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CN112808272B - Nano composite substrate with SERS activity and degradation performance and preparation method thereof - Google Patents

Nano composite substrate with SERS activity and degradation performance and preparation method thereof Download PDF

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CN112808272B
CN112808272B CN202011536464.6A CN202011536464A CN112808272B CN 112808272 B CN112808272 B CN 112808272B CN 202011536464 A CN202011536464 A CN 202011536464A CN 112808272 B CN112808272 B CN 112808272B
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渠陆陆
田菲
杨国海
张迎娣
戴诗雨
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Abstract

A method of preparing a nanocomposite substrate having SERS activity and degradation properties, comprising: reacting MgCl 2 Dissolving ultrapure water to form a solution a; adding ammonia water and anhydrous ethanol into the solution a under stirring to form solution b, filtering, washing to separate Mg (OH) 2 And (4) precipitating. The precipitate is calcined at high temperature for a period of time to obtain MgO. Subsequently dispersing it in H 2 O 2 To form a suspension c, and separating the solid from the suspension to obtain MgO as a product 2 . Adding MgO 2 Ultrasonically mixing with polyetherimide to obtain suspension d, centrifuging and washing for several times, adding gold nanoparticles into the resuspended d, ultrasonically treating, washing, and resuspending to form gold nanoparticles and MgO 2 The complex of (a); soaking carbon nanotube sponge in the gold nanoparticles and MgO 2 Forming a nanocomposite substrate. The method of the invention is carried out with MgCl 2 Synthesis of MgO for precursors 2 And then the nano composite substrate with SERS activity and degradation performance is respectively assembled with the gold nanoparticles and the carbon nanotube sponge.

Description

一种具有SERS活性和降解性能的纳米复合基底及其制备方法A nanocomposite substrate with SERS activity and degradation performance and its preparation method

技术领域technical field

本发明涉及降解和SERS活性,具体涉及一种具有SERS活性和降解性能的纳米复合基底的制备方法。The invention relates to degradation and SERS activity, in particular to a method for preparing a nanocomposite substrate with SERS activity and degradation performance.

背景技术Background technique

在典型的芬顿反应中,H2O2通常被用作氧化剂来降解有机污染物。然而,液态过氧化氢不稳定,且在高浓度下具有很高的生物毒性。因此,使用高纯过氧化镁(MgO2)纳米颗粒,并用其代替H2O2降解有机染料。金纳米粒子作为一种贵金属,分子吸附在贵金属表面,在激光照射下,会产生很强的表面增强拉曼散射(SERS)信号,但是制备的纳米材料循环使用难。此外,分散的催化剂和增强材料难以回收,会对环境造成二次污染。碳基材料较大的比表面积和具有的孔隙结构,使其可以吸附水体的有机污染物,同时对进行催化反应的材料进行负载和回收。 In a typical Fenton reaction, H2O2 is usually used as an oxidizing agent to degrade organic pollutants. However, liquid hydrogen peroxide is unstable and highly biotoxic at high concentrations. Therefore, high-purity magnesium peroxide (MgO 2 ) nanoparticles were used and used instead of H 2 O 2 to degrade organic dyes. As a noble metal, gold nanoparticles are adsorbed on the surface of the noble metal. Under laser irradiation, a strong surface-enhanced Raman scattering (SERS) signal will be generated, but the prepared nanomaterials are difficult to recycle. In addition, dispersed catalysts and reinforcing materials are difficult to recycle, which will cause secondary pollution to the environment. The large specific surface area and pore structure of carbon-based materials enable them to adsorb organic pollutants in water bodies, and at the same time, carry out loading and recovery of materials for catalytic reactions.

发明内容Contents of the invention

本发明的目的是提供一种具有SERS活性和降解性能的纳米复合材料的制备方法,改善材料功能单一的问题,通过与碳纳米管海绵组装改善多功能纳米材料不可回收的问题。The purpose of the present invention is to provide a preparation method of a nanocomposite material with SERS activity and degradation performance, improve the problem of single function of the material, and improve the non-recyclable problem of multifunctional nanomaterials by assembling with carbon nanotube sponge.

为实现上述发明目的,本发明的技术方案具体如下:In order to realize the above-mentioned purpose of the invention, the technical scheme of the present invention is specifically as follows:

一种具有SERS活性和降解性能的纳米复合基底的制备方法,包括以下步骤:A method for preparing a nanocomposite substrate with SERS activity and degradation performance, comprising the following steps:

S1:将MgCl2溶解于超纯水中形成溶液a;在不断搅拌下在溶液a中加入氨水和无水乙醇形成溶液b,将溶液b抽滤、洗涤分离出Mg(OH)2沉淀;S1: Dissolve MgCl2 in ultrapure water to form solution a; add ammonia water and absolute ethanol to solution a under constant stirring to form solution b, and filter and wash solution b to separate Mg(OH) 2 as a precipitate;

S2:将此沉淀在高温下煅烧一段时间,得到MgO;S2: calcining the precipitate at high temperature for a period of time to obtain MgO;

S3:随后将其分散于H2O2中形成悬浮液c,将固体从悬浮液中分离出来,得到产物MgO2S3: then disperse it in H 2 O 2 to form a suspension c, and separate the solid from the suspension to obtain the product MgO 2 ;

S4:将MgO2与聚醚酰亚胺超声混合得到悬浮液d,离心洗涤数次;S4: Ultrasonic mixing of MgO2 and polyetherimide to obtain suspension d, centrifuged and washed several times;

S5:在重悬过后的d中加入金纳米粒子,超声一段时间,离心洗涤数次,重悬后形成金纳米粒子与MgO2的复合物;S5: Add gold nanoparticles to d after resuspension, sonicate for a period of time, centrifuge and wash several times, and form a complex of gold nanoparticles and MgO 2 after resuspension;

S6:将碳纳米管海绵浸泡在金纳米粒子与MgO2的复合物中,形成纳米复合基底。S6: Soak the carbon nanotube sponge in the composite of gold nanoparticles and MgO 2 to form a nanocomposite substrate.

作为优选的技术方案,所述步骤S3中,H2O2的浓度为30%。As a preferred technical solution, in the step S3, the concentration of H 2 O 2 is 30%.

作为优选的技术方案,所述步骤S4包括:将MgO2与聚醚酰亚胺超声混合得到悬浮液 d,离心洗涤数次;聚醚酰亚胺的浓度为0.01%,常温超声,时间为2h,用超纯水离心洗涤次数为6次。As a preferred technical solution, the step S4 includes: ultrasonically mixing MgO2 and polyetherimide to obtain a suspension d, centrifuging and washing several times; the concentration of polyetherimide is 0.01%, and ultrasonication at room temperature for 2 hours , centrifuged and washed with ultrapure water for 6 times.

作为优选的技术方案,所述步骤S5包括:在重悬过后的d中加入金纳米粒子,常温超声2h,超纯水离心洗涤4次,重悬后形成金纳米粒子与MgO2的复合物。As a preferred technical solution, the step S5 includes: adding gold nanoparticles to d after resuspension, sonicating at room temperature for 2 hours, centrifuging and washing with ultrapure water for 4 times, and forming a complex of gold nanoparticles and MgO after resuspension.

作为优选的技术方案,所述步骤S6包括:将碳纳米海绵进行酸化处理,之后将碳纳米管海绵浸泡在金纳米粒子与MgO2的复合物中,形成纳米复合基底。As a preferred technical solution, the step S6 includes: acidifying the carbon nano-sponge, and then soaking the carbon nano-tube sponge in a composite of gold nanoparticles and MgO 2 to form a nano-composite substrate.

本发明还提供了由上述方法制备的具有SERS活性和降解性能的纳米复合基底。The invention also provides the nanocomposite substrate with SERS activity and degradation performance prepared by the above method.

与现有技术相比,本发明的有益效果:Compared with prior art, the beneficial effect of the present invention:

本发明的方法是MgO2与金纳米粒子,通过静电自组装而成。利用MgO2的降解性能和金纳米粒子的表面等离子体共振效应,将两者相结合,实现材料的多功能性质;The method of the present invention is that MgO 2 and gold nanoparticles are assembled by electrostatic self-assembly. Utilize the degradation performance of MgO2 and the surface plasmon resonance effect of gold nanoparticles, combine the two to realize the multifunctional properties of the material;

本发明的方法利用碳材料较强的吸附性能,对有机污染物进行吸附和富集,再负载上复合材料,改善了分散的催化剂难回收的问题。The method of the invention utilizes the strong adsorption performance of the carbon material to adsorb and enrich the organic pollutants, and then load the composite material to improve the problem that the dispersed catalyst is difficult to recover.

附图说明Description of drawings

图1(a)MgO2的X-射线粉末衍射图(XRD);(b)MgO2@Au的X-射线粉末衍射图 (XRD);Figure 1(a) X-ray powder diffraction pattern (XRD) of MgO 2 ; (b) X-ray powder diffraction pattern (XRD) of MgO 2 @Au;

图2(a)MgO2的扫描电镜图(SEM);(b)MgO2@Au的扫描电镜图(SEM);(c)MgO2@Au 降解有机污染物的紫外图;(d)MgO2@Au测定10-4M有机污染物的SERS光谱图;Figure 2(a) Scanning electron microscope (SEM) of MgO 2 ; (b) Scanning electron microscope (SEM) of MgO 2 @Au; (c) UV image of MgO 2 @Au degradation of organic pollutants; (d) MgO 2 SERS spectrum of 10 -4 M organic pollutants measured by @Au;

图3(a)海绵负载MgO2@Au的扫描电镜图(SEM);(b)海绵负载MgO2@Au复合材料对有机污染物的降解前后的SERS图谱。Fig. 3(a) Scanning electron microscope (SEM) image of sponge-loaded MgO 2 @Au; (b) SERS spectra of sponge-loaded MgO 2 @Au composite before and after degradation of organic pollutants.

具体实施方式:Detailed ways:

下面将结合本发明实施例中的附图,对本发明实施例中的技术方案进行清楚、完整地描述,显然,所描述的实施例仅是本发明一部分实施例,而不是全部的实施例。基于本发明中的实施例,本领域普通技术人员在没有做出创造性劳动前提下所获得的所有其他实施例,都属于本发明保护的范围。The following will clearly and completely describe the technical solutions in the embodiments of the present invention with reference to the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only some of the embodiments of the present invention, not all of them. Based on the embodiments of the present invention, all other embodiments obtained by persons of ordinary skill in the art without making creative efforts belong to the protection scope of the present invention.

实施例Example

1、MgO2@Au的合成方法:1. The synthesis method of MgO 2 @Au:

将MgCl2溶解超纯水中形成溶液a;在不断搅拌下在溶液a中加入氨水和无水乙醇形成溶液b,将溶液b抽滤、洗涤分离出Mg(OH)2沉淀。将此沉淀在高温下煅烧一段时间,得到MgO。随后将其分散于H2O2中形成悬浮液c,将固体从悬浮液中分离出来,得到产物 MgO2。将MgO2与聚醚酰亚胺超声混合得到悬浮液d,离心洗涤数次,再在重悬过后的d 中加入金纳米粒子,超声一段时间,离心洗涤数次,重悬后形成金纳米粒子与MgO2的复合物。图1为在上述实验条件下通过所得的MgO2和MgO2@Au的XRD。XRD图(1a)表明所得产物为较好结晶性的MgO2,图(1b)表明MgO2与金纳米粒子的复合物通过静电作用成功自组装。图2(a)是MgO2的扫描电镜图(SEM),(b)是MgO2@Au的扫描电镜图(SEM),从图2(a)、2(b)分别可以看出过氧化镁是由粒径很小的纳米粒子堆积而成的块状结构;粒径约为70nm的金纳米粒子表面附着着粒径很小的MgO2。图2(c)是MgO2@Au降解有机污染物的紫外图,结果表明该复合物可有效降解有机污染物。图2(d)是MgO2@Au测定10-4M 有机污染物的SERS光谱图,从图谱中可以分析得到该复合物具有SERS活性。Dissolve MgCl 2 in ultrapure water to form solution a; add ammonia water and absolute ethanol to solution a under constant stirring to form solution b, and filter and wash solution b to separate Mg(OH) 2 precipitate. This precipitate is calcined at high temperature for a period of time to obtain MgO. It is subsequently dispersed in H2O2 to form a suspension c, from which the solid is separated to give the product MgO2 . Mix MgO2 and polyetherimide ultrasonically to obtain a suspension d, centrifuge and wash several times, then add gold nanoparticles to the resuspended d, ultrasonicate for a period of time, centrifuge and wash several times, and form gold nanoparticles after resuspension Complexes with MgO2 . Figure 1 shows the XRD of MgO 2 and MgO 2 @Au obtained under the above experimental conditions. The XRD pattern (1a) shows that the obtained product is MgO 2 with good crystallinity, and the pattern (1b) shows that the complex of MgO 2 and gold nanoparticles self-assembles successfully through electrostatic interaction. Figure 2(a) is the scanning electron microscope image (SEM) of MgO 2 , (b) is the scanning electron microscope image (SEM) of MgO 2 @Au, it can be seen from Figure 2(a) and 2(b) that magnesium peroxide It is a massive structure formed by the accumulation of nanoparticles with a particle size of about 70nm; the surface of gold nanoparticles with a particle size of about 70nm is attached with MgO 2 with a small particle size. Figure 2(c) is the UV diagram of the degradation of organic pollutants by MgO 2 @Au, and the results show that the composite can effectively degrade organic pollutants. Figure 2(d) is the SERS spectrum of 10 -4 M organic pollutants measured by MgO 2 @Au. From the spectrum, it can be analyzed that the complex has SERS activity.

2、碳纳米管海绵负载MgO2@Au:2. Carbon nanotube sponge loaded with MgO 2 @Au:

将碳纳米管海绵浸泡在上述的金纳米粒子与MgO2的复合物中,形成一个纳米复合基底。图3(a)海绵负载MgO2@Au的扫描电镜图(SEM);(b)海绵负载MgO2@Au复合材料对有机污染物的降解前后的SERS图谱。SEM图表明MgO2@Au纳米复合材料成功附着在海绵上。图3(b)说明材料负载在海绵上,并不影响该材料的性能,且海绵可以对此分散的催化剂起到良好的收集作用。The carbon nanotube sponge was soaked in the above-mentioned composite of gold nanoparticles and MgO 2 to form a nanocomposite substrate. Fig. 3(a) Scanning electron microscope (SEM) image of sponge-loaded MgO 2 @Au; (b) SERS spectra of sponge-loaded MgO 2 @Au composite before and after degradation of organic pollutants. The SEM images indicated that the MgO 2 @Au nanocomposites were successfully attached to the sponge. Figure 3(b) shows that the material loaded on the sponge does not affect the performance of the material, and the sponge can play a good role in collecting the dispersed catalyst.

Claims (6)

1.一种具有SERS活性和降解性能的纳米复合基底的制备方法,其特征在于,包括以下步骤:1. A preparation method of a nanocomposite substrate with SERS activity and degradation performance, characterized in that, comprising the following steps: S1:将MgCl2溶解于超纯水中形成溶液a;在不断搅拌下在溶液a中加入氨水和无水乙醇形成溶液b,将溶液b抽滤、洗涤分离出Mg(OH)2沉淀;S1: Dissolve MgCl2 in ultrapure water to form solution a; add ammonia water and absolute ethanol to solution a under constant stirring to form solution b, and filter and wash solution b to separate Mg(OH) 2 as a precipitate; S2:将此沉淀在高温下煅烧一段时间,得到MgO;S2: calcining the precipitate at high temperature for a period of time to obtain MgO; S3:随后将其分散于H2O2中形成悬浮液c,将固体从悬浮液中分离出来,得到产物MgO2S3: then disperse it in H 2 O 2 to form a suspension c, and separate the solid from the suspension to obtain the product MgO 2 ; S4:将MgO2与聚醚酰亚胺超声混合得到悬浮液d,离心洗涤数次;S4: Ultrasonic mixing of MgO2 and polyetherimide to obtain suspension d, centrifuged and washed several times; S5:在重悬过后的d中加入金纳米粒子,超声一段时间,离心洗涤数次,重悬后形成金纳米粒子与MgO2的复合物;S5: Add gold nanoparticles to d after resuspension, sonicate for a period of time, centrifuge and wash several times, and form a complex of gold nanoparticles and MgO 2 after resuspension; S6:将碳纳米管海绵浸泡在金纳米粒子与MgO2的复合物中,形成纳米复合基底。S6: Soak the carbon nanotube sponge in the composite of gold nanoparticles and MgO 2 to form a nanocomposite substrate. 2.根据权利要求1所述的制备方法,其特征在于,所述步骤S3中,H2O2的浓度为30%。 2. The preparation method according to claim 1 , characterized in that, in the step S3, the concentration of H2O2 is 30%. 3.根据权利要求1所述的制备方法,其特征在于,所述步骤S4包括:将MgO2与聚醚酰亚胺超声混合得到悬浮液d,离心洗涤数次;聚醚酰亚胺的浓度为0.01%,常温超声,时间为2h,用超纯水离心洗涤次数为6次。3. The preparation method according to claim 1 , characterized in that, said step S4 comprises: mixing MgO with polyetherimide ultrasonically to obtain a suspension d, and centrifugally washing several times; the concentration of polyetherimide 0.01%, sonicated at room temperature for 2 hours, and centrifuged and washed with ultrapure water for 6 times. 4.根据权利要求1所述的制备方法,其特征在于,所述步骤S5包括:在重悬过后的d中加入金纳米粒子,常温超声2h,超纯水离心洗涤4次,重悬后形成金纳米粒子与MgO2的复合物。4. The preparation method according to claim 1, characterized in that the step S5 comprises: adding gold nanoparticles into the resuspended d, ultrasonication at room temperature for 2 hours, centrifugal washing with ultrapure water for 4 times, and forming after resuspension Composite of gold nanoparticles and MgO2 . 5.根据权利要求1所述的制备方法,其特征在于,所述步骤S6包括:将碳纳米海绵进行酸化处理,之后将碳纳米管海绵浸泡在金纳米粒子与MgO2的复合物中,形成纳米复合基底。5. preparation method according to claim 1, is characterized in that, described step S6 comprises: carbon nano-sponge is carried out acidification treatment, then carbon nano-tube sponge is soaked in gold nanoparticle and MgO in the compound , forms Nanocomposite substrates. 6.由上述任一权利要求所述方法制备的具有SERS活性和降解性能的纳米复合基底。6. A nanocomposite substrate with SERS activity and degradation properties prepared by the method according to any one of the preceding claims.
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