF6的体积比为7:46.5:46.5,制备得到了反相微乳液A;1) Referring to the method and preparation conditions in step 1) of Example 1, only the volume ratio of the mixed salt solution, DMF and BmimPF 6 was changed to 7:46.5:46.5, and an inverse microemulsion A was prepared;
2)参照实施例1步骤2)中的方法和制备条件,只改变混合盐溶液、DMF和BmimPF6的体积比为7:46.5:46.5,制备得到了反相微乳液B;2) With reference to the method and preparation conditions in step 2) of Example 1, only the volume ratio of the mixed salt solution, DMF and BmimPF 6 was changed to 7:46.5:46.5, and an inverse microemulsion B was prepared;
3)采用实施例1步骤3)中的方法和制备条件,得到前驱体小粒径超薄类水滑石纳米片;3) Using the method and preparation conditions in step 3) of Example 1, the precursor small particle size ultra-thin hydrotalcite-like nanosheets are obtained;
4)采用实施例1步骤4)中的方法和制备条件,煅烧上步得到的前驱体小粒径超薄类水滑石纳米片,得层状双金属氧化物吸附剂,记为LDOb。4) Using the method and preparation conditions in Step 4) of Example 1, calcining the precursor small-size ultra-thin hydrotalcite-like nanosheets obtained in the previous step to obtain a layered bimetallic oxide adsorbent, denoted as LDO b .
实施例3:Example 3:
1)参照实施例1步骤1)中的方法和制备条件,只改变混合盐溶液、DMF和BmimPF6的体积比为7:31:62,制备得到了反相微乳液A;1) With reference to the method and preparation conditions in step 1) of Example 1, only the volume ratio of the mixed salt solution, DMF and BmimPF 6 was changed to 7:31:62, and an inverse microemulsion A was prepared;
2)参照实施例1步骤2)中的方法和制备条件,只改变混合盐溶液、DMF和BmimPF6的体积比为7:31:62,制备得到了反相微乳液B;2) With reference to the method and preparation conditions in step 2) of Example 1, only the volume ratio of the mixed salt solution, DMF and BmimPF 6 was changed to 7:31:62, and an inverse microemulsion B was prepared;
3)采用实施例1步骤3)中的方法和制备条件,得到前驱体小粒径超薄类水滑石纳米片;3) Using the method and preparation conditions in step 3) of Example 1, the precursor small particle size ultra-thin hydrotalcite-like nanosheets are obtained;
4)采用实施例1步骤4)中的方法和制备条件,煅烧上步得到的前驱体小粒径超薄类水滑石纳米片,得层状双金属氧化物吸附剂,记为LDOc。4) Using the method and preparation conditions in Step 4) of Example 1, calcining the precursor small-size ultra-thin hydrotalcite-like nanosheets obtained in the previous step to obtain a layered bimetallic oxide adsorbent, denoted as LDO c .
实施例4:Example 4:
1)采用实施例2步骤1)中的方法和制备条件,制备得到了反相微乳液A;1) The method and preparation conditions in Step 1) of Example 2 were adopted to prepare an inverse microemulsion A;
2)采用实施例2步骤2)中的方法和制备条件,制备得到了反相微乳液B;2) using the method and preparation conditions in step 2) of Example 2, an inverse microemulsion B was prepared;
3)采用实施例1步骤3)中的方法和制备条件,只是将老化时间减少到12h,得到前驱体小粒径超薄类水滑石纳米片;3) Adopt the method and preparation conditions in step 3) of Example 1, but reduce the aging time to 12h, and obtain the ultra-thin hydrotalcite-like nanosheets with a small particle size of the precursor;
4)采用实施例1步骤4)中的方法和制备条件,煅烧上步得到的前驱体小粒径超薄类水滑石纳米片,得层状双金属氧化物吸附剂,记为LDOd。4) Using the method and preparation conditions in Step 4) of Example 1, calcining the precursor small-size ultra-thin hydrotalcite-like nanosheets obtained in the previous step to obtain a layered bimetallic oxide adsorbent, denoted as LDO d .
实施例5:Example 5:
1)采用实施例2步骤1)中的方法和制备条件,制备得到了反相微乳液A;1) The method and preparation conditions in Step 1) of Example 2 were adopted to prepare an inverse microemulsion A;
2)采用实施例2步骤2)中的方法和制备条件,制备得到了反相微乳液B;2) using the method and preparation conditions in step 2) of Example 2, an inverse microemulsion B was prepared;
3)采用实施例1步骤3)中的方法和制备条件,只是将反应温度降低为25℃,得到前驱体小粒径超薄类水滑石纳米片。3) Adopt the method and preparation conditions in Step 3) of Example 1, except that the reaction temperature is lowered to 25° C. to obtain ultrathin hydrotalcite-like nanosheets of the precursor with small particle size.
4)采用实施例1步骤4)中的方法和制备条件,煅烧上步得到的前驱体小粒径超薄类水滑石纳米片,得层状双金属氧化物吸附剂,记为LDOe。4) Using the method and preparation conditions in Step 4) of Example 1, calcining the precursor small-size ultra-thin hydrotalcite-like nanosheets obtained in the previous step to obtain a layered bimetallic oxide adsorbent, denoted as LDO e .
对比例1:Comparative example 1:
1)分别称取MgCl2·6H2O和AlCl3·9H2O,加入去离子水,配制总金属离子浓度为0.45mol/L,MgCl2和AlCl3的摩尔浓度比为2:1,制备得到了溶液A;1) Weigh MgCl 2 6H 2 O and AlCl 3 9H 2 O respectively, add deionized water to prepare a total metal ion concentration of 0.45mol/L, and a molar concentration ratio of MgCl 2 and AlCl 3 of 2:1 to prepare Solution A is obtained;
2)浓度为25%(w/w)的氨水为溶液B;2) Aqueous ammonia with a concentration of 25% (w/w) is solution B;
3)在磁力搅拌条件下,将溶液A和溶液B同时滴定,控制pH在9.0~10.0之间,室温搅拌反应12h,之后在75℃条件下老化24h,所得浆液在10000rpm转速下离心10min,依次用DMF、无水乙醇和去离子水分别洗涤2次,60℃真空下干燥12小时,得到LDH。3) Under the condition of magnetic stirring, titrate solution A and solution B at the same time, control the pH between 9.0 and 10.0, stir and react at room temperature for 12 hours, and then age at 75°C for 24 hours, centrifuge the obtained slurry at 10000rpm for 10 minutes, and then Wash twice with DMF, absolute ethanol and deionized water, and dry under vacuum at 60°C for 12 hours to obtain LDH.
对比例2:Comparative example 2:
按照实施2中步骤1)~3)的方法和条件,制备得到前驱体小粒径超薄类水滑石纳米片,记为LDH-M。According to the method and conditions of steps 1) to 3) in Implementation 2, the precursor small particle size ultra-thin hydrotalcite-like nanosheets were prepared, which was denoted as LDH-M.
对比例3:Comparative example 3:
将实施例2所得的样品LDHb在去离子水中搅拌反应2小时,得到恢复的层状双金属氢氧化物,记为LDHr。The sample LDH b obtained in Example 2 was stirred and reacted in deionized water for 2 hours to obtain a recovered layered double metal hydroxide, which was denoted as LDH r .
图1是实施例2、对比例1~3所得样品的XRD结果图。图中LDH、LDH-M和LDHr三个样品均在低2θ处出现了类水滑石003、006、和009晶面三个特征衍射峰,其中LDH-M和LDHr与LDH样品特征峰相比,其峰宽明显变宽,强度明显变弱,说明采用本发明所述的双微乳液共沉淀法方法制备的前驱体LDH纳米片结晶度较低,由双金属氧化物水合恢复后其结晶度变低。三个样品的d003值在0.78~0.80nm之间,与Cl-LDH相当,它们的晶胞参数a和b(a=b=2d110)约为与文献值一致。衍射峰的宽度和强度很好地反映着样品的结晶度。在高2θ处三个样品也都出现了110和113衍射峰,但很明显LDH-M和LDHr与LDH样品特征峰相比,110和113衍射峰不但重叠,而且强度变弱、峰宽变宽了,说明采用本发明所述的双微乳液共沉淀法方法制备的前驱体LDH纳米片和由双金属氧化物水合恢复所得的LDH结晶度均较低,而且片层很薄。当LDH-M经500℃煅烧5小时后生成了层状双金属氧化物,XRD显示原有的片层结构坍塌,结合的氢氧根和层间的水分子失去,同时出现了新的氧化物相的衍射峰。Fig. 1 is the XRD result chart of the samples obtained in Example 2 and Comparative Examples 1-3. In the figure, the three samples of LDH, LDH-M and LDH r all have three characteristic diffraction peaks of hydrotalcite-like crystal planes 003, 006, and 009 at low 2θ, and LDH-M and LDH r are similar to the characteristic peaks of the LDH sample. Ratio, its peak width obviously widens, and intensity obviously weakens, and the crystallinity of the precursor LDH nanosheet that adopts double microemulsion co-precipitation method of the present invention to prepare is lower, and its crystallization is recovered by double metal oxide hydration. degree becomes lower. The d 003 values of the three samples are between 0.78 and 0.80nm, comparable to Cl-LDH, and their unit cell parameters a and b (a=b=2d 110 ) are about consistent with literature values. The width and intensity of the diffraction peaks well reflect the crystallinity of the sample. The three samples also have 110 and 113 diffraction peaks at high 2θ, but it is obvious that compared with the characteristic peaks of LDH samples, the 110 and 113 diffraction peaks of LDH-M and LDH r not only overlap, but also become weaker in intensity and wider in width. Broadly, it shows that the crystallinity of the precursor LDH nanosheets prepared by the double microemulsion co-precipitation method described in the present invention and the LDH recovered from the double metal oxide hydration are low, and the sheets are very thin. When LDH-M was calcined at 500°C for 5 hours, a layered double metal oxide was formed. XRD showed that the original sheet structure collapsed, the combined hydroxide and interlayer water molecules were lost, and new oxides appeared at the same time. phase diffraction peaks.
图2为实施例2、对比例1和2所得样品的N2吸附脱附等温线和孔径分布图。吸附等温线显示所有样品均为带有H3-型滞回曲线(P/P0>0.4)的典型的IV等温线,表明为介孔材料。其中LDH-M样品的比表面积为140.83m2/g,高于传统共沉淀法制备的LDH样品(53.28m2/g),说明无表面活性剂微乳液共沉淀法可以制备比表面积大的层状双金属氢氧化物超薄纳米片。而其煅烧产物LDOb由于失去了原有类水滑石的片层结构,比表面积有所减小,为113.05m2/g,但还是远高于传统共沉淀法制备的LDH样品。LDH-M和LDOb的孔径分别为3.83和10.94nm,远小于传统共沉淀法制备的LDH样品(21.87nm),这说明前两个样品缺少有序的片层结构,具体结果见表1。Fig. 2 is the N2 adsorption-desorption isotherm and pore size distribution diagram of samples obtained in Example 2, Comparative Examples 1 and 2. Adsorption isotherms showed that all samples were typical IV isotherms with H3-type hysteresis curves (P/P 0 >0.4), indicating mesoporous materials. Among them, the specific surface area of the LDH-M sample is 140.83m 2 /g, which is higher than that of the LDH sample (53.28m 2 /g) prepared by the traditional co-precipitation method, indicating that the microemulsion co-precipitation method without surfactant can prepare a layer with a large specific surface area double metal hydroxide nanosheets. The specific surface area of the calcined product LDO b is 113.05m 2 /g because of the loss of the original hydrotalcite-like sheet structure, but it is still much higher than that of the LDH sample prepared by the traditional co-precipitation method. The pore diameters of LDH-M and LDO b are 3.83 and 10.94 nm, respectively, which are much smaller than the LDH sample (21.87 nm) prepared by the traditional co-precipitation method, which indicates that the first two samples lack an ordered lamellar structure. The specific results are shown in Table 1.
表1:LDH纳米片的BET比表面和孔径结果.Table 1: BET specific surface and pore size results of LDH nanosheets.
图3为实施例2、对比例1~3所得样品的扫描电镜照片。电镜照片显示:传统共沉淀法制备的LDH样品具有明显层状结构,颗粒较大且聚集明显。而采用本发明所述无表面活性剂微乳液共沉淀法制备的前驱体LDH-M粒径较小,且因片层薄而呈现弯曲均匀分散。而其煅烧产物LDOb由于类水滑石的片层结构坍塌,呈现出了以小颗粒存在无定形结构。当LDOb在水介质中恢复后,由于LDH的“记忆效应”,LDHr又出现了类水滑石的片层结构,而且仍然具有良好的分散性,但是它的片层变大了,而且片层也变厚了,这是因为在此过程中没有微乳液体系中“小水池”的限域作用,类水滑石纳米片可以自由生长。Fig. 3 is the scanning electron micrograph of the samples obtained in Example 2 and Comparative Examples 1-3. Electron micrographs show that the LDH samples prepared by the traditional co-precipitation method have obvious layered structure, large particles and obvious aggregation. However, the precursor LDH-M prepared by the co-precipitation method of the surfactant-free microemulsion of the present invention has a smaller particle size, and is curved and uniformly dispersed due to the thin layer. The calcined product LDO b presents an amorphous structure with small particles due to the collapse of the hydrotalcite-like sheet structure. When LDO b was recovered in aqueous medium, due to the "memory effect" of LDH, LDH r appeared a hydrotalcite-like sheet structure, and still had good dispersion, but its sheet became larger, and the sheet The layer also becomes thicker, because the hydrotalcite-like nanosheets can grow freely without the confinement of the "small pool" in the microemulsion system during this process.
图4为对比例3所得样品的原子力显微镜照片(a)和a图中沿红色直线的横断面分析(b)。原子力显微镜照片显示所制备的煅烧产物LDOb经水中恢复后,呈现了明显的聚集,虽然红色直线的横断面分析结果显示,其粒径大小在20~60nm之间,厚度约为0.96~3.22nm,但可以清楚看到其他区域有呈现了明显聚集,其粒径和厚度应当更大,这与扫描电镜结果相一致。Fig. 4 is the atomic force microscope photograph (a) of the sample obtained in Comparative Example 3 and the cross-sectional analysis (b) along the red straight line in the figure a. The atomic force microscope photos show that the prepared calcined product LDO b shows obvious aggregation after being recovered in water, although the cross-sectional analysis results of the red line show that its particle size is between 20-60nm and the thickness is about 0.96-3.22nm , but it can be clearly seen that there are obvious aggregations in other regions, and the particle size and thickness should be larger, which is consistent with the results of scanning electron microscopy.
实施例5应用效果试验例Embodiment 5 application effect test example
试验对象:实施例1-5制得的产品,对比例1所得产品;Test object: the product that embodiment 1-5 makes, comparative example 1 gained product;
试验目的:考察本发明实施例1-5制得的产品和对比例1所得LDH对水体中低浓度磷酸根的吸附性能。Purpose of the test: To investigate the adsorption performance of the products obtained in Examples 1-5 of the present invention and LDH obtained in Comparative Example 1 on low-concentration phosphate radicals in water.
试验分组:Test group:
试验1组:实施例1制得的产品LDOa;Test 1 group: the product LDO a that embodiment 1 makes;
试验2组:实施例2制得的产品LDOb;Test 2 groups: the product LDO b that embodiment 2 makes;
试验3组:实施例3制得的产品LDOc;Test 3 groups: the product LDO c that embodiment 3 makes;
试验4组:实施例4制得的产品LDOd;Test 4 groups: the product LDO d that embodiment 4 makes;
试验5组:实施例5制得的产品LDOe;Test 5 groups: the product LDO e that embodiment 5 makes;
对比试验组:对比例1和2制得的产品LDH和LDH-M。Comparative test group: the products LDH and LDH-M prepared in Comparative Examples 1 and 2.
试验方法:experiment method:
将本发明试验对象各50mg分别加入到50mL、浓度为2mg/L的磷酸二氢钾水溶液中,搅拌反应5小时。每组试验重复六次,测量其处理后浓度,并测定其去除率,取平均值,其中去除率的计算公式如下:Add 50 mg of each test object of the present invention into 50 mL of potassium dihydrogen phosphate aqueous solution with a concentration of 2 mg/L, and stir and react for 5 hours. Every group of experiments is repeated six times, and the concentration after its treatment is measured, and its removal rate is determined, and the average value is obtained, wherein the calculation formula of the removal rate is as follows:
试验结果:test results:
表2:本发明产品和对比样品对水体中低浓度磷酸根的吸附试验结果Table 2: Adsorption test results of products of the present invention and comparative samples to low-concentration phosphate radicals in water bodies
备注:*与对比组LDH相比较,P<0.05;#与对比组LDH-M相比较,P<0.05。Remarks: * Compared with the comparison group LDH, P<0.05;#Compared with the comparison group LDH-M, P<0.05.
小结:通过表2的试验结果可以看出:Summary: From the test results in Table 2, it can be seen that:
结果表明:在加入相同质量吸附剂条件下,本发明各实验组(试验1、2、3、4和5组)与对比组LDH和LDH-M相比,它们对水体中低浓度磷酸根的吸附去除率都具有显著性差异,可见本发明所得层状双金属氧化物吸附剂LDO对水体中低浓度磷酸根的吸附去除效果明显优于小粒径超薄LDH纳米片和传统共沉淀法制备的大颗粒类水滑石,这主要是因为本发明所得的层状双金属氧化物吸附剂LDO除了利用大的比表面积吸附,而且在结构重建形成LDO时,磷酸根参与了类水滑石的重建,因此它们与小粒径超薄LDH纳米片以及传统共沉淀法制备的大颗粒类水滑石相比,取得了意料不到的技术效果。The result shows: under adding same mass adsorbent condition, each experimental group of the present invention (experiment 1,2,3,4 and 5 groups) compares contrast group LDH and LDH-M, they are to the phosphate radical of low concentration in water body The adsorption and removal rates all have significant differences. It can be seen that the layered double metal oxide adsorbent LDO obtained by the present invention has significantly better adsorption and removal effects on low-concentration phosphate radicals in water than those prepared by small particle size ultra-thin LDH nanosheets and traditional co-precipitation methods. This is mainly because the layered double metal oxide adsorbent LDO obtained in the present invention not only utilizes the large specific surface area for adsorption, but also when the structure is reconstructed to form LDO, the phosphate radical participates in the reconstruction of the hydrotalcite, Therefore, compared with ultra-thin LDH nanosheets with small particle size and large-particle hydrotalcites prepared by traditional co-precipitation method, they have achieved unexpected technical effects.
Claims (6)
Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510339972.8A CN105032342B (en) | 2015-06-18 | 2015-06-18 | A preparation method of layered double metal oxide adsorbent for effectively removing low-concentration phosphate |
Applications Claiming Priority (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
CN201510339972.8A CN105032342B (en) | 2015-06-18 | 2015-06-18 | A preparation method of layered double metal oxide adsorbent for effectively removing low-concentration phosphate |
Publications (2)
Publication Number | Publication Date |
---|---|
CN105032342A true CN105032342A (en) | 2015-11-11 |
CN105032342B CN105032342B (en) | 2017-08-01 |
Family
ID=54439660
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
CN201510339972.8A Active CN105032342B (en) | 2015-06-18 | 2015-06-18 | A preparation method of layered double metal oxide adsorbent for effectively removing low-concentration phosphate |
Country Status (1)
Country | Link |
---|---|
CN (1) | CN105032342B (en) |
Cited By (10)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106241893A (en) * | 2015-06-06 | 2016-12-21 | 青岛科技大学 | A kind of flower ball-shaped nickel aluminum layered double hydroxide and its preparation method and application |
CN107552007A (en) * | 2017-10-18 | 2018-01-09 | 福州大学 | Ion liquid modified magnalium laminar double-hydroxide adsorbent and its preparation and application |
CN110105865A (en) * | 2019-05-30 | 2019-08-09 | 江苏美乔科技有限公司 | A kind of environment protection damp-proof UV oil polish and preparation method thereof |
CN110372022A (en) * | 2019-06-26 | 2019-10-25 | 河海大学 | Macroscopical 3D multistage porous nanometer material one-step method for synthesizing |
CN111426736A (en) * | 2020-05-27 | 2020-07-17 | 青岛科技大学 | Preparation method of CoAl-L DH/PANI modified electrode |
CN112121758A (en) * | 2020-09-14 | 2020-12-25 | 江苏开放大学(江苏城市职业学院) | Layered double hydroxide composite attapulgite clay and preparation method thereof |
CN112237897A (en) * | 2020-09-04 | 2021-01-19 | 南京大学 | A layered bimetallic nanometer lanthanum material and its preparation method and application |
CN113083216A (en) * | 2021-04-23 | 2021-07-09 | 江苏大学 | Two-dimensional nickel-based composite metal oxide adsorbent, preparation method and application for removing phosphate radical |
CN113788502A (en) * | 2021-08-17 | 2021-12-14 | 天津大学 | Material preparation and detection method for distinguishing phosphate ion concentration in water environment |
CN115646429A (en) * | 2022-10-27 | 2023-01-31 | 南京工业大学 | A kind of ultra-thin magnesium-lanthanum layered double metal oxide adsorbent and its preparation method and application |
Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2005263596A (en) * | 2004-03-22 | 2005-09-29 | National Institute For Materials Science | Layered double hydroxide / zeolite composite and process for producing the same |
CN101970099A (en) * | 2008-01-31 | 2011-02-09 | 协和化学工业株式会社 | Selective adsorbent material, and method for production thereof |
-
2015
- 2015-06-18 CN CN201510339972.8A patent/CN105032342B/en active Active
Patent Citations (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JP2005263596A (en) * | 2004-03-22 | 2005-09-29 | National Institute For Materials Science | Layered double hydroxide / zeolite composite and process for producing the same |
CN101970099A (en) * | 2008-01-31 | 2011-02-09 | 协和化学工业株式会社 | Selective adsorbent material, and method for production thereof |
Non-Patent Citations (4)
Title |
---|
JIE XU, ET AL: "Synthesis of Mg2Al-Cl layered double hydroxide nanosheets in a surfactant-free reverse microemulsion", 《COLLOID POLYM SCI》 * |
印露,等: "焙烧态镁铝铁类水滑石对磷酸根离子的吸附", 《环境化学》 * |
徐洁: "无表面活性剂微乳液及其在纳米颗粒制备中的应用", 《中国博士学位论文全文数据库工程科技I辑》 * |
詹天荣: "曾状双金属氢氧化物在绿色材料中的应用", 《化学通报》 * |
Cited By (15)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
CN106241893A (en) * | 2015-06-06 | 2016-12-21 | 青岛科技大学 | A kind of flower ball-shaped nickel aluminum layered double hydroxide and its preparation method and application |
CN107552007A (en) * | 2017-10-18 | 2018-01-09 | 福州大学 | Ion liquid modified magnalium laminar double-hydroxide adsorbent and its preparation and application |
CN107552007B (en) * | 2017-10-18 | 2019-05-10 | 福州大学 | Ionic liquid modified magnesium aluminum layered double hydroxide adsorbent and its preparation and application |
CN110105865A (en) * | 2019-05-30 | 2019-08-09 | 江苏美乔科技有限公司 | A kind of environment protection damp-proof UV oil polish and preparation method thereof |
CN110372022B (en) * | 2019-06-26 | 2021-10-19 | 河海大学 | One-step synthesis of macroscopic 3D hierarchical porous nanomaterials |
CN110372022A (en) * | 2019-06-26 | 2019-10-25 | 河海大学 | Macroscopical 3D multistage porous nanometer material one-step method for synthesizing |
CN111426736A (en) * | 2020-05-27 | 2020-07-17 | 青岛科技大学 | Preparation method of CoAl-L DH/PANI modified electrode |
CN111426736B (en) * | 2020-05-27 | 2022-09-09 | 青岛科技大学 | A kind of preparation method of CoAl-LDH/PANI modified electrode |
CN112237897A (en) * | 2020-09-04 | 2021-01-19 | 南京大学 | A layered bimetallic nanometer lanthanum material and its preparation method and application |
CN112121758A (en) * | 2020-09-14 | 2020-12-25 | 江苏开放大学(江苏城市职业学院) | Layered double hydroxide composite attapulgite clay and preparation method thereof |
CN113083216A (en) * | 2021-04-23 | 2021-07-09 | 江苏大学 | Two-dimensional nickel-based composite metal oxide adsorbent, preparation method and application for removing phosphate radical |
CN113083216B (en) * | 2021-04-23 | 2023-11-10 | 江苏大学 | Two-dimensional nickel-based composite metal oxide adsorbent, preparation method and application in removing phosphate radicals |
CN113788502A (en) * | 2021-08-17 | 2021-12-14 | 天津大学 | Material preparation and detection method for distinguishing phosphate ion concentration in water environment |
CN113788502B (en) * | 2021-08-17 | 2023-02-17 | 天津大学 | Material preparation and detection method for distinguishing phosphate ion concentration in water environment |
CN115646429A (en) * | 2022-10-27 | 2023-01-31 | 南京工业大学 | A kind of ultra-thin magnesium-lanthanum layered double metal oxide adsorbent and its preparation method and application |
Also Published As
Publication number | Publication date |
---|---|
CN105032342B (en) | 2017-08-01 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
CN105032342B (en) | A preparation method of layered double metal oxide adsorbent for effectively removing low-concentration phosphate | |
El Hassani et al. | Effect of morphological properties of layered double hydroxides on adsorption of azo dye Methyl Orange: A comparative study | |
Taher et al. | Preparation of magnetite-nanoparticle-decorated NiFe layered double hydroxide and its adsorption performance for congo red dye removal | |
Li et al. | Uniformly coating ZnAl layered double oxide nanosheets with ultra-thin carbon by ligand and phase transformation for enhanced adsorption of anionic pollutants | |
Lei et al. | Ultrathin dodecyl-sulfate-intercalated Mg-Al layered double hydroxide nanosheets with high adsorption capability for dye pollution | |
Guo et al. | Superb adsorption of organic dyes from aqueous solution on hierarchically porous composites constructed by ZnAl-LDH/Al (OH) 3 nanosheets | |
CN104437344B (en) | A kind of Copper-cladding Aluminum Bar composite magnetic nano material and preparation thereof and application | |
Lv et al. | Highly efficient removal of As (V) by using NiAl layered double oxide composites | |
CN104998609B (en) | A kind of method that surfactant-free reverse micro emulsion prepares the ultra-thin acrylic/hydrotalcite-like nano piece of small particle | |
Zhang et al. | Mechano-hydrothermal synthesis of SDS intercalated LDH nanohybrids and their removal efficiency for 2, 4-dichlorophenoxyacetic acid from aqueous solution | |
CN104874365B (en) | Carboxymethyl cellulose ion insertion hydrotalcite-like composite material and preparation method and application | |
CN107486141B (en) | A kind of preparation method of magnesium oxide chemically modified diatomite with high adsorption capacity | |
CN112169748A (en) | Adsorbent and preparation method and application thereof | |
Zhuang et al. | Alcohol-assisted self-assembled 3D hierarchical iron (hydr) oxide nanostructures for water treatment | |
CN109692653B (en) | Adsorbent for efficiently adsorbing phosphate ions in water and preparation method thereof | |
CN102068957B (en) | Zirconium-based arsenic removing material and preparation method and application thereof | |
CN112108106A (en) | Preparation method of calcined calcium magnesium aluminum based LDHs and dephosphorization application thereof | |
CN101128626A (en) | Preparation of suspension | |
CN115779849A (en) | A kind of mesoporous alumina adsorbent and its preparation method and application | |
CN118373438A (en) | Preparation method of layered double hydroxide nano-sheet and application of layered double hydroxide nano-sheet in removal of perfluoro or polyfluoroalkyl substances in water body | |
CN110711553A (en) | Hydrotalcite-pseudo-boehmite composite film and preparation method and application thereof | |
Xu et al. | Template-free synthesis of mesoporous CeO 2 powders by integrating bottom-up and top-down routes for acid orange 7 adsorption | |
CN113231023A (en) | Preparation method and application of expanded graphite-based cobalt-indium bimetal hydroxide interlayer composite material | |
CN115072790A (en) | Synthetic method and application of layered double-metal-based nano lanthanum material capable of synchronously locking phosphorus, removing algae and reducing turbidity | |
CN103480324A (en) | A kind of mesoporous Fe3O4 microsphere and its preparation and application method |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
C06 | Publication | ||
PB01 | Publication | ||
C10 | Entry into substantive examination | ||
SE01 | Entry into force of request for substantive examination | ||
CB03 | Change of inventor or designer information |
Inventor after: Sun Yuan Inventor after: Zhan Tianrong Inventor after: Yang Qi Inventor after: Xu Jie Inventor after: Hou Wanguo Inventor before: Zhan Tianrong Inventor before: Zhang Yumei Inventor before: Yang Qi Inventor before: Song Yang Inventor before: Xu Jie |
|
CB03 | Change of inventor or designer information | ||
GR01 | Patent grant | ||
GR01 | Patent grant | ||
TR01 | Transfer of patent right |
Effective date of registration: 20190301 Address after: 230000 B-1512, west of Ganquan Road, Shushan District, Hefei, Anhui. Patentee after: Anhui Eagle Dragon Industrial Design Co., Ltd. Address before: 266000 Qingdao University of Science & Technology, 53 Zhengzhou Road, Shibei District, Qingdao, Shandong Patentee before: Qingdao University of Science & Technology |
|
TR01 | Transfer of patent right | ||
TR01 | Transfer of patent right |
Effective date of registration: 20190823 Address after: 526000 Zhaoxing Hardware Surface Treatment Industrial Park, Jinli Town, Gaoyao District, Zhaoqing City, Guangdong Province Patentee after: Zhaoqing Gaoyao District Yonghenghui Metal Products Co., Ltd. Address before: Ganquan road Shushan District of Hefei City, Anhui Province, 230000 West hillock road to the South Wild Garden commercial office building room B-1512 Patentee before: Anhui Eagle Dragon Industrial Design Co., Ltd. |
|
TR01 | Transfer of patent right |