[go: up one dir, main page]

CN104525222B - A kind of preparation method of carbon nanotube composite ZnIn2S4 green deep water treatment agent - Google Patents

A kind of preparation method of carbon nanotube composite ZnIn2S4 green deep water treatment agent Download PDF

Info

Publication number
CN104525222B
CN104525222B CN201410843621.6A CN201410843621A CN104525222B CN 104525222 B CN104525222 B CN 104525222B CN 201410843621 A CN201410843621 A CN 201410843621A CN 104525222 B CN104525222 B CN 104525222B
Authority
CN
China
Prior art keywords
cnt
znin
treatment agent
water treatment
preparation
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.)
Expired - Fee Related
Application number
CN201410843621.6A
Other languages
Chinese (zh)
Other versions
CN104525222A (en
Inventor
刘保江
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
SHANGHAI SANYI ENVIRONMENT TECHNOLOGY CO LTD
Donghua University
Original Assignee
SHANGHAI SANYI ENVIRONMENT TECHNOLOGY CO LTD
Donghua University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by SHANGHAI SANYI ENVIRONMENT TECHNOLOGY CO LTD, Donghua University filed Critical SHANGHAI SANYI ENVIRONMENT TECHNOLOGY CO LTD
Priority to CN201410843621.6A priority Critical patent/CN104525222B/en
Publication of CN104525222A publication Critical patent/CN104525222A/en
Application granted granted Critical
Publication of CN104525222B publication Critical patent/CN104525222B/en
Expired - Fee Related legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Landscapes

  • Physical Water Treatments (AREA)
  • Water Treatment By Sorption (AREA)
  • Solid-Sorbent Or Filter-Aiding Compositions (AREA)

Abstract

本发明涉及一种碳纳米管复合ZnIn2S4绿色深度水处理剂的制备方法,包括:(1)将碳纳米管依次羧基化、氨基化改性、2,4,6‑三氟‑5‑氯嘧啶改性制备反应型碳纳米管;(2)将纳米ZnIn2S4、稳定剂、模板剂和反应型碳纳米管加入到磷酸盐缓冲液中,搅拌30~60min,形成悬浊液;(3)过滤干燥得产物即可。本发明的成本低廉,制备方法简单,对设备的要求低,可操作性好;本发明的水处理剂可以去除水中高浓度有机污染物,适用于各种废水的深度处理,环保无二次污染,且具有抗菌、除臭、可以吸附其他重金属离子等优点。The invention relates to a preparation method of a carbon nanotube composite ZnIn 2 S 4 green deep water treatment agent, comprising: (1) sequentially carboxylation, amination modification, 2,4,6-trifluoro-5 carbon nanotubes ‑Chloropyrimidine modification to prepare reactive carbon nanotubes; (2) Add nano ZnIn 2 S 4 , stabilizer, template agent and reactive carbon nanotubes to phosphate buffer, stir for 30-60min to form a suspension ; (3) filter and dry to get the product. The invention has the advantages of low cost, simple preparation method, low requirements on equipment, and good operability; the water treatment agent of the invention can remove high-concentration organic pollutants in water, is suitable for advanced treatment of various waste water, and is environmentally friendly without secondary pollution , and has the advantages of antibacterial, deodorizing, and can adsorb other heavy metal ions.

Description

一种碳纳米管复合ZnIn2S4绿色深度水处理剂的制备方法A kind of preparation method of carbon nanotube composite ZnIn2S4 green deep water treatment agent

技术领域 technical field

本发明属于水处理剂领域,特别涉及一种碳纳米管复合ZnIn2S4绿色深度水处理剂的制备方法。 The invention belongs to the field of water treatment agents, in particular to a preparation method of a carbon nanotube composite ZnIn 2 S 4 green deep water treatment agent.

背景技术 Background technique

全球仅约10%的水是直接为人类所用。最大的份额,70%用于农业,剩余的20%为工业用。中国的排污约为全球的20%,而它只得到全球的5%的新鲜水。因此,解决污染问题已列入议事日程。在纺织印染、皮革、造纸行业加工过程中,大量使用了污染环境和对人体有害的助剂,这些助剂大多以液体的形态排放而污染环境,生物降解性差,毒性大,游离甲醛含量高,重金属离子的含量超标。其中,印染湿整理更是无可争议地成为水污染大户。从上浆开始到退浆、水洗、练漂、丝光,然后染色印花、可能还需涂层,按此流程每道工序都涉及水洗,而每道工序每千克材料需20L耗水。结果是湿整理过程中每千克原棉的用水量加起来多达200L。当一件标准的男式衬衣定制后在商店橱窗展示时,超过2000L水在生产加工它时被用掉了(布料:纯棉,125g/m)。 Only about 10% of the world's water is directly used by humans. The largest share, 70%, is used in agriculture, and the remaining 20% is used in industry. China's sewage is about 20% of the world's, but it only gets 5% of the world's fresh water. Therefore, solving the pollution problem is on the agenda. In the processing of textile printing and dyeing, leather, and papermaking industries, a large number of additives that pollute the environment and are harmful to the human body are used. Most of these additives are discharged in the form of liquid and pollute the environment. They have poor biodegradability, high toxicity, and high content of free formaldehyde. The content of heavy metal ions exceeds the standard. Among them, printing and dyeing wet finishing is indisputably a major water polluter. From sizing to desizing, washing, bleaching, mercerizing, dyeing and printing, and possibly coating, each process involves washing, and each process requires 20L of water per kilogram of material. The result is up to 200 liters of water per kilogram of raw cotton added up during wet finishing. When a standard men's shirt is customized and displayed in the shop window, more than 2000L of water is used in the production and processing of it (fabric: pure cotton, 125g/m).

目前使用的处理废水的方法主要有:物理分离法、生物降解法、化学分解法,但这些方法都存在一定的局限性,不利于可持续发展。因而,人们开始致力于开发高效、低能耗、适用范围广和有深度氧化能力的污染物清除技术。近年来,很多学者将ZnIn2S4用于光催化降解水中有机污染物,将ZnIn2S4负载到碳纳米管上,制备高效的光催化剂成为当前研究的热点。 The methods currently used to treat wastewater mainly include: physical separation, biodegradation, and chemical decomposition, but these methods have certain limitations and are not conducive to sustainable development. Therefore, people began to devote themselves to the development of pollutant removal technology with high efficiency, low energy consumption, wide application range and deep oxidation ability. In recent years, many scholars have used ZnIn 2 S 4 for photocatalytic degradation of organic pollutants in water, and loading ZnIn 2 S 4 on carbon nanotubes to prepare efficient photocatalysts has become a current research hotspot.

发明内容 Contents of the invention

本发明所要解决的技术问题是提供一种碳纳米管复合ZnIn2S4绿色深度水处理剂的制备方法,该方法操作简单,成本低廉,对设备的要求低;水处理剂适用于各种废水的深度处理,环保无二次污染。 The technical problem to be solved by the present invention is to provide a preparation method of carbon nanotube composite ZnIn 2 S 4 green deep water treatment agent, the method is simple to operate, low in cost, and has low requirements on equipment; the water treatment agent is suitable for various waste water Advanced treatment, environmental protection and no secondary pollution.

本发明的一种碳纳米管复合ZnIn2S4绿色深度水处理剂的制备方法,包括: A kind of preparation method of carbon nanotube composite ZnIn 2 S 4 green advanced water treatment agent of the present invention, comprising:

(1)将碳纳米管在H2SO4和HNO3混合液中室温超声反应30~60min,水洗到中性,室温真空烘干,得到羧基化碳纳米管;然后将羧基化碳纳米管分散到过量二乙烯三胺中,加入2-(7-偶氮苯并三氮唑)-N,N,N',N'-四甲基脲六氟磷酸酯,40~50℃反应5~6h,乙醇洗涤,室温真空烘干,得到氨基化碳纳米管;然后将氨基化碳纳米管超声分散到水和丙酮的混合液中,调节pH值为5~6,冰水浴滴加2,4,6-三氟-5-氯嘧啶,调节pH值为6~6.5,20~30℃超声反应24~48h,乙醇洗涤,水洗,室温真空烘干,辐照(在222nm准分子紫外光源下 辐照3min)得到反应型碳纳米管; (1) Ultrasonically react the carbon nanotubes in a mixture of H 2 SO 4 and HNO 3 at room temperature for 30-60 minutes, wash with water until neutral, and dry in vacuum at room temperature to obtain carboxylated carbon nanotubes; then disperse the carboxylated carbon nanotubes Add 2-(7-azobenzotriazole)-N,N,N',N'-tetramethyluronium hexafluorophosphate to excess diethylenetriamine, react at 40~50℃ for 5~6h , washed with ethanol, and vacuum-dried at room temperature to obtain aminated carbon nanotubes; then ultrasonically disperse the aminated carbon nanotubes into a mixture of water and acetone, adjust the pH value to 5-6, add 2,4, 6-trifluoro-5-chloropyrimidine, adjust the pH value to 6-6.5, 20-30 ℃ ultrasonic reaction 24-48h, ethanol washing, water washing, room temperature vacuum drying, irradiation (irradiation under 222nm excimer ultraviolet light source 3min) to obtain reactive carbon nanotubes;

(2)将纳米ZnIn2S4、稳定剂、模板剂和步骤(1)中的反应型碳纳米管加入到磷酸盐缓冲液中,搅拌30~60min,形成悬浊液;其中,纳米ZnIn2S4与反应型碳纳米管的质量比为1:5~1:20; (2) Add nano-ZnIn 2 S 4 , stabilizers, templates, and reactive carbon nanotubes in step (1) into phosphate buffer, stir for 30-60 minutes to form a suspension; wherein, nano-ZnIn 2 The mass ratio of S4 to reactive carbon nanotubes is 1: 5 to 1:20;

(3)用碱性溶液调节pH值为5~6,加热至80~100℃回流6~24h并过滤,得到碳纳米管复合ZnIn2S4绿色深度水处理剂。 (3) Adjust the pH value to 5-6 with an alkaline solution, heat to 80-100° C. to reflux for 6-24 hours and filter to obtain a carbon nanotube composite ZnIn 2 S 4 green deep water treatment agent.

所述步骤(1)中的碳纳米管与H2SO4和HNO3混合液的比例为10~20g:4L;其中,H2SO4和HNO3的体积比为1:1~5:1。 The ratio of carbon nanotubes to H 2 SO 4 and HNO 3 mixture in the step (1) is 10-20g:4L; wherein, the volume ratio of H 2 SO 4 and HNO 3 is 1:1-5:1 .

所述步骤(1)中的羧基化碳纳米管与2-(7-偶氮苯并三氮唑)-N,N,N',N'-四甲基脲六氟磷酸的质量比为5~8:0.1~0.6。 The mass ratio of the carboxylated carbon nanotubes in the step (1) to 2-(7-azobenzotriazole)-N,N,N',N'-tetramethyluronium hexafluorophosphoric acid is 5 ~8:0.1~0.6.

所述步骤(1)中的氨基化碳纳米管与水和丙酮的混合液的比例为4~4.5g:1L;其中,水和丙酮的体积比为3:1~5:1。 The ratio of the aminated carbon nanotube to the mixture of water and acetone in the step (1) is 4-4.5g:1L; wherein, the volume ratio of water and acetone is 3:1-5:1.

所述步骤(1)中的氨基化碳纳米管与2,4,6-三氟-5-氯嘧啶的质量比为4~4.5:4~6。 The mass ratio of the aminated carbon nanotubes to 2,4,6-trifluoro-5-chloropyrimidine in the step (1) is 4-4.5:4-6.

所述步骤(1)中采用碳酸钠溶液调节pH值。 In the step (1), sodium carbonate solution is used to adjust the pH value.

所述步骤(2)中的纳米ZnIn2S4浓度为0.01~0.2mol/L。 The nano ZnIn 2 S 4 concentration in the step (2) is 0.01-0.2 mol/L.

所述步骤(2)中的稳定剂为乙二胺四乙酸二钠、乙二胺四乙酸四钠、葡萄糖酸钠、丁烷四羧酸中的一种;稳定剂浓度为0.01~0.1mol/L。 The stabilizer in the step (2) is one of disodium edetate, tetrasodium edetate, sodium gluconate, butane tetracarboxylic acid; the concentration of stabilizer is 0.01~0.1mol/ L.

所述步骤(2)中的模板剂为质量比1:3的三嵌段聚醚P123和三嵌段共聚物F127的混合物;模板剂浓度为0.01~0.1mol/L。 The template in the step (2) is a mixture of tri-block polyether P123 and tri-block copolymer F127 with a mass ratio of 1:3; the template concentration is 0.01-0.1 mol/L.

所述步骤(2)中的磷酸盐缓冲液由浓度0.025~0.05mol/L磷酸二氢钠和0.05~0.1mol/L磷酸氢钠组成。 The phosphate buffer in the step (2) is composed of 0.025-0.05 mol/L sodium dihydrogen phosphate and 0.05-0.1 mol/L sodium hydrogen phosphate.

所述步骤(3)中的碱性溶液为浓度0.5mol/L~1.5mol/L的氢氧化钠或氢氧化钾的水溶液。 The alkaline solution in the step (3) is an aqueous solution of sodium hydroxide or potassium hydroxide with a concentration of 0.5mol/L˜1.5mol/L.

碳纳米管作为一种多孔物质,具有特殊的层间特性,可在其表面负载纳米ZnIn2S4微粒,制备成负载型催化剂。这种负载型光催化剂可以提高光催化剂的分散性,利于回收重复利用。 As a porous substance, carbon nanotubes have special interlayer characteristics, and can be loaded with nano ZnIn 2 S 4 particles on their surface to prepare supported catalysts. The supported photocatalyst can improve the dispersibility of the photocatalyst, which is beneficial to recycling and reuse.

本发明利用碳纳米管的多孔、吸附能力强、与水易分离等特点和纳米ZnIn2S4的光催化活性结合起来,将纳米ZnIn2S4成功地负载到碳纳米管上,制备成可以悬浮于废水中而又可以顺利与水分离的高催化活性的可见光光催化材料,并且将其应用于废水的深度处理,可以实现对水中高浓度有机污染物氧化去除,而不是转移到其他地方,是一个环保型 的工艺技术。 The present invention combines the characteristics of carbon nanotubes such as porosity, strong adsorption capacity, and easy separation from water with the photocatalytic activity of nano-ZnIn 2 S 4 to successfully load nano-ZnIn 2 S 4 on carbon nanotubes to prepare a Visible light photocatalytic materials with high catalytic activity that are suspended in wastewater and can be successfully separated from water, and applied to the advanced treatment of wastewater, can realize the oxidation and removal of high-concentration organic pollutants in water instead of transferring them to other places. It is an environmentally friendly process technology.

有益效果Beneficial effect

(1)本发明成本低廉,制备方法简单,对设备的要求低,可操作性好; (1) The present invention has low cost, simple preparation method, low requirement on equipment, and good operability;

(2)本发明的水处理剂可以去除水中高浓度有机污染物,适用于各种废水的深度处理,环保无二次污染,且具有抗菌、除臭、可以吸附其他重金属离子等优点; (2) The water treatment agent of the present invention can remove high-concentration organic pollutants in water, is suitable for advanced treatment of various waste water, is environmentally friendly and has no secondary pollution, and has the advantages of antibacterial, deodorizing, and can adsorb other heavy metal ions;

(3)本发明的水处理剂可以克服现有铋基水处理剂的不足,水处理效果好,可以循环使用。 (3) The water treatment agent of the present invention can overcome the deficiency of the existing bismuth-based water treatment agent, has good water treatment effect and can be recycled.

具体实施方式 detailed description

下面结合具体实施例,进一步阐述本发明。应理解,这些实施例仅用于说明本发明而不用于限制本发明的范围。此外应理解,在阅读了本发明讲授的内容之后,本领域技术人员可以对本发明作各种改动或修改,这些等价形式同样落于本申请所附权利要求书所限定的范围。 Below in conjunction with specific embodiment, further illustrate the present invention. It should be understood that these examples are only used to illustrate the present invention and are not intended to limit the scope of the present invention. In addition, it should be understood that after reading the teachings of the present invention, those skilled in the art can make various changes or modifications to the present invention, and these equivalent forms also fall within the scope defined by the appended claims of the present application.

实施例1 Example 1

(1)将10g碳纳米管在4L体积比为1:1的H2SO4和HNO4混合液中室温超声反应30min,水洗到中性,室温真空烘干48h,得到5g羧基化碳纳米管;然后将上述5g羧基化碳纳米管分散到过量二乙烯三胺中,加入100mg 2-(7-偶氮苯并三氮唑)-N,N,N',N'-四甲基脲六氟磷酸酯,40℃反应5h,乙醇洗涤,室温真空烘干48h,得到4g氨基化碳纳米管;最后将4g氨基化碳纳米管超声分散在1L体积比为3:1的水和丙酮的混合液中,用碳酸钠溶液调节pH值为5,冰水浴滴加4g 2,4,6-三氟-5-氯嘧啶,用碳酸钠溶液调节pH值为6,20℃超声反应24h,乙醇洗涤,水洗,室温真空烘干48h,在222nm准分子紫外光源下辐照3min得到反应型碳纳米管; (1) 10g of carbon nanotubes were ultrasonically reacted at room temperature for 30min in 4L of H 2 SO 4 and HNO 4 mixed solution with a volume ratio of 1:1, washed with water until neutral, and vacuum-dried at room temperature for 48h to obtain 5g of carboxylated carbon nanotubes ; Then the above-mentioned 5g carboxylated carbon nanotubes were dispersed in excess diethylenetriamine, and 100mg 2-(7-azobenzotriazole)-N,N,N',N'-tetramethylurea hexa Fluorophosphate, reacted at 40°C for 5 hours, washed with ethanol, and dried in vacuum at room temperature for 48 hours to obtain 4g of aminated carbon nanotubes; finally, 4g of aminated carbon nanotubes were ultrasonically dispersed in 1L of a mixture of water and acetone with a volume ratio of 3:1 In the solution, adjust the pH value to 5 with sodium carbonate solution, add 4 g of 2,4,6-trifluoro-5-chloropyrimidine dropwise in an ice-water bath, adjust the pH value to 6 with sodium carbonate solution, react with ultrasonic at 20°C for 24 hours, wash with ethanol , washed with water, vacuum-dried at room temperature for 48 hours, and irradiated under a 222nm excimer ultraviolet light source for 3 minutes to obtain reactive carbon nanotubes;

(2)将纳米ZnIn2S4、乙二胺四乙酸二钠、质量比为1:3的三嵌段聚醚P123和三嵌段共聚物F127的混合物和上述步骤(1)中反应型碳纳米管加入到浓度为0.025mol/L磷酸二氢钠和0.05mol/L磷酸氢钠组成的缓冲液中,搅拌30min,形成悬浊液;其中纳米ZnIn2S4的浓度为0.01mol/L、稳定剂的浓度为0.01mol/L、模板剂的浓度为0.05mol/L。 (2) The mixture of nano ZnIn 2 S 4 , disodium edetate, triblock polyether P123 and triblock copolymer F127 with a mass ratio of 1:3 and the reactive carbon in the above step (1) The nanotubes were added to the buffer solution composed of 0.025mol/L sodium dihydrogen phosphate and 0.05mol/L sodium hydrogen phosphate, and stirred for 30min to form a suspension; the concentration of nano ZnIn 2 S 4 was 0.01mol/L, The concentration of the stabilizer is 0.01mol/L, and the concentration of the template is 0.05mol/L.

(3)用浓度0.5mol/L的氢氧化钠水溶液调节上述悬浊液的pH值为5,加热80℃下,回流6h,过滤,得反应产物;其中纳米ZnIn2S4与碳纳米管的质量比为1:5。 (3) Adjust the pH value of the above-mentioned suspension to 5 with an aqueous sodium hydroxide solution with a concentration of 0.5mol/L, heat at 80° C., reflux for 6 hours, and filter to obtain a reaction product; wherein nano-ZnIn 2 S 4 and carbon nanotubes The mass ratio is 1:5.

实施例2 Example 2

(1)将10g碳纳米管在4L体积比为3:1的H2SO4和HNO4混合液中室温超声反应45min,水洗到中性,室温真空烘干54h,得到6.5g羧基化碳纳米管;然后将上述5g羧基化碳纳米管分散到过量二乙烯三胺中,加入300mg 2-(7-偶氮苯并三氮唑)-N,N,N',N'-四甲基脲六氟磷酸酯,45℃反应5h,乙醇洗涤,室温真空烘干48h,得到4.2g氨基化碳纳米管;最后将4.2g氨基化碳纳米管超声分散在1L体积比为4:1的水和丙酮的混合液中,用碳酸钠溶液调节pH值为5.5,冰水浴滴加5g 2,4,6-三氟-5-氯嘧啶,用碳酸钠溶液调节pH值为6.2,25℃超声反应36h,乙醇洗涤,水洗,室温真空烘干48h,在222nm准分子紫外光源下辐照3min得到反应型碳纳米管; (1) 10 g of carbon nanotubes were ultrasonically reacted at room temperature for 45 min in 4 L of H 2 SO 4 and HNO 4 mixed solution with a volume ratio of 3:1, washed with water until neutral, and vacuum-dried at room temperature for 54 h to obtain 6.5 g of carboxylated carbon nanotubes. tube; then the above 5g carboxylated carbon nanotubes were dispersed into excess diethylenetriamine, and 300mg 2-(7-azobenzotriazole)-N,N,N',N'-tetramethylurea was added Hexafluorophosphate, reacted at 45°C for 5 hours, washed with ethanol, and dried in vacuum at room temperature for 48 hours to obtain 4.2 g of aminated carbon nanotubes; finally, ultrasonically dispersed 4.2 g of aminated carbon nanotubes in 1 L of water with a volume ratio of 4:1 and In the mixed solution of acetone, use sodium carbonate solution to adjust the pH value to 5.5, add 5g of 2,4,6-trifluoro-5-chloropyrimidine dropwise in an ice-water bath, use sodium carbonate solution to adjust the pH value to 6.2, and conduct ultrasonic reaction at 25°C for 36 hours , washed with ethanol, washed with water, dried in vacuum at room temperature for 48 hours, and irradiated for 3 minutes under a 222nm excimer ultraviolet light source to obtain reactive carbon nanotubes;

(2)将纳米ZnIn2S4、葡萄糖酸钠、质量比为1:3的三嵌段聚醚P123和三嵌段共聚物F127的混合物和上述步骤(1)中反应型碳纳米管加入到浓度为0.03mol/L磷酸二氢钠和0.05mol/L磷酸氢钠组成的缓冲液中,搅拌45min,形成悬浊液;其中纳米ZnIn2S4的浓度为0.01mol/L、稳定剂的浓度为0.03mol/L、模板剂的浓度为0.07mol/L。 (2) The mixture of nano-ZnIn 2 S 4 , sodium gluconate, tri-block polyether P123 and tri-block copolymer F127 with a mass ratio of 1:3 and the reactive carbon nanotubes in the above step (1) were added to The concentration is 0.03mol/L sodium dihydrogen phosphate and 0.05mol/L sodium hydrogen phosphate in the buffer solution, stirring for 45min to form a suspension; the concentration of nano ZnIn 2 S 4 is 0.01mol/L, the concentration of stabilizer is 0.03mol/L, and the concentration of template agent is 0.07mol/L.

(3)用浓度0.5mol/L的氢氧化钠水溶液调节上述悬浊液的pH值为7,加热90℃下,回流16h,过滤,得反应产物;其中纳米ZnIn2S4碳纳米管的质量比为1:15。 (3) Adjust the pH value of the above-mentioned suspension to 7 with an aqueous sodium hydroxide solution with a concentration of 0.5mol/L, heat at 90°C, reflux for 16h, and filter to obtain a reaction product; wherein the mass of nano ZnIn 2 S 4 carbon nanotubes The ratio is 1:15.

实施例3 Example 3

(1)将10g碳纳米管在4L体积比为5:1的H2SO4和HNO4混合液中室温超声反应60min,水洗到中性,室温真空烘干60h,得到8g羧基化碳纳米管;然后将上述8g羧基化碳纳米管分散到过量二乙烯三胺中,加入600mg 2-(7-偶氮苯并三氮唑)-N,N,N',N'-四甲基脲六氟磷酸酯,50℃反应5h,乙醇洗涤,室温真空烘干48h,得到4.5g氨基化碳纳米管;最后将4.5g氨基化碳纳米管超声分散在1L体积比为5:1的水和丙酮的混合液中,用碳酸钠溶液调节pH值为6,冰水浴滴加6g 2,4,6-三氟-5-氯嘧啶,用碳酸钠溶液调节pH值为6.5,30℃超声反应48h,乙醇洗涤,水洗,室温真空烘干48h,在222nm准分子紫外光源下辐照3min得到反应型碳纳米管; (1) 10 g of carbon nanotubes were ultrasonically reacted at room temperature for 60 min in 4 L of H 2 SO 4 and HNO 4 mixed solution with a volume ratio of 5:1, washed with water until neutral, and vacuum-dried at room temperature for 60 h to obtain 8 g of carboxylated carbon nanotubes ; Then the above-mentioned 8g carboxylated carbon nanotubes were dispersed in excess diethylenetriamine, and 600mg 2-(7-azobenzotriazole)-N,N,N',N'-tetramethylurea hexa Fluorophosphate, reacted at 50°C for 5h, washed with ethanol, and dried in vacuum at room temperature for 48h to obtain 4.5g of aminated carbon nanotubes; finally, 4.5g of aminated carbon nanotubes were ultrasonically dispersed in 1L of water and acetone with a volume ratio of 5:1 In the mixed solution, adjust the pH value to 6 with sodium carbonate solution, add 6 g of 2,4,6-trifluoro-5-chloropyrimidine dropwise in an ice-water bath, adjust the pH value to 6.5 with sodium carbonate solution, and perform ultrasonic reaction at 30°C for 48 hours. Washing with ethanol, washing with water, vacuum drying at room temperature for 48 hours, and irradiating for 3 minutes under a 222nm excimer ultraviolet light source to obtain reactive carbon nanotubes;

(2)将纳米ZnIn2S4、丁烷四羧酸、质量比为1:3的三嵌段聚醚P123和三嵌段共聚物F127的混合物和上述步骤(1)中反应型碳纳米管加入到浓度为0.05mol/L磷酸二氢钠和0.1mol/L磷酸氢钠组成的缓冲液中,搅拌60min,形成悬浊液;其中纳米ZnIn2S4的浓度0.15mol/L、稳定剂的浓度为0.05mol/L、模板剂的浓度为0.1mol/L。 (2) the mixture of nanometer ZnIn 2 S 4 , butane tetracarboxylic acid, mass ratio 1:3 triblock polyether P123 and triblock copolymer F127 and reactive carbon nanotubes in the above step (1) Add it into the buffer solution with a concentration of 0.05mol/L sodium dihydrogen phosphate and 0.1mol/L sodium hydrogen phosphate, stir for 60min to form a suspension; wherein the concentration of nano ZnIn 2 S 4 is 0.15mol/L, the concentration of stabilizer The concentration is 0.05 mol/L, and the concentration of template agent is 0.1 mol/L.

(3)用浓度1.5mol/L的氢氧化钾水溶液调节上述悬浊液的pH值为9,加热100℃下,回流24h,过滤,得反应产物;其中纳米ZnIn2S4与碳纳米管的质量比为1:20。 (3) Adjust the pH value of the above-mentioned suspension to 9 with an aqueous potassium hydroxide solution with a concentration of 1.5mol/L, heat at 100° C., reflux for 24 hours, and filter to obtain a reaction product; wherein nano-ZnIn 2 S 4 and carbon nanotubes The mass ratio is 1:20.

以同一时间取样的印染厂的印染废水为处理对象,在废水中分别加入不同浓度的实施例1~3所得的水处理剂,经过6小时日光照射后,水处理剂对印染废水的脱色率如下表所示: Taking the printing and dyeing wastewater of the printing and dyeing factory sampled at the same time as the treatment object, the water treatment agents obtained in Examples 1 to 3 of different concentrations were added to the wastewater, and after 6 hours of sunlight, the decolorization rate of the water treatment agent on the printing and dyeing wastewater was as follows As shown in the table:

脱色率 Decolorization rate COD去除率 COD removal rate 实施例1 Example 1 99.2% 99.2% 90.5% 90.5% 实施例2 Example 2 99.4% 99.4% 92.3% 92.3% 实施例3 Example 3 99.5% 99.5% 93.1% 93.1%

Claims (10)

1. a CNT is combined ZnIn2S4The preparation method of green deep water treatment agent, including:
(1) by CNT at H2SO4And HNO3Room temperature ultrasonic reaction 30~60min in mixed liquor, washing is to neutrality, room temperature Vacuum drying, obtains carboxylic carbon nano-tube;Then carboxylic carbon nano-tube is distributed in excess diethylenetriamine, adds 2-(7-azo BTA)-N, N, N', N'-tetramethylurea hexafluorophosphoric acid ester, 40~50 DEG C of reactions 5~6h, washing with alcohol, room Temperature vacuum drying, obtains aminated carbon nano tube;Then by aminated carbon nano tube ultrasonic disperse to water and the mixed liquor of acetone In, regulation pH value is 5~6, and ice-water bath dropping 2,4,6-tri-fluoro-5-chloropyrimide, regulation pH value is 6~6.5,20~30 DEG C Ultrasonic reaction 24~48h, washing with alcohol, washing, room temperature in vacuo drying, irradiation obtains response type CNT;
(2) by nanometer Zn In2S4, stabilizer, response type CNT in template and step (1) join phosphate-buffered In liquid, stir 30~60min, form suspension;Wherein, nanometer Zn In2S4With the mass ratio of response type CNT it is 1:5~1:20;Wherein, stabilizer is disodiumedetate, tetrasodium ethylenediamine tetraacetate, sodium gluconate, butane One in tetrabasic carboxylic acid;Template is triblock polyether P123 and the mixing of triblock copolymer F127 of mass ratio 1:3 Thing;
(3) regulating pH value with alkaline solution is 5~6, is heated to reflux and filters, obtaining CNT and be combined ZnIn2S4Green deep Degree water treatment agent.
A kind of CNT the most according to claim 1 is combined ZnIn2S4The preparation method of green deep water treatment agent, it is special Levy and be: the CNT in described step (1) and H2SO4And HNO3The ratio of mixed liquor is 10~20g:4L;Wherein, H2SO4And HNO3Volume ratio be 1:1~5:1.
A kind of CNT the most according to claim 1 is combined ZnIn2S4The preparation method of green deep water treatment agent, it is special Levy and be: the carboxylic carbon nano-tube in described step (1) and 2-(7-azo BTA)-N, N, N', N'-tetramethylurea The mass ratio of hexafluorophosphoric acid ester is 5~8:0.1~0.6.
A kind of CNT the most according to claim 1 is combined ZnIn2S4The preparation method of green deep water treatment agent, it is special Levy and be: the aminated carbon nano tube in described step (1) is 4~4.5g:1L with the ratio of water and the mixed liquor of acetone;Its In, the volume ratio of water and acetone is 3:1~5:1.
A kind of CNT the most according to claim 1 is combined ZnIn2S4The preparation method of green deep water treatment agent, it is special Levy and be: the aminated carbon nano tube in described step (1) is 4~4.5:4~6 with the mass ratio of 2,4,6-tri-fluoro-5-chloropyrimide.
A kind of CNT the most according to claim 1 is combined ZnIn2S4The preparation method of green deep water treatment agent, it is special Levy and be: described step (1) uses sodium carbonate liquor regulation pH value.
A kind of CNT the most according to claim 1 is combined ZnIn2S4The preparation method of green deep water treatment agent, it is special Levy and be: the stabilizer concentration in described step (2) is 0.01~0.1mol/L.
A kind of CNT the most according to claim 1 is combined ZnIn2S4The preparation method of green deep water treatment agent, it is special Levy and be: the template concentration in described step (2) is 0.01~0.1mol/L.
A kind of CNT the most according to claim 1 is combined ZnIn2S4The preparation method of green deep water treatment agent, it is special Levy and be: the phosphate buffer in described step (2) by concentration 0.025~0.05mol/L sodium dihydrogen phosphate and 0.05~0.1mol/L disodium hydrogen phosphate composition.
A kind of CNT the most according to claim 1 is combined ZnIn2S4The preparation method of green deep water treatment agent, it is special Levy and be: the alkaline solution in described step (3) is concentration 0.5mol/L~the sodium hydroxide of 1.5mol/L or potassium hydroxide Aqueous solution.
CN201410843621.6A 2014-12-25 2014-12-25 A kind of preparation method of carbon nanotube composite ZnIn2S4 green deep water treatment agent Expired - Fee Related CN104525222B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201410843621.6A CN104525222B (en) 2014-12-25 2014-12-25 A kind of preparation method of carbon nanotube composite ZnIn2S4 green deep water treatment agent

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201410843621.6A CN104525222B (en) 2014-12-25 2014-12-25 A kind of preparation method of carbon nanotube composite ZnIn2S4 green deep water treatment agent

Publications (2)

Publication Number Publication Date
CN104525222A CN104525222A (en) 2015-04-22
CN104525222B true CN104525222B (en) 2016-08-17

Family

ID=52840955

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201410843621.6A Expired - Fee Related CN104525222B (en) 2014-12-25 2014-12-25 A kind of preparation method of carbon nanotube composite ZnIn2S4 green deep water treatment agent

Country Status (1)

Country Link
CN (1) CN104525222B (en)

Families Citing this family (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN109395744B (en) * 2018-11-07 2021-05-25 江苏大学 A kind of preparation method of Ag2O quantum dot hybrid ZnIn2S4 nanosheet p-n type composite photocatalyst
CN110227552A (en) * 2019-07-10 2019-09-13 西北师范大学 A kind of preparation method of BCN@AZIS composite catalyst
CN116851007B (en) * 2023-07-11 2024-09-17 山东交通学院 Preparation method and magnetic field assisted photocatalysis application of carbon nanotube-indium zinc sulfide nanosheet composite material

Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104086094A (en) * 2014-07-16 2014-10-08 哈尔滨工业大学 Carbon-nanotube-containing glass fiber wetting agent, and preparation method and application thereof
CN104085879A (en) * 2014-07-16 2014-10-08 哈尔滨工业大学 Preparation method of high-concentration carbon nanotube dispersion liquid

Family Cites Families (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US6821730B2 (en) * 2001-11-09 2004-11-23 Intel Corporation Carbon nanotube molecular labels

Patent Citations (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN104086094A (en) * 2014-07-16 2014-10-08 哈尔滨工业大学 Carbon-nanotube-containing glass fiber wetting agent, and preparation method and application thereof
CN104085879A (en) * 2014-07-16 2014-10-08 哈尔滨工业大学 Preparation method of high-concentration carbon nanotube dispersion liquid

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
"Preparation of a MWCNTs/ZnIn2S4 composite and its enhanced photocatalytic hydrogen production under visible-light irradiation";Bo Chai,et al;《Dalton Transactions》;20111125;第41卷;全文 *

Also Published As

Publication number Publication date
CN104525222A (en) 2015-04-22

Similar Documents

Publication Publication Date Title
CN104525173B (en) A kind of preparation method of carbon nanotube composite TiO2 green deep water treatment agent
CN104437466B (en) A kind of CNT is combined the preparation method of pucherite green deep water treatment agent
CN104525227B (en) Preparation method for environment-friendly advanced water treatment agent by combining carbon nano tube and Ag/BiOX
CN103801284A (en) Method for preparing pucherite-graphene composite photocatalyst
CN107999023A (en) Carry the preparation method of cobalt ordered mesoporous carbon material and its application in Oxone rhodamine B degradation waste water is catalyzed
CN104475100B (en) A preparation method of carbon nanotube composite bismuth molybdate green deep water treatment agent
CN104525222B (en) A kind of preparation method of carbon nanotube composite ZnIn2S4 green deep water treatment agent
CN104528865B (en) A kind of preparation method of carbon nanotube composite SrFeO3 green deep water treatment agent
CN104437639B (en) A kind of CNT is combined the preparation method of tetrasulfonic acid iron-phthalocyanine green deep water treatment agent
CN102228829A (en) Method for preparing bentonite self-assembled green bismuth vanadate advanced water treatment agent
CN104528866B (en) A kind of preparation method of carbon nanotube compound bismuth tungstate green deep water conditioner
CN106423301A (en) Fiber/carbon nanotube/Bi2MoO6 three-dimensional recyclable efficient catalytic material as well as preparation method and application of catalytic material
CN104525115B (en) A preparation method of carbon nanotube composite WO3 green deep water treatment agent
CN106732795A (en) A kind of fiber/CNT/BiFeO3Three-dimensional recyclable efficient catalytic material and its preparation and application
CN102489291B (en) Method for preparing expanded graphite load nanometer bismuth vanadate photochemical catalyst
CN104528867B (en) A kind of preparation method of carbon nanotube compound ferric vandate green deep water conditioner
CN106732790A (en) A kind of fiber/CNT/Ag3PO4 three-dimensional recyclable efficient catalytic material and its preparation and application
CN106283616A (en) A kind of preparation method of fabric anion finishing liquor
CN110526484A (en) A kind of organophosphorus pesticide technique for treating industrial wastewater
CN110115993A (en) A kind of method of high-level oxidation technology processing adsorption saturation powdered activated carbon
CN102442710A (en) Preparation method of attapulgite self-assembled bismuth vanadate green advanced water treatment agent
CN111957320B (en) Supported catalyst filter fiber for catalytic degradation of pollutants in water, and preparation and application thereof
CN102247831A (en) Method for preparing activated carbon self-assembled bismuth vanadate water treatment agent
CN106732805A (en) A kind of fiber/CNT/BiVO4 three-dimensional recyclable efficient catalytic material and its preparation and application
CN106423302A (en) A fiber/carbon nanotube/BiPO4 three-dimensional recyclable high-efficiency catalytic material and its preparation and application

Legal Events

Date Code Title Description
PB01 Publication
C10 Entry into substantive examination
SE01 Entry into force of request for substantive examination
C14 Grant of patent or utility model
GR01 Patent grant
CF01 Termination of patent right due to non-payment of annual fee
CF01 Termination of patent right due to non-payment of annual fee

Granted publication date: 20160817

Termination date: 20181225