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CN106861626B - Adsorption-photocatalysis dual-function material, preparation method thereof and application thereof in volatile organic gas treatment process - Google Patents

Adsorption-photocatalysis dual-function material, preparation method thereof and application thereof in volatile organic gas treatment process Download PDF

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CN106861626B
CN106861626B CN201710033528.2A CN201710033528A CN106861626B CN 106861626 B CN106861626 B CN 106861626B CN 201710033528 A CN201710033528 A CN 201710033528A CN 106861626 B CN106861626 B CN 106861626B
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肖静
李希翼
皮云红
李忠
夏启斌
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South China University of Technology SCUT
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Abstract

本发明公开了一种吸附‑光催化双功能材料及其制备方法与在挥发性有机气体治理工艺的应用。该制备方法为:将2‑氨基对苯二甲酸和铁元素前驱体溶于N,N‑二甲基甲酰胺,加入甲醇溶剂,搅拌均匀,加入钛元素前驱体,搅拌,将混合液进行水热合成反应;产物依次进行DMF洗和甲醇洗涤后,离心过滤提取产物,将产物放入甲醇溶液中纯化,最后离心过滤提取产物,烘干,制得吸附‑光催化双功能材料。本发明吸附‑光催化双功能材料具有高的VOCs吸附容量选择性和可见光光催化降解效率,发明工艺可在常温、常压、可见光辐射下实现VOCs吸附‑光催化降解循环操作,工艺简单,能耗低,可实现含VOCs废气的半连续深度净化。

Figure 201710033528

The invention discloses an adsorption-photocatalytic bifunctional material, a preparation method thereof, and an application in a volatile organic gas treatment process. The preparation method includes: dissolving 2-aminoterephthalic acid and iron element precursor in N,N-dimethylformamide, adding methanol solvent, stirring evenly, adding titanium element precursor, stirring, and subjecting the mixed solution to water Thermal synthesis reaction; after the product is washed with DMF and methanol in sequence, the product is extracted by centrifugal filtration, the product is put into a methanol solution for purification, and finally the product is extracted by centrifugal filtration, and dried to obtain an adsorption-photocatalytic bifunctional material. The adsorption-photocatalytic bifunctional material of the invention has high VOCs adsorption capacity selectivity and visible light photocatalytic degradation efficiency, and the inventive process can realize the VOCs adsorption-photocatalytic degradation cycle operation under normal temperature, normal pressure and visible light radiation, the process is simple, and the energy Low consumption, can realize semi-continuous deep purification of waste gas containing VOCs.

Figure 201710033528

Description

一种吸附-光催化双功能材料及其制备方法与在挥发性有机 气体治理工艺的应用A kind of adsorption-photocatalytic bifunctional material and preparation method thereof and in volatile organic Application of gas treatment process

技术领域technical field

本发明属于材料制备领域,具体涉及一种吸附-光催化双功能材料及其制备方法与在挥发性有机气体治理工艺的应用。The invention belongs to the field of material preparation, and in particular relates to an adsorption-photocatalysis bifunctional material, a preparation method thereof, and an application in a volatile organic gas treatment process.

背景技术Background technique

目前我国成千上万的工厂仍存在无组织地向环境排放大量的挥发性有机物(VOCs),是当今大气污染的主要源头之一。VOCs污染已严重威胁着人类的健康和破坏环境的生态平衡,制约社会可持续发展,已引起了公众的强烈不满和政府的极大关注。因此要有效地治理VOCs的污染已迫在眉睫。因此,研发VOCs排放控制关键材料与技术有着重大的国家需求和现实意义。At present, thousands of factories in my country still discharge a large amount of volatile organic compounds (VOCs) into the environment unorganized, which is one of the main sources of air pollution today. VOCs pollution has seriously threatened human health, destroyed the ecological balance of the environment, and restricted the sustainable development of society. It has aroused strong public dissatisfaction and great concern from the government. Therefore, it is urgent to effectively control the pollution of VOCs. Therefore, the research and development of key materials and technologies for VOCs emission control has great national needs and practical significance.

为有效地治理有机废气中VOCs污染,国内外广泛采用的技术有催化燃烧法、吸附法、吸收法等,近年来研究的治理技术还有生物膜法、光催化氧化法、等离子体法等[1YuB.F.;Hu Z.B.;Liu M.;Yang H.L;Kong Q.X.;Liu Y.H.,Review of research on air-conditioning systems and indoor air quality control for humanhealth.International Journal of Refrigeration.2009,32,3-20]。其中,吸附法是目前被认为最有发展潜力的大风量、低浓度VOCs(几百ppm)的治理技术。吸附是一种以多孔材料为核心的分离技术[2陈寒光;张忠良;王东辉,活性炭模块的制备及其对苯的吸附性能研究.北京化工大学学报(自然科学版).2012,39,26-30]。它能够有效地吸附废气中的挥发性有机污染物,已在有机废气的净化和VOCs的回收方面得到较为广泛的应用。然而,目前吸附技术治理VOCs所面临的关键瓶颈问题包括:(1)虽然吸附是一个自发过程,但吸附剂对VOCs的吸附容量有限;(2)当吸附剂对VOCs的吸附接近饱和时需要进行再生,而再生则是一个需要外界施加能量的过程。常规的吸附剂再生方法,如热脱附,溶剂洗脱[3丁照兵;李娼;李波,室内空气净化技术研究综述.微量元素与健康研究.2008,25,63-68]等,不可避免的造成二次污染,且能耗高或工艺复杂,也直接决定了吸附技术的可行性和经济性。吸附剂的再生实际也是吸附技术能应用于实际工业的关键点,但在研究过程中往往被忽视。同时兼具VOCs高吸附容量,且吸附剂再生过程不造成二次污染能耗低的吸附技术鲜有报道。因此,研究新型高VOCs吸附容量的吸附剂、且吸附剂在再生过程中不造成二次污染的技术将对吸附技术的实际工业应用有重要的推动作用,值得学术界和工业界重点攻关。In order to effectively control VOCs pollution in organic waste gas, the technologies widely used at home and abroad include catalytic combustion method, adsorption method, absorption method, etc. In recent years, the treatment technologies studied include biofilm method, photocatalytic oxidation method, plasma method, etc. 1YuB.F.;Hu Z.B.;Liu M.;Yang H.L;Kong Q.X.;Liu Y.H.,Review of research on air-conditioning systems and indoor air quality control for humanhealth.International Journal of Refrigeration.2009,32,3-20] . Among them, the adsorption method is currently considered to be the most promising treatment technology for large air volume and low concentration of VOCs (hundreds of ppm). Adsorption is a separation technology with porous materials as the core. -30]. It can effectively adsorb volatile organic pollutants in waste gas, and has been widely used in the purification of organic waste gas and the recovery of VOCs. However, the key bottleneck problems faced by the current adsorption technology for VOCs treatment include: (1) Although adsorption is a spontaneous process, the adsorption capacity of the adsorbent for VOCs is limited; (2) When the adsorption of VOCs by the adsorbent is close to saturation, it needs to be carried out. Regeneration, and regeneration is a process that requires external energy. Conventional adsorbent regeneration methods, such as thermal desorption, solvent elution [3 Ding Zhaobing; Li Di; Li Bo, Review of Research on Indoor Air Purification Technology. Research on Trace Elements and Health. 2008, 25, 63-68], etc., inevitably It causes secondary pollution, high energy consumption or complex process, which directly determines the feasibility and economy of adsorption technology. The regeneration of adsorbents is also a key point for adsorption technology to be applied to practical industries, but it is often ignored in the research process. At the same time, there are few reports on adsorption technologies with high VOCs adsorption capacity and low energy consumption without causing secondary pollution during the regeneration process of the adsorbent. Therefore, the study of new adsorbents with high VOCs adsorption capacity and the technology that the adsorbent does not cause secondary pollution during the regeneration process will have an important role in promoting the practical industrial application of adsorption technology, and it is worthy of key research in academia and industry.

金属有机框架材料(Metal-Organic Frameworks,简称MOFs)是一类由金属离子或金属簇与有机配体通过自组装过程形成具有周期性无线网络结构的多孔有机-无机杂化晶态材料。MOFs材料具有丰富规则的孔隙结构,超高的比表面积和超大孔容,孔径和表面化学性质可调,以及含有不饱和金属位点等,在可持续能源和环境治理上已有较大的应用前景。在VOCs吸附方面,杨坤等人报道了MIL-101(Cr)材料对VOCs的吸附,在25℃下对甲苯的吸附容量达11.91mmol/g。[4Yang K.;Sun Q.;Xue R;LinD.H.,Adsorption of volatileorganic compounds by metal-organic frameworks MIL-101:influence of molecularsize and shape.Journal of Hazardous materials.2011,195,124-131]我们前期研究也发现HKUST-1在298K、8kPa下对苯的吸附容量达6.90mmol·g-1。[5李玉洁,苗晋朋,孙雪娇,肖静,夏启斌,奚红霞,李忠,机械化学法合成金属有机框架材料HKUST-1及其吸附苯性能.2015,66,793-799]然而,同时具备高VOCs吸附容量和高VOCs光催化降解活性的吸附-光催化双功能金属有机框架材料,以及基于该类材料的VOCs吸附-光催化耦合治理工艺均未见报道。Metal-Organic Frameworks (MOFs) are a class of porous organic-inorganic hybrid crystalline materials with periodic wireless network structure formed by metal ions or metal clusters and organic ligands through self-assembly process. MOFs materials have rich and regular pore structure, ultra-high specific surface area and ultra-large pore volume, adjustable pore size and surface chemical properties, and contain unsaturated metal sites, etc., and have been widely used in sustainable energy and environmental governance. prospect. In terms of VOCs adsorption, Yang Kun et al. reported the adsorption of VOCs by MIL-101(Cr) material, and the adsorption capacity of toluene at 25 °C reached 11.91 mmol/g. [4 Yang K.; Sun Q.; Xue R; Lin D.H., Adsorption of volatileorganic compounds by metal-organic frameworks MIL-101: influence of molecular size and shape. Journal of Hazardous materials. 2011, 195, 124-131] Our previous study It was also found that HKUST-1 had an adsorption capacity of 6.90 mmol·g -1 for benzene at 298 K and 8 kPa. [5 Li Yujie, Miao Jinpeng, Sun Xuejiao, Xiao Jing, Xia Qibin, Xi Hongxia, Li Zhong, Mechanochemical synthesis of metal-organic framework material HKUST-1 and its adsorption performance for benzene. 2015, 66, 793-799] However, at the same time, with high VOCs adsorption The adsorption-photocatalytic bifunctional metal-organic framework materials with high capacity and high VOCs photocatalytic degradation activity, and the VOCs adsorption-photocatalytic coupling treatment process based on such materials have not been reported.

发明内容SUMMARY OF THE INVENTION

为了克服现有技术的缺点与不足,本发明的首要目的在于发明一种吸附-光催化双功能材料及挥发性有机气体治理新工艺。该吸附-光催化双功能材料同时具备高VOCs吸附容量和高VOCs光催化降解活性;而基于该吸附-光催化双功能材料的VOCs治理技术可实现半连续的吸附净化-光催化降解的同时实现材料的再生过程,且材料再生过程不造成二次污染、能耗低。In order to overcome the shortcomings and deficiencies of the prior art, the primary purpose of the present invention is to invent an adsorption-photocatalytic bifunctional material and a new process for treating volatile organic gases. The adsorption-photocatalytic bifunctional material has both high VOCs adsorption capacity and high VOCs photocatalytic degradation activity; and the VOCs treatment technology based on the adsorption-photocatalytic bifunctional material can realize semi-continuous adsorption purification-photocatalytic degradation at the same time. The material regeneration process, and the material regeneration process does not cause secondary pollution and low energy consumption.

本发明的目的通过如下技术方案实现:The object of the present invention is achieved through the following technical solutions:

一种吸附-光催化双功能材料及其制备方法,包括如下步骤:An adsorption-photocatalytic bifunctional material and a preparation method thereof, comprising the following steps:

(1)将2-氨基对苯二甲酸和铁元素前驱体溶于N,N-二甲基甲酰胺(DMF),加入甲醇溶剂,搅拌均匀,加入钛元素前驱体,继续搅拌均匀后,将混合液进行水热合成反应;(1) Dissolve 2-aminoterephthalic acid and iron precursor in N,N-dimethylformamide (DMF), add methanol solvent, stir evenly, add titanium precursor, continue to stir evenly, then add The mixed solution is subjected to a hydrothermal synthesis reaction;

(2)产物依次进行DMF洗和甲醇洗涤后,离心过滤提取产物,将产物放入甲醇溶液中纯化,期间定时更换溶剂,最后离心过滤提取产物,烘干,制得铁钛双金属有机框架材料,即吸附-光催化双功能材料。(2) After the product is washed with DMF and washed with methanol in turn, the product is extracted by centrifugal filtration, the product is put into methanol solution for purification, the solvent is regularly replaced during the period, and finally the product is extracted by centrifugal filtration, and dried to obtain an iron-titanium bimetallic organic framework material , namely adsorption-photocatalytic bifunctional materials.

上述方法中,所述铁元素前驱体为硝酸铁、氯化铁、硫酸铁或者氧化铁;所述钛元素前驱体为钛酸四丁酯、钛酸四异丙酯、硫酸氧钛、四氯化钛或硝酸钛;所述铁元素前驱体与钛元素前驱体满足钛与铁的摩尔比为0.5~2;所述2-氨基对苯二甲酸与铁元素前驱体的摩尔比为0.5~3;所述水热合成反应溶液温度为120~180℃;所述水热合成反应时间为48~72h;所述离心转速为6000~9000r/min;所述的干燥温度为80~150℃。In the above method, the iron element precursor is iron nitrate, iron chloride, iron sulfate or iron oxide; the titanium element precursor is tetrabutyl titanate, tetraisopropyl titanate, titanium oxysulfate, tetrachloride Titanium oxide or titanium nitrate; the iron element precursor and the titanium element precursor satisfy that the molar ratio of titanium to iron is 0.5-2; the molar ratio of the 2-aminoterephthalic acid to the iron element precursor is 0.5-3 The temperature of the hydrothermal synthesis reaction solution is 120~180°C; the reaction time of the hydrothermal synthesis is 48~72h; the centrifugal speed is 6000~9000r/min; the drying temperature is 80~150°C.

上述方法中,所述铁钛双金属金属有机框架双功能催化吸附材料的Ti质量百分数为0.5~3.0wt.%;吸光边带在700~800nm,晶体尺寸为长在500~800nm、宽在100~600nm。In the above method, the Ti mass percentage of the iron-titanium bimetallic metal organic framework bifunctional catalytic adsorption material is 0.5-3.0 wt.%; the light absorption sideband is 700-800 nm, and the crystal size is 500-800 nm in length and 100 in width. ~600nm.

一种吸附-光催化双功能材料在挥发性有机气体治理工艺,包括如下步骤:An adsorption-photocatalytic dual-functional material treatment process for volatile organic gases, comprising the following steps:

(1)将含VOCs的空气通入填充吸附-光催化双功能材料床层,吸附-光催化双功能材料床层吸附VOCs,从而获得洁净空气;(1) Pass the air containing VOCs into the bed filled with adsorption-photocatalytic bifunctional material, and the bed of adsorption-photocatalytic bifunctional material adsorbs VOCs, thereby obtaining clean air;

(2)吸附-光催化双功能材料床层接近吸附饱和时,开启光源,使得吸附-光催化双功能材料表面富集的VOCs发生光催化降解生成CO2和H2O,有效避免了再生过程中VOCs脱附导致的二次污染及能耗,与此同时,吸附-光催化双功能材料床层得以再生,进入下一个吸附-光催化循环。(2) When the adsorption-photocatalytic bifunctional material bed is close to adsorption saturation, the light source is turned on, so that the VOCs enriched on the surface of the adsorption-photocatalytic bifunctional material undergo photocatalytic degradation to generate CO 2 and H 2 O, which effectively avoids the regeneration process. The secondary pollution and energy consumption caused by the desorption of VOCs in the medium are eliminated. At the same time, the bed of the adsorption-photocatalytic bifunctional material is regenerated and enters the next adsorption-photocatalytic cycle.

上述吸附-光催化双功能材料在挥发性有机气体治理工艺,步骤(1)中,所述VOCs为甲苯、苯、甲醛或者异丙醇;所述VOCs在空气中的含量为50~300ppm;所述气体流速为5~20ml/min;步骤(2)中,所述再生环境为室温;所述光催化再生光源为100~300mW/cm2;再生时间为2~6h。In the volatile organic gas treatment process of the above adsorption-photocatalytic bifunctional material, in step (1), the VOCs are toluene, benzene, formaldehyde or isopropanol; the content of the VOCs in the air is 50-300ppm; The gas flow rate is 5-20ml/min; in step (2), the regeneration environment is room temperature; the photocatalytic regeneration light source is 100-300mW/cm 2 ; the regeneration time is 2-6h.

上述吸附-光催化双功能材料在挥发性有机气体治理工艺,VOCs的吸附率达95%以上;光催化再生后材料的VOCs吸附性能保持原来的90%以上。本发明的工作原理:In the volatile organic gas treatment process of the above adsorption-photocatalytic dual-functional materials, the adsorption rate of VOCs reaches more than 95%; after photocatalytic regeneration, the VOCs adsorption performance of the material remains more than 90% of the original. The working principle of the present invention:

吸附-光催化双功能材料同时具备吸附和光催化两个功能。传统材料往往只具备其中一种功能,比如分子筛和活性炭等,其具备一定的比表面积从而具备催化剂的功能,但作为光催化剂的潜力有限;而金属氧化物TiO2和CdS等,其具有光催化活性,但比表面积有限因而作为吸附剂的潜力有限。金属有机框架材料是一类具有超高比表面积孔结构有序的有机-无机杂化材料,兼具高比表面积和半导体特性,因此具有可设计成为吸附-光催化双功能材料的潜力。本发明的铁钛双金属有机框架材料吸附-光催化双功能材料,由于具有金属有机杂化的框架结构,因而具备交强的VOCs吸附能力;由于在有机无机杂化材料中掺杂了钛元素,提高了半导体的导带位置,从而提高了材料的还原能力,因而具备了在光照条件下产生光生电子和氧气结合产生过氧负离子,进而氧化VOCs的能力。Adsorption-photocatalytic bifunctional materials have both adsorption and photocatalytic functions. Traditional materials often only have one of these functions, such as molecular sieves and activated carbon, which have a certain specific surface area to function as catalysts, but have limited potential as photocatalysts; while metal oxides such as TiO 2 and CdS have photocatalytic properties. active, but limited specific surface area and thus limited potential as an adsorbent. Metal-organic frameworks are a class of organic-inorganic hybrid materials with ultra-high specific surface area and pore structure order, which have both high specific surface area and semiconducting properties, so they have the potential to be designed as adsorption-photocatalytic bifunctional materials. The iron-titanium bimetallic organic framework material adsorption-photocatalytic bifunctional material of the present invention has a strong VOCs adsorption capacity because of the metal-organic hybrid framework structure; since the organic-inorganic hybrid material is doped with titanium element , which improves the conduction band position of the semiconductor, thereby improving the reducing ability of the material, so it has the ability to generate photogenerated electrons and oxygen combined to generate peroxy anions under illumination conditions, thereby oxidizing VOCs.

基于吸附-光催化双功能金属有机框架材料的VOCs治理新工艺原理为:双功能材料表面同时具有VOCs吸附位和光催化位,当含VOCs废气通过材料床层时,材料表面的吸附位会选择性的吸附VOCs,从而获得洁净空气;而当床层趋近吸附饱和时,在光源辐射下,材料表面富集的VOCs会经光催化位降解生成CO2和H2O,有效避免了再生过程中VOCs脱附导致的二次污染及能耗,与此同时,吸附-光催化双功能材料床层得以再生,进入下一个吸附-光催化循环。The new process principle of VOCs treatment based on adsorption-photocatalytic bifunctional metal organic framework materials is as follows: the surface of the bifunctional material has both VOCs adsorption sites and photocatalytic sites. When the VOCs-containing waste gas passes through the material bed, the adsorption sites on the material surface will be selective. When the bed is close to adsorption saturation, the VOCs enriched on the surface of the material will be degraded by photocatalytic sites to generate CO 2 and H 2 O under the radiation of the light source, which effectively avoids the regeneration process. The secondary pollution and energy consumption caused by VOCs desorption, at the same time, the adsorption-photocatalytic bifunctional material bed can be regenerated and enter the next adsorption-photocatalytic cycle.

本发明相对于现有的技术,具有如下的优点及效果:Compared with the prior art, the present invention has the following advantages and effects:

1.本发明吸附-光催化双功能材料具有高的VOCs吸附容量选择性和可见光光催化降解效率;1. The adsorption-photocatalytic bifunctional material of the present invention has high VOCs adsorption capacity selectivity and visible light photocatalytic degradation efficiency;

2.本发明工艺可在常温、常压、可见光辐射下实现VOCs吸附-光催化降解(再生)循环操作,工艺简单,能耗低,可实现含VOCs废气的半连续深度净化。2. The process of the invention can realize VOCs adsorption-photocatalytic degradation (regeneration) cycle operation under normal temperature, normal pressure and visible light radiation, the process is simple, the energy consumption is low, and the semi-continuous deep purification of VOCs-containing waste gas can be realized.

附图说明Description of drawings

图1为基于吸附-光催化双功能材料的VOCs治理工艺图;Figure 1 is a process diagram of VOCs treatment based on adsorption-photocatalytic bifunctional materials;

图2为本发明实施例1~实施例4的XRD谱图;Fig. 2 is the XRD spectrum of embodiment 1 to embodiment 4 of the present invention;

图3a为本发明实施例2的TEM-EDS图;Fig. 3a is the TEM-EDS figure of the embodiment of the present invention 2;

图3b为实例2的元素分布;Fig. 3b is the element distribution of example 2;

图4为本发明实施例1~实施例4的UV-Vis谱图;Fig. 4 is the UV-Vis spectrogram of the embodiments 1 to 4 of the present invention;

图5为本发明实施例2的价带XPS谱图;Fig. 5 is the valence band XPS spectrogram of the embodiment of the present invention 2;

图6为本发明实施例1~实施例4对甲醛、甲苯、异丙醇、苯的吸附性能图;Fig. 6 is the adsorption performance diagram of formaldehyde, toluene, isopropanol, and benzene in Examples 1 to 4 of the present invention;

图7为本发明实施例1~实施例4对甲醛、甲苯、异丙醇、苯的可见光降解性能图。7 is a graph showing the visible light degradation performance of formaldehyde, toluene, isopropanol and benzene in Examples 1 to 4 of the present invention.

具体实施方式Detailed ways

下面结合附图表和实施例对本发明作进一步的描述,但本发明要求保护的范围并不局限于实施例表述的范围。The present invention will be further described below with reference to the accompanying drawings and the embodiments, but the scope of protection of the present invention is not limited to the scope of the embodiments.

实施例1Example 1

1、双功能吸附-光催化金属有机框架材料的制备1. Preparation of bifunctional adsorption-photocatalytic metal-organic frameworks

(1)将1.054g 2-氨基对苯二甲酸和5.16g铁元素前驱体氧化铁溶于N,N-二甲基甲酰胺(DMF),加入甲醇溶剂,搅拌均匀,后加入0.26ml四氯化钛,继续搅拌均匀后,将混合液在120℃下进行水热合成反应72h。(1) Dissolve 1.054g of 2-aminoterephthalic acid and 5.16g of iron precursor iron oxide in N,N-dimethylformamide (DMF), add methanol solvent, stir evenly, and then add 0.26ml of tetrachloride Titanium was removed, and after stirring evenly, the mixture was subjected to hydrothermal synthesis reaction at 120 °C for 72 h.

(2)产物依次进行DMF和甲醇洗涤后,离心过滤提取产物,将产物放进甲醇溶液中纯化,期间定时更换溶剂,最后离心过滤提取产物,在150℃下烘干,制得铁钛双金属有机框架材料。(2) After the product is washed with DMF and methanol in sequence, the product is extracted by centrifugal filtration, the product is put into methanol solution for purification, the solvent is changed regularly during the period, and finally the product is extracted by centrifugal filtration, and dried at 150 ° C to obtain the iron-titanium bimetallic Organic frame material.

2、基于双功能吸附-光催化金属有机框架材料的VOCs治理新工艺2. A new process for VOCs treatment based on bifunctional adsorption-photocatalytic metal organic framework materials

(1)将甲醛含量为300ppm的空气以5ml/min的流速通入填充吸附-光催化双功能材料床层,吸附-光催化双功能材料床层可选择性吸附甲醛,从而获得洁净空气;(1) The air with a formaldehyde content of 300 ppm is passed into the bed filled with adsorption-photocatalytic bifunctional material at a flow rate of 5 ml/min, and the bed of adsorption-photocatalytic bifunctional material can selectively adsorb formaldehyde, thereby obtaining clean air;

(2)吸附-光催化双功能材料床层接近吸附饱和时,开启100mW/cm2光强光源光照6h,使得吸附-光催化双功能材料表面富集的VOCs发生光催化降解生成CO2和H2O,有效避免了再生过程中VOCs脱附导致的二次污染及能耗,与此同时,吸附-光催化双功能材料床层得以再生,进入下一个吸附-光催化循环。(2) When the bed of the adsorption-photocatalytic bifunctional material is close to the adsorption saturation, turn on the light source of 100 mW/ cm2 light intensity for 6 h, so that the VOCs enriched on the surface of the adsorption-photocatalytic bifunctional material undergo photocatalytic degradation to generate CO and H. 2 O, which effectively avoids the secondary pollution and energy consumption caused by the desorption of VOCs during the regeneration process. At the same time, the adsorption-photocatalytic bifunctional material bed can be regenerated and enter the next adsorption-photocatalytic cycle.

实施例2Example 2

1、双功能吸附-光催化金属有机框架材料的制备1. Preparation of bifunctional adsorption-photocatalytic metal-organic frameworks

(1)将1.054g 2-氨基对苯二甲酸和3.18g铁元素前驱体硫酸铁溶于N,N-二甲基甲酰胺(DMF),加入甲醇溶剂,搅拌均匀后,加入0.52ml硫酸氧钛,继续搅拌均匀后,将混合液在160℃下水热合成反应60h。(1) Dissolve 1.054g 2-aminoterephthalic acid and 3.18g iron precursor ferric sulfate in N,N-dimethylformamide (DMF), add methanol solvent, stir evenly, add 0.52ml oxygen sulfate Titanium, after continuing to stir evenly, the mixture was hydrothermally synthesized at 160 °C for 60 h.

(2)产物依次进行DMF和甲醇洗涤后,离心过滤提取产物,将产物放入甲醇溶液中纯化,期间定时更换溶剂,最后离心过滤提取产物,在120℃下烘干,制得铁钛双金属有机框架材料。(2) After the product is washed with DMF and methanol in turn, the product is extracted by centrifugal filtration, the product is put into methanol solution for purification, the solvent is changed regularly during the period, and finally the product is extracted by centrifugal filtration, and dried at 120 ° C to obtain the iron-titanium bimetallic Organic frame material.

2、基于双功能吸附-光催化金属有机框架材料的VOCs治理新工艺2. A new process for VOCs treatment based on bifunctional adsorption-photocatalytic metal organic framework materials

(1)将甲苯含量为200ppm的空气以10ml/min的流速通入填充吸附-光催化双功能材料床层,吸附-光催化双功能材料床层可选择性吸附甲苯,从而获得洁净空气;(1) The air with a toluene content of 200 ppm is passed into the bed filled with adsorption-photocatalytic bifunctional material at a flow rate of 10 ml/min, and the bed of adsorption-photocatalytic bifunctional material can selectively adsorb toluene, thereby obtaining clean air;

(2)吸附-光催化双功能材料床层接近吸附饱和时,开启200mW/cm2光强光源光照5h,使得吸附-光催化双功能材料表面富集的甲苯发生光催化降解生成CO2和H2O,有效避免了再生过程中甲苯脱附导致的二次污染及能耗,与此同时,吸附-光催化双功能材料床层得以再生,进入下一个吸附-光催化循环。(2) When the bed of the adsorption-photocatalytic bifunctional material is close to the adsorption saturation, turn on the light source of 200 mW/ cm2 light intensity for 5 h, so that the toluene enriched on the surface of the adsorption-photocatalytic bifunctional material undergoes photocatalytic degradation to generate CO and H. 2 O, which effectively avoids the secondary pollution and energy consumption caused by toluene desorption during the regeneration process. At the same time, the adsorption-photocatalytic bifunctional material bed can be regenerated and enter the next adsorption-photocatalytic cycle.

实施例3Example 3

1、双功能吸附-光催化金属有机框架材料的制备1. Preparation of bifunctional adsorption-photocatalytic metal-organic frameworks

(1)将1.054g 2-氨基对苯二甲酸和2.58g铁元素前驱体硝酸铁溶于N,N-二甲基甲酰胺(DMF),加入甲醇溶剂,搅拌均匀后,加入0.78ml钛酸四异丙酯,继续搅拌均匀后,将混合液在120℃下水热合成反应48h。(1) Dissolve 1.054g 2-aminoterephthalic acid and 2.58g iron precursor ferric nitrate in N,N-dimethylformamide (DMF), add methanol solvent, stir evenly, add 0.78ml titanic acid Tetraisopropyl ester, after continuing to stir evenly, the mixture was subjected to hydrothermal synthesis reaction at 120°C for 48h.

(2)产物依次进行DMF和甲醇洗涤后,离心过滤提取产物,将产物放入甲醇溶液中纯化,期间定时更换溶剂,最后离心过滤提取产物,在100℃下烘干,制得铁钛双金属有机框架材料。(2) After the product is washed with DMF and methanol in turn, the product is extracted by centrifugal filtration, the product is put into methanol solution for purification, the solvent is changed regularly during the period, and finally the product is extracted by centrifugal filtration, and dried at 100 ° C to obtain the iron-titanium bimetallic Organic frame material.

2、基于双功能吸附-光催化金属有机框架材料的VOCs治理新工艺2. A new process for VOCs treatment based on bifunctional adsorption-photocatalytic metal organic framework materials

(1)将异丙醇含量为100ppm的空气以15ml/min的流速通入填充吸附-光催化双功能材料床层,吸附-光催化双功能材料床层可选择性吸附异丙醇,从而获得洁净空气;(1) The air with the isopropanol content of 100 ppm is passed into the bed of the filled adsorption-photocatalytic bifunctional material at a flow rate of 15 ml/min, and the bed of the adsorption-photocatalytic bifunctional material can selectively adsorb isopropanol, thereby obtaining clean air;

(2)吸附-光催化双功能材料床层接近吸附饱和时,开启150mW/cm2光强光源光照4h,使得吸附-光催化双功能材料表面富集的异丙醇发生光催化降解生成CO2和H2O,有效避免了再生过程中异丙醇脱附导致的二次污染及能耗,与此同时,吸附-光催化双功能材料床层得以再生,进入下一个吸附-光催化循环。(2) When the bed of the adsorption-photocatalytic bifunctional material is close to the adsorption saturation, turn on the light source of 150 mW/ cm2 light intensity for 4 h, so that the enriched isopropanol on the surface of the adsorption-photocatalytic bifunctional material undergoes photocatalytic degradation to generate CO2 and H 2 O, which effectively avoids the secondary pollution and energy consumption caused by isopropanol desorption during the regeneration process.

实施例4Example 4

1、双功能吸附-光催化金属有机框架材料的制备1. Preparation of bifunctional adsorption-photocatalytic metal-organic frameworks

(1)将1.054g 2-氨基对苯二甲酸和1.29g铁元素前驱体氯化铁溶于N,N-二甲基甲酰胺(DMF),加入甲醇溶剂,搅拌均匀后,加入1.04ml钛酸四丁酯,继续搅拌均匀后,将混合液在150℃下水热合成反应72h。(1) Dissolve 1.054g 2-aminoterephthalic acid and 1.29g iron precursor ferric chloride in N,N-dimethylformamide (DMF), add methanol solvent, stir evenly, add 1.04ml titanium tetrabutyl acid, and after continuing to stir evenly, the mixture was subjected to a hydrothermal synthesis reaction at 150 °C for 72 h.

(2)产物依次进行DMF和甲醇洗涤后,离心过滤提取产物,将产物放入甲醇溶液中纯化,期间定时更换溶剂,最后离心过滤提取产物,在80℃下烘干,制得铁钛双金属有机框架材料。(2) After the product was washed with DMF and methanol in sequence, the product was extracted by centrifugal filtration, the product was put into methanol solution for purification, the solvent was changed regularly during the period, and finally the product was extracted by centrifugal filtration, and dried at 80 ° C to obtain the iron-titanium bimetallic Organic frame material.

2、基于双功能吸附-光催化金属有机框架材料的VOCs治理新工艺2. A new process for VOCs treatment based on bifunctional adsorption-photocatalytic metal organic framework materials

(1)将苯含量为50ppm的空气以20ml/min的流速通入填充吸附-光催化双功能材料床层,吸附-光催化双功能材料床层可选择性吸附苯,从而获得洁净空气;(1) The air with a benzene content of 50 ppm is passed into the bed filled with adsorption-photocatalytic bifunctional material at a flow rate of 20 ml/min, and the bed of adsorption-photocatalytic bifunctional material can selectively adsorb benzene, thereby obtaining clean air;

(2)吸附-光催化双功能材料床层接近吸附饱和时,开启300mW/cm2光强光源光照5h,使得吸附-光催化双功能材料表面富集的苯发生光催化降解生成CO2和H2O,有效避免了再生过程中苯脱附导致的二次污染及能耗,与此同时,吸附-光催化双功能材料床层得以再生,进入下一个吸附-光催化循环。(2) When the bed of the adsorption-photocatalytic bifunctional material is close to the adsorption saturation, turn on the light source of 300 mW/ cm2 light intensity for 5 h, so that the benzene enriched on the surface of the adsorption-photocatalytic bifunctional material undergoes photocatalytic degradation to generate CO and H. 2 O, which effectively avoids the secondary pollution and energy consumption caused by benzene desorption during the regeneration process. At the same time, the adsorption-photocatalytic bifunctional material bed can be regenerated and enter the next adsorption-photocatalytic cycle.

本发明提出一种双功能吸附-光催化金属有机框架材料及其VOCs治理新工艺,其钛含量、晶型结构、吸光范围、VOCs吸附性能和VOCs光催化降解性能如下:The present invention proposes a bifunctional adsorption-photocatalytic metal-organic framework material and a new VOCs treatment process. Its titanium content, crystal structure, light absorption range, VOCs adsorption performance and VOCs photocatalytic degradation performance are as follows:

(1)孔铁钛双金属有机框架材料的钛含量(1) Titanium content of porous iron-titanium bimetallic organic frameworks

采用Varian 715-ES等离子发射光谱分析仪对本发明实施例1~4的铁、钛含量进行分析,结果如表1所示。A Varian 715-ES plasma emission spectrometer was used to analyze the iron and titanium content of Examples 1 to 4 of the present invention, and the results are shown in Table 1.

由表1可以看出,本发明所制备的铁钛双金属有机框架材料中的铁钛含量比与投料量的变化趋势一致,最终钛含量随着前驱体中钛摩尔比的增加而增加。It can be seen from Table 1 that the iron-titanium content ratio in the iron-titanium bimetallic organic framework material prepared by the present invention is consistent with the change trend of the feeding amount, and the final titanium content increases with the increase of the titanium molar ratio in the precursor.

(2)铁钛双金属有机框架材料的晶体结构性质(2) Crystal structure properties of iron-titanium bimetallic organic frameworks

采用德国Bruker公司D8-ADVANCE型X射线衍射仪对本发明实施例1(Fe-Ti-1)、实施例2(Fe-Ti-2)、实施例3(Fe-Ti-3)和实施例4(Fe-Ti-4)的晶体结构分别进行表征,其中操作条件为:Cu靶Kα光源,辐射管内电流40mA,电压40kv,,连续扫描方式,扫描角度范围为5-40°,扫描速度为0.1秒/步,扫描步长为0.02°。Example 1 (Fe-Ti-1), Example 2 (Fe-Ti-2), Example 3 (Fe-Ti-3) and Example 4 of the present invention were analyzed by a D8-ADVANCE X-ray diffractometer from Bruker, Germany. The crystal structure of (Fe-Ti-4) was characterized respectively, and the operating conditions were: Cu target Kα light source, the current in the radiant tube was 40mA, the voltage was 40kv, the continuous scanning mode, the scanning angle range was 5-40°, and the scanning speed was 0.1 sec/step, the scan step size is 0.02°.

图2中展示了本发明实例1(Fe-Ti-1)、实施例2(Fe-Ti-2)、实施例3(Fe-Ti-3)和实施例4(Fe-Ti-4)与纯铁基MOF的XRD谱图,从图2中可以看出,随着Ti含量的增加,在8°左右的主峰有逐渐向左位移的现象,说明Ti进入晶格中替代了Fe的位置,由于Ti离子的半径大于Fe的离子半径,所以晶体框架发生扭曲增大,峰位置左移。Inventive Example 1 (Fe-Ti-1), Example 2 (Fe-Ti-2), Example 3 (Fe-Ti-3) and Example 4 (Fe-Ti-4) and The XRD pattern of pure iron-based MOF can be seen from Figure 2. With the increase of Ti content, the main peak at about 8° gradually shifts to the left, indicating that Ti enters the lattice and replaces the position of Fe. Since the radius of Ti ions is larger than that of Fe, the crystal frame is twisted and increased, and the peak position is shifted to the left.

(3)铁钛双金属有机框架材料的晶体形貌和元素分布(3) Crystal morphology and element distribution of Fe-Ti bimetallic organic frameworks

应用JEM-2100透射电子显微镜分析铁钛双金属有机框架材料的晶体形貌和元素分布。图3a示出本发明实施例2在电镜下的形貌,图3b展示出本发明实例2的元素分布。由图3a可知,该材料为长900nm,宽200nm的椭球形。另外,根据电子能谱分析发现,代表元素Fe和元素Ti可以遍布整个晶体,证明元素Fe和Ti均可以在整个框架上均匀分布。The crystal morphology and element distribution of Fe-Ti bimetallic organic frameworks were analyzed by JEM-2100 transmission electron microscope. FIG. 3a shows the morphology of Example 2 of the present invention under an electron microscope, and FIG. 3b shows the element distribution of Example 2 of the present invention. It can be seen from Figure 3a that the material is an ellipsoid with a length of 900 nm and a width of 200 nm. In addition, according to the analysis of electron energy spectrum, it is found that the representative elements Fe and Ti can be distributed throughout the whole crystal, which proves that both Fe and Ti can be uniformly distributed on the whole frame.

(4)铁钛双金属有机框架材料的紫外可见吸收光谱分析(4) UV-Vis absorption spectroscopic analysis of iron-titanium bimetallic organic frameworks

应用日本岛津公司的UV-Vis光谱仪分析铁钛双金属有机框架材料的紫外可见吸收。图4展示了本发明实例1(Fe-Ti-1)、实施例2(Fe-Ti-2)、实施例3(Fe-Ti-3)和实施例4(Fe-Ti-4)与纯铁基MOF的紫外吸收光谱,从图中可以看出,随着Ti含量的增加,吸收边带出现蓝移,说明禁带宽度在不断拉大。The UV-Vis absorption of iron-titanium bimetallic organic framework materials was analyzed by UV-Vis spectrometer from Shimadzu Corporation of Japan. Figure 4 shows the invention Example 1 (Fe-Ti-1), Example 2 (Fe-Ti-2), Example 3 (Fe-Ti-3) and Example 4 (Fe-Ti-4) with pure The UV absorption spectrum of the iron-based MOF can be seen from the figure, with the increase of Ti content, the absorption sideband appears blue-shifted, indicating that the forbidden band width is increasing.

(5)铁钛双金属有机框架材料的价带XPS谱图(5) Valence band XPS spectra of iron-titanium bimetallic organic frameworks

应用ESCALAB 250Xi X射线光电子能谱测铁钛双金属有机框架材料的价带。图5展示了本发明实例2的价带和纯铁基MOF的价带对比。由图5可知,Ti的引入可以使材料的价带升高,Fe-Ti-2的价带值为2.38eV,Fe-MOF为2.64eV,结合紫外吸收光谱可知,导带相比纯铁基MOF将有更高的抬升,样品的还原能力也增强。The valence band of iron-titanium bimetallic organic frameworks was measured by ESCALAB 250Xi X-ray photoelectron spectroscopy. FIG. 5 shows the comparison of the valence band of Example 2 of the present invention and the valence band of pure iron-based MOF. It can be seen from Figure 5 that the introduction of Ti can increase the valence band of the material. The valence band of Fe-Ti-2 is 2.38 eV, and Fe-MOF is 2.64 eV. Combined with the UV absorption spectrum, it can be seen that the conduction band is higher than that of pure iron base. The MOF will have a higher lift and the reducing power of the sample will also be enhanced.

(6)铁钛双金属有机框架材料对甲醛、甲苯、异丙醇、苯的吸附性能(6) Adsorption properties of iron-titanium bimetallic organic framework materials for formaldehyde, toluene, isopropanol and benzene

应用美国Quantachrome公司AUTOSORB-1气体吸附仪测定本发明实例2(Fe-Ti-2)的对VOC的饱和吸附量。由图6可知,Fe-Ti-2对甲醛、甲苯、异丙醇、苯都有较高的吸附容量,说明该材料具备吸附VOC的能力。The saturated adsorption amount of VOC in Example 2 (Fe-Ti-2) of the present invention was measured by using the AUTOSORB-1 gas adsorption instrument of Quantachrome Company in the United States. It can be seen from Figure 6 that Fe-Ti-2 has high adsorption capacity for formaldehyde, toluene, isopropanol, and benzene, indicating that the material has the ability to adsorb VOCs.

(7)铁钛双金属有机框架材料对甲醛、甲苯、异丙醇、苯的可见光降解性能(7) Visible light degradation performance of iron-titanium bimetallic organic framework materials to formaldehyde, toluene, isopropanol and benzene

应用北京泊菲莱公司的PLS-SXE300型号氙灯作为光源,采用420nm滤光片作为光源。采用GC9560型气相色谱仪、氢火焰离子化检测器检测VOC含量。反应容器100ml,通入VOC(甲醛、甲苯、异丙醇或者苯)浓度300ppm的干空气,达到吸附平衡后,光照6h,取样测试剩余VOC含量。The PLS-SXE300 xenon lamp of Beijing Bofeilai Company was used as the light source, and the 420nm filter was used as the light source. The VOC content was detected by GC9560 gas chromatograph and hydrogen flame ionization detector. A 100ml reaction vessel was filled with dry air with a concentration of 300ppm of VOC (formaldehyde, toluene, isopropanol or benzene), after reaching the adsorption equilibrium, the light was illuminated for 6h, and samples were taken to test the remaining VOC content.

图7展示了本发明实例2(Fe-Ti-2)的对VOC的光催化降解率,对甲醛、甲苯、异丙醇、苯的降解率分别为98%、90%、95%、86%,说明该样品具有较高的光催化反应能力。Figure 7 shows the photocatalytic degradation rate of VOC of Example 2 (Fe-Ti-2) of the present invention, and the degradation rates of formaldehyde, toluene, isopropanol, and benzene are 98%, 90%, 95%, and 86%, respectively. , indicating that the sample has high photocatalytic reaction ability.

表1本发明铁钛双金属金属有机框架材料的铁、钛含量Table 1 iron and titanium content of iron-titanium bimetallic metal organic framework material of the present invention

Figure BDA0001210945210000081
Figure BDA0001210945210000081

上述实施例为本发明较佳的实施方式,但本发明的实施方式并不受上述实施例的限制,其他的任何未背离本发明的精神实质与原理下所作的改变、修饰、替代、组合、简化,均应为等效的置换方式,都包含在本发明的保护范围之内。The above-mentioned embodiments are preferred embodiments of the present invention, but the embodiments of the present invention are not limited by the above-mentioned embodiments, and any other changes, modifications, substitutions, combinations, The simplification should be equivalent replacement manners, which are all included in the protection scope of the present invention.

Claims (3)

1.一种吸附-光催化双功能材料的制备方法,其特征在于,包括如下步骤:1. a preparation method of adsorption-photocatalytic bifunctional material, is characterized in that, comprises the steps: (1)将2-氨基对苯二甲酸和铁元素前驱体溶于N,N-二甲基甲酰胺(DMF),加入甲醇溶剂,搅拌均匀,加入钛元素前驱体,继续搅拌均匀后,将混合液进行水热合成反应;(1) Dissolve 2-aminoterephthalic acid and iron precursor in N,N-dimethylformamide (DMF), add methanol solvent, stir evenly, add titanium precursor, continue stirring, The mixed solution is subjected to a hydrothermal synthesis reaction; (2)产物依次进行DMF洗和甲醇洗涤后,离心过滤提取产物,将产物放入甲醇溶液中纯化,期间定时更换溶剂,最后离心过滤提取产物,烘干,制得铁钛双金属有机框架材料,即吸附-光催化双功能材料;(2) After the product is washed with DMF and methanol in sequence, the product is extracted by centrifugal filtration, the product is put into methanol solution for purification, the solvent is regularly replaced during the period, and finally the product is extracted by centrifugal filtration, and dried to obtain an iron-titanium bimetallic organic framework material , namely adsorption-photocatalytic bifunctional materials; 所述铁元素前驱体为硝酸铁、氯化铁、硫酸铁或者氧化铁;所述钛元素前驱体为钛酸四丁酯、钛酸四异丙酯、硫酸氧钛、四氯化钛或硝酸钛;所述铁元素前驱体与钛元素前驱体满足钛与铁的摩尔比为0.5~2;所述2-氨基对苯二甲酸与铁元素前驱体的摩尔比为0.5~3;所述水热合成反应溶液温度为120~180℃;所述水热合成反应时间为48~72 h;所述离心转速为6000~9000 r/min;所述烘干温度为80~150℃;The iron element precursor is iron nitrate, iron chloride, iron sulfate or iron oxide; the titanium element precursor is tetrabutyl titanate, tetraisopropyl titanate, titanium oxysulfate, titanium tetrachloride or nitric acid titanium; the iron element precursor and the titanium element precursor satisfy that the molar ratio of titanium to iron is 0.5-2; the molar ratio of the 2-aminoterephthalic acid to the iron element precursor is 0.5-3; the water The temperature of the thermal synthesis reaction solution is 120-180 °C; the hydrothermal synthesis reaction time is 48-72 h; the centrifugal rotation speed is 6000-9000 r/min; the drying temperature is 80-150 °C; 所述铁钛双金属有机框架双功能催化吸附材料的Ti质量百分数为0.5~3.0 wt.%;吸光边带在700~800 nm;所述铁钛双金属有机框架双功能催化吸附材料的晶体尺寸为长在500~800 nm、宽在100~600 nm;The mass percentage of Ti of the iron-titanium bimetallic organic framework bifunctional catalytic adsorption material is 0.5-3.0 wt.%; the light absorption sideband is 700-800 nm; the crystal size of the iron-titanium bimetallic organic framework bifunctional catalytic adsorption material is 500~800 nm long and 100~600 nm wide; 所述吸附-光催化双功能材料在挥发性有机气体治理工艺中的应用,包括如下步骤:The application of the adsorption-photocatalytic bifunctional material in the volatile organic gas treatment process includes the following steps: (1)将含VOCs的空气通入填充吸附-光催化双功能材料床层,吸附-光催化双功能材料床层吸附VOCs,从而获得洁净空气;(1) Pass the air containing VOCs into the bed filled with adsorption-photocatalytic bifunctional material, and the bed of adsorption-photocatalytic bifunctional material adsorbs VOCs, thereby obtaining clean air; (2)吸附-光催化双功能材料床层接近吸附饱和时,开启光源,使得吸附-光催化双功能材料表面富集的VOCs发生光催化降解生成CO2和H2O,与此同时,吸附-光催化双功能材料床层得以再生,进入下一个吸附-光催化循环。(2) When the adsorption-photocatalytic bifunctional material bed is close to adsorption saturation, the light source is turned on, so that the VOCs enriched on the surface of the adsorption-photocatalytic bifunctional material undergo photocatalytic degradation to generate CO 2 and H 2 O. At the same time, the adsorption - The photocatalytic bifunctional material bed is regenerated to enter the next adsorption-photocatalytic cycle. 2.根据权利要求1中所述吸附-光催化双功能材料的制备方法,其特征在于,步骤(1)中,所述VOCs为甲苯、苯、甲醛或者异丙醇;所述VOCs在空气中的含量为50~300 ppm;所述气体流速为5~20 mL/min;步骤(2)中,所述再生环境为室温;所述光催化再生光源为100~300mW/cm2;再生时间为2~6 h。2. according to the preparation method of adsorption-photocatalytic bifunctional material described in claim 1, it is characterized in that, in step (1), described VOCs is toluene, benzene, formaldehyde or isopropanol; Described VOCs is in air The content is 50~300 ppm; Described gas flow rate is 5~20 mL/min; In step (2), described regeneration environment is room temperature; Described photocatalytic regeneration light source is 100~300mW/cm ; The regeneration time is 2 to 6 hours. 3.根据权利要求2中所述吸附-光催化双功能材料的制备方法,其特征在于,VOCs的吸附率达95 %以上;光催化再生后材料的VOCs吸附性能保持原来的90 %以上。3. according to the preparation method of adsorption-photocatalytic bifunctional material described in claim 2, it is characterized in that, the adsorption rate of VOCs reaches more than 95%; The VOCs adsorption performance of material after photocatalytic regeneration keeps original more than 90%.
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