CN113603181B - Method for degrading oxytetracycline by double-chamber photoelectrocatalysis - Google Patents
Method for degrading oxytetracycline by double-chamber photoelectrocatalysis Download PDFInfo
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Abstract
Description
技术领域technical field
本发明涉及污染物光电催化领域,具体为一种双室光电催化降解土霉素的方法。The invention relates to the field of photoelectric catalysis of pollutants, in particular to a method for degrading oxytetracycline by photoelectric catalysis with two chambers.
背景技术Background technique
近年来,基于半导体的光催化技术因其在降解有机污染物方面的优异特性而受到广泛关注。In recent years, semiconductor-based photocatalysis has attracted extensive attention due to its excellent properties in degrading organic pollutants.
与单一光催化工艺相比,双室光电催化工艺在光阳极室具有更低的能耗和更高的降解效率。同时,在阴极室也可以实现污染物的去除。光电催化过程中施加偏压可以防止光生电子-空穴对的复合,显着提高光催化效率。双室光电催化反应系统实现了土霉素的同时降解、氢气的产生和二氧化碳的还原。Compared with the single photocatalytic process, the dual-chamber photocatalytic process has lower energy consumption and higher degradation efficiency in the photoanode chamber. At the same time, the removal of pollutants can also be achieved in the cathode chamber. Applying a bias voltage during the photocatalytic process can prevent the recombination of photogenerated electron-hole pairs and significantly improve the photocatalytic efficiency. The dual-chamber photocatalytic reaction system realizes simultaneous degradation of oxytetracycline, generation of hydrogen and reduction of carbon dioxide.
土霉素的降解工艺主要有生物处理法、氯化法和高级氧化技术,其中高级氧化技术效率较高,主要分为臭氧法、芬顿法、光解法、半导体处理、光电处理方法等。本发明设计的双室光电催化处理属于高级氧化法,与现有工艺相比降解效率高,可实现土霉素在光环境和暗环境下的同步降解。The degradation processes of oxytetracycline mainly include biological treatment, chlorination and advanced oxidation technology, among which advanced oxidation technology is more efficient, mainly divided into ozone method, Fenton method, photolysis method, semiconductor treatment, photoelectric treatment method, etc. The double-chamber photocatalytic treatment designed by the present invention belongs to the advanced oxidation method, and compared with the existing process, the degradation efficiency is high, and the synchronous degradation of the oxytetracycline in the light environment and the dark environment can be realized.
在双室光电催化系统中,土霉素的降解机制的研究尚未发现。双室光电催化系统的光阳极室和阴极室中电子的得失是不同的,因此土霉素在有光照的阳极室和暗环境的阴极室中的降解机理和作用机制可能不同。所以,模拟太阳光下双室光电催化系统降解土霉素的方法具有重要意义。In the dual-chamber photocatalytic system, the degradation mechanism of oxytetracycline has not yet been discovered. The gain and loss of electrons in the photoanode and cathode chambers of the dual-chamber photocatalytic system are different, so the degradation mechanism and action mechanism of oxytetracycline in the illuminated anode chamber and the dark cathode chamber may be different. Therefore, it is of great significance to simulate the method of degrading oxytetracycline by a dual-chamber photocatalytic system under sunlight.
发明内容Contents of the invention
针对现有技术的不足,本发明提供一种双室光电催化降解土霉素的方法,构建了双室光电催化体系,将石墨相氮化碳在二氧化钛纳米管阵列光电极运用于双室光电催化体系,实现土霉素在阴极和阳极上的同步降解,该催化体系廉价,稳定性好,光电转换效率高,光催化活性高,绿色无污染,具有可见光光催化活性。Aiming at the deficiencies of the prior art, the present invention provides a dual-chamber photocatalytic degradation method for oxytetracycline, constructs a dual-chamber photocatalytic system, and uses graphite-phase carbon nitride on a titanium dioxide nanotube array photoelectrode for dual-chamber photocatalytic system to realize simultaneous degradation of oxytetracycline on the cathode and anode, the catalytic system is cheap, good stability, high photoelectric conversion efficiency, high photocatalytic activity, green and pollution-free, and has visible light photocatalytic activity.
为实现上述目的,本发明提供如下技术方案:一种双室光电催化降解土霉素的方法,包括如下具体步骤:In order to achieve the above object, the present invention provides the following technical scheme: a kind of double-chamber photocatalytic degradation method for oxytetracycline, comprising the following specific steps:
S1:构建双室光电催化体系S1: Construction of a dual-chamber photocatalytic system
将两个底部带有连通管的石英反应器连接,中间加阳离子交换膜,将自制石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极分别用作光电催化体系的阳极和阴极,阳极和阴极接通电源,阳极用氙灯照射;Connect two quartz reactors with connecting tubes at the bottom, add a cation exchange membrane in the middle, and use the self-made graphite-phase carbon nitride-doped titanium dioxide nanotube array photoelectrode as the anode and cathode of the photoelectrocatalytic system, and the anode and cathode Turn on the power supply and irradiate the anode with a xenon lamp;
S2:光电催化体系降解土霉素S2: Degradation of Oxytetracycline by Photocatalytic System
向双室光电催化体系的反应器内加入一定浓度的土霉素溶液,打开氙灯,调整外接偏压,对土霉素进行降解;Add a certain concentration of oxytetracycline solution into the reactor of the double-chamber photocatalytic system, turn on the xenon lamp, adjust the external bias voltage, and degrade oxytetracycline;
所述石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极采用一步法制备,具体方法如下:在石墨相氮化碳、无水硫酸钠及氟化钠混合体系溶液中,用预处理后的钛片作阳极,铂片做为阴极,一定电压条件下阳极氧化后,将氧化后的钛片阳极置于马弗炉中高温退火,从而得到自制的石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极。The titanium dioxide nanotube array photoelectrode doped with graphite phase carbon nitride is prepared by a one-step method, and the specific method is as follows: in the mixed system solution of graphite phase carbon nitride, anhydrous sodium sulfate and sodium fluoride, pretreated The titanium sheet is used as the anode, and the platinum sheet is used as the cathode. After anodic oxidation under a certain voltage condition, the oxidized titanium sheet anode is placed in a muffle furnace for high-temperature annealing, thereby obtaining self-made graphite-phase carbon nitride-doped titanium dioxide nanotubes. Array photoelectrodes.
优选的,步骤S1中阳极与阴极接通的电源为直流稳压电源,氙灯距离阳极反应器的距离为1-3cm,氙灯的功率为100-150W。Preferably, the power supply connected between the anode and the cathode in step S1 is a DC stabilized power supply, the distance between the xenon lamp and the anode reactor is 1-3 cm, and the power of the xenon lamp is 100-150W.
优选的,步骤S2中反应器中土霉素的浓度为10-50mg/L,氙灯与外加偏压同时打开,外加偏压的范围是0.5-1.5V,反应温度为15-30℃。Preferably, in step S2, the concentration of oxytetracycline in the reactor is 10-50 mg/L, the xenon lamp is turned on simultaneously with the applied bias voltage, the range of the applied bias voltage is 0.5-1.5V, and the reaction temperature is 15-30°C.
优选的,钛片中钛含量>99.9%,所述钛片的预处理方法如下:用氢氟酸洗去表面氧化层,用清水冲洗后用砂纸打磨,打磨完的钛片用清洗剂清洗。Preferably, the titanium content in the titanium sheet is >99.9%, and the pretreatment method of the titanium sheet is as follows: wash off the surface oxide layer with hydrofluoric acid, polish with sandpaper after rinsing with water, and clean the polished titanium sheet with a cleaning agent.
优选的,所述清洗剂为乙醇、丙酮、去离子水的一种或二种以上。Preferably, the cleaning agent is one or more of ethanol, acetone and deionized water.
优选的,所述石墨相氮化碳的制备方法如下:将三聚氰胺在400℃-550℃高温煅烧,煅烧后自然冷去至室温,研磨粉碎得到石墨相氮化碳。Preferably, the preparation method of the graphite phase carbon nitride is as follows: melamine is calcined at a high temperature of 400° C. to 550° C., cooled naturally to room temperature after calcination, and ground and pulverized to obtain the graphite phase carbon nitride.
优选的,步骤S2中的石墨相氮化碳的前体物包括三聚氰胺、尿素的一种或二种。Preferably, the precursor of the graphitic carbon nitride in step S2 includes one or both of melamine and urea.
优选的,所述钛片阳极氧化电压为15-30V,马弗炉退火温度为450-600℃,退火时间为1-6h。Preferably, the anodic oxidation voltage of the titanium sheet is 15-30V, the muffle furnace annealing temperature is 450-600°C, and the annealing time is 1-6h.
优选的,所述混合溶液体系由浓度为0.2-1g/L的石墨相氮化碳、浓度为0.5-1mol/L的无水硫酸钠及浓度为0.2-0.6wt%的氟化钠溶液配制而成,溶液现配现用。Preferably, the mixed solution system is prepared from graphite phase carbon nitride with a concentration of 0.2-1g/L, anhydrous sodium sulfate with a concentration of 0.5-1mol/L and sodium fluoride solution with a concentration of 0.2-0.6wt%. Complete, the solution is ready-to-use.
本发明的有益效果:Beneficial effects of the present invention:
1.本发明构建了有效的双室光电催化体系用于降解土霉素,实现土霉素在阴极和阳极上的同步降解,制备出电极稳定性好,光电转换效率高,光催化活性高,绿色无污染,具有可见光光催化活性的二氧化钛纳米管阵列光电极,将其应用于双室光电催化体系中实现土霉素的高效降解。1. The present invention constructs an effective dual-chamber photocatalytic system for degrading oxytetracycline, realizes simultaneous degradation of oxytetracycline on the cathode and anode, and prepares electrodes with good stability, high photoelectric conversion efficiency, and high photocatalytic activity. Green and non-polluting, titanium dioxide nanotube array photoelectrode with visible light photocatalytic activity is applied in a dual-chamber photocatalytic system to achieve efficient degradation of oxytetracycline.
2.双室光电催化体系降解土霉素,相对于传统单室光催化工艺,双室光电催化体系可以同时实现光环境和暗环境下土霉素的降解。双室光电催化体系在同样的能耗下,阴极的降解效率提高了60%,利用光催化与电催化的共同作用,产生超氧自由基和羟基自由基,完成土霉素的降解。2. The dual-chamber photocatalytic system degrades oxytetracycline. Compared with the traditional single-chamber photocatalytic process, the dual-chamber photocatalytic system can simultaneously realize the degradation of oxytetracycline in light environment and dark environment. Under the same energy consumption, the dual-chamber photocatalytic system can increase the degradation efficiency of the cathode by 60%. Using the joint action of photocatalysis and electrocatalysis, superoxide radicals and hydroxyl radicals are generated to complete the degradation of oxytetracycline.
3.本发明基于阳极氧化同步沉积工艺,通过一步法将石墨相氮化碳在二氧化钛纳米管阵列光电极生成的同时掺杂在其上,石墨氮化碳的导带为-1.1eV,二氧化钛的导带为-0.29eV。在两者复合时,石墨氮化碳导带中产生的激发电子可以转移到二氧化钛导带上,从而促进光生载流子与空穴的分离,产生更多的电子空穴来降解污染物;相对于传统的工艺,即石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极的合成分为二氧化钛纳米管阵列光电极合成与石墨相氮化碳掺杂两个过程,缩短了制备工艺,解决制备成本高的问题,节省制备工艺步骤,也提高了光催化性能。3. The present invention is based on an anodic oxidation synchronous deposition process, and graphite phase carbon nitride is doped on the titanium dioxide nanotube array photoelectrode by a one-step method. The conduction band of graphite carbon nitride is -1.1eV, and that of titanium dioxide The conduction band is -0.29eV. When the two are recombined, the excited electrons generated in the conduction band of graphite carbon nitride can be transferred to the conduction band of titanium dioxide, thereby promoting the separation of photogenerated carriers and holes, and generating more electron holes to degrade pollutants; relatively Compared with the traditional process, the synthesis of titanium dioxide nanotube array photoelectrode doped with graphite phase carbon nitride is divided into two processes: synthesis of titanium dioxide nanotube array photoelectrode and graphite phase carbon nitride doping, which shortens the preparation process and solves the problem of preparation The problem of high cost saves the preparation process steps and improves the photocatalytic performance.
4.石墨氮化碳,即g-C3N4的半导体带隙较窄,能够吸收可见光,而且TiO2和g-C3N4二者能级的位置相匹配,光照时两者能够形成异质结,同时也使光生载流子得到有效分离,是拓宽后者光吸收范围和促进电荷分离的有效方法,本发明通过一步法制备完成,制备条件温和,简便可靠,大大提高了二氧化钛纳米管阵列光电极的量子效率以及光电转换能力,并且具备可见光光催化活性,能够利用太阳光中的大部分可见光能。4. Graphite carbon nitride, that is, gC 3 N 4 has a narrow semiconductor band gap and can absorb visible light, and the positions of the energy levels of TiO 2 and gC 3 N 4 match, and the two can form a heterojunction when illuminated. At the same time, the photogenerated carriers are effectively separated, which is an effective method to broaden the light absorption range of the latter and promote charge separation. The present invention is prepared by a one-step method, and the preparation conditions are mild, simple and reliable, and greatly improves the efficiency of the titanium dioxide nanotube array photoelectrode. It has excellent quantum efficiency and photoelectric conversion ability, and has visible light photocatalytic activity, which can utilize most of the visible light energy in sunlight.
5.相比于传统方法制备的石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极,本发明制备的光电极性质更稳定,可循环性能良好。在五次循环后仍然能保持较高的降解效率。二氧化钛和氮化碳之间具有协同作用,二氧化钛可被紫外波段的光激发、氮化碳可被可见波段的光激发,二者协同作用,对光照的利用率大大提升。5. Compared with the graphite-phase carbon nitride-doped titania nanotube array photoelectrode prepared by the traditional method, the photoelectrode prepared by the present invention has more stable properties and good cycle performance. High degradation efficiency can still be maintained after five cycles. There is a synergistic effect between titanium dioxide and carbon nitride. Titanium dioxide can be excited by light in the ultraviolet band, and carbon nitride can be excited by light in the visible band. The synergistic effect of the two greatly improves the utilization rate of light.
附图说明Description of drawings
图1是本发明与单独光催化、单独电催化、不加偏压的三个对照组的阳极的降解效果比较;Fig. 1 is the degradation effect comparison of the anode of the present invention and three control groups of independent photocatalysis, independent electrocatalysis, no bias;
图2是本发明与单独光催化、单独电催化、不加偏压的三个对照组的阴极的降解效果比较;Fig. 2 is the degradation effect comparison of the cathode of the present invention and three control groups of independent photocatalysis, independent electrocatalysis, no bias;
图3是本发明在不同电压下,阳极和阴极对土霉素的降解效果;Fig. 3 is that the present invention is under different voltages, the degradation effect of anode and cathode to oxytetracycline;
图4是本发明在不同pH下,阳极和阴极对土霉素的降解效果;Fig. 4 is the degradation effect of anode and cathode to oxytetracycline of the present invention under different pH;
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, not all, embodiments of the present invention. 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1Example 1
一步法制备石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极One-step preparation of graphitic carbon nitride-doped titanium dioxide nanotube array photoelectrodes
(1)将钛片用氢氟酸洗去表面氧化层,用清水冲洗后用砂纸打磨,打磨完的钛片用乙醇、丙酮、去离子水清洗;(1) Wash the titanium sheet with hydrofluoric acid to remove the surface oxide layer, polish it with sandpaper after rinsing with clear water, and clean the polished titanium sheet with ethanol, acetone, and deionized water;
(2)制备石墨相氮化碳(2) Preparation of graphite phase carbon nitride
将三聚氰胺400℃-550℃煅烧,冷却至室温后,研磨粉碎得到石墨相氮化碳;Calcining melamine at 400°C-550°C, cooling to room temperature, grinding and pulverizing to obtain graphite phase carbon nitride;
(3)配制石墨相氮化碳浓度为0.2-1g/L、无水硫酸钠浓度为0.5-1mol/L、氟化钠浓度为0.2-0.6wt%的混合溶液体系,用步骤(1)处理后的钛片做阳极,铂片做为阴极,在15-30V的电压条件下阳极氧化2-4h,再置于马弗炉中450-600℃退火1-6h,从而得到石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极。(3) preparing graphite phase carbon nitride concentration is 0.2-1g/L, anhydrous sodium sulfate concentration is 0.5-1mol/L, sodium fluoride concentration is the mixed solution system of 0.2-0.6wt%, processes with step (1) The final titanium sheet is used as the anode, and the platinum sheet is used as the cathode. It is anodized at a voltage of 15-30V for 2-4h, and then placed in a muffle furnace for annealing at 450-600°C for 1-6h to obtain graphite phase carbon nitride. Doped titania nanotube array photoelectrode.
利用双室光电催化降解土霉素:Photocatalytic degradation of oxytetracycline using dual chambers:
S1:构建双室光电催化体系S1: Construction of a dual-chamber photocatalytic system
将两个直径为3cm、高度为10cm底部带有连通管的石英反应器连接,中间加阳离子交换膜,将制备好的石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极分别用作光电催化体系的阳极和阴极,阳极和阴极接通电源,阳极用100-150W氙灯照射,氙灯距离阳极反应器的距离为1-3cm。Connect two quartz reactors with a diameter of 3 cm and a height of 10 cm with connecting tubes at the bottom, add a cation exchange membrane in the middle, and use the prepared graphite-phase carbon nitride-doped titanium dioxide nanotube array photoelectrodes as photoelectrocatalysts. The anode and cathode of the system, the anode and the cathode are powered on, the anode is irradiated with a 100-150W xenon lamp, and the distance between the xenon lamp and the anode reactor is 1-3cm.
S2:氙灯下光电催化体系降解土霉素S2: Degradation of Oxytetracycline by Photocatalytic System under Xenon Lamp
双室光电催化体系的反应器内加入浓度为10-50mg/L的土霉素溶液,打开氙灯,调整外接偏压为0.5-1.5V,反应温度为15-30℃下对土霉素进行降解,用紫外可见分光光度计在356nm波长下的吸光度计算土霉素的浓度和降解效率。Add oxytetracycline solution with a concentration of 10-50mg/L into the reactor of the dual-chamber photocatalytic system, turn on the xenon lamp, adjust the external bias voltage to 0.5-1.5V, and degrade oxytetracycline at a reaction temperature of 15-30°C , Calculate the concentration and degradation efficiency of oxytetracycline by absorbance at 356nm wavelength with a UV-Vis spectrophotometer.
实例2Example 2
一步法制备石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极One-step preparation of graphitic carbon nitride-doped titanium dioxide nanotube array photoelectrodes
(1)将钛片用氢氟酸洗去表面氧化层,用清水冲洗后用砂纸打磨,打磨完的钛片用乙醇、丙酮、去离子水清洗;(1) Wash the titanium sheet with hydrofluoric acid to remove the surface oxide layer, polish it with sandpaper after rinsing with clear water, and clean the polished titanium sheet with ethanol, acetone, and deionized water;
(2)制备石墨相氮化碳(2) Preparation of graphite phase carbon nitride
将三聚氰胺550℃煅烧,冷却至室温后,研磨粉碎得到石墨相氮化碳;Calcining melamine at 550°C, cooling to room temperature, grinding and pulverizing to obtain graphite phase carbon nitride;
(4)配制石墨相氮化碳浓度为1g/L、无水硫酸钠浓度为0.5mol/L、氟化钠浓度为0.2wt%的混合溶液体系,用步骤(1)处理后的钛片做阳极,铂片做为阴极,在15V的电压条件下阳极氧化2h,再置于马弗炉中450℃退火1-6h,从而得到石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极。(4) preparation graphite phase carbon nitride concentration is that 1g/L, anhydrous sodium sulfate concentration are 0.5mol/L, sodium fluoride concentration are the mixed solution system of 0.2wt%, make with the titanium plate after step (1) process The anode and the platinum sheet are used as the cathode, anodized at 15V for 2h, and then annealed at 450°C for 1-6h in a muffle furnace to obtain a titanium dioxide nanotube array photoelectrode doped with carbon nitride in the graphite phase.
利用双室光电催化降解土霉素Photocatalytic Degradation of Oxytetracycline Using Dual Chambers
S1:构建双室光电催化体系S1: Construction of a dual-chamber photocatalytic system
将两个直径为3cm、高度为10cm底部带有连通管的石英反应器连接,中间加阳离子交换膜,将制备好的石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极分别用作光电催化体系的阳极和阴极,阳极和阴极接通电源,阳极用150W氙灯照射,氙灯距离阳极反应器的距离为3cm。Connect two quartz reactors with a diameter of 3 cm and a height of 10 cm with connecting tubes at the bottom, add a cation exchange membrane in the middle, and use the prepared graphite-phase carbon nitride-doped titanium dioxide nanotube array photoelectrodes as photoelectrocatalysts. The anode and cathode of the system, the anode and the cathode are powered on, the anode is irradiated with a 150W xenon lamp, and the distance between the xenon lamp and the anode reactor is 3cm.
S2:氙灯下光电催化体系降解土霉素S2: Degradation of Oxytetracycline by Photocatalytic System under Xenon Lamp
双室光电催化体系的反应器内加入浓度为10mg/L的土霉素溶液,打开氙灯,调整外接偏压为1.5V,反应温度为30℃下对土霉素进行降解,用紫外可见分光光度计在356nm波长下的吸光度计算土霉素的浓度和降解效率。Add oxytetracycline solution with a concentration of 10mg/L into the reactor of the double-chamber photocatalytic system, turn on the xenon lamp, adjust the external bias voltage to 1.5V, and degrade the oxytetracycline at a reaction temperature of 30°C, and use UV-visible spectrophotometry Calculate the concentration and degradation efficiency of oxytetracycline by calculating the absorbance at 356nm wavelength.
实例4Example 4
一步法制备石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极One-step preparation of graphitic carbon nitride-doped titanium dioxide nanotube array photoelectrodes
(1)将钛片用氢氟酸洗去表面氧化层,用清水冲洗后用砂纸打磨,打磨完的钛片用乙醇、丙酮、去离子水清洗;(1) Wash the titanium sheet with hydrofluoric acid to remove the surface oxide layer, polish it with sandpaper after rinsing with clear water, and clean the polished titanium sheet with ethanol, acetone, and deionized water;
(2)制备石墨相氮化碳(2) Preparation of graphite phase carbon nitride
将三聚氰胺400℃煅烧,冷却至室温后,研磨粉碎得到石墨相氮化碳;Calcining melamine at 400°C, cooling to room temperature, grinding and pulverizing to obtain graphite phase carbon nitride;
(5)配制石墨相氮化碳浓度为0.5g/L、无水硫酸钠浓度为1mol/L、氟化钠浓度为0.6wt%的混合溶液体系,用步骤(1)处理后的钛片做阳极,铂片做为阴极,在30V的电压条件下阳极氧化2h,再置于马弗炉中450℃退火5h,从而得到石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极。(5) preparation graphite phase carbon nitride concentration is 0.5g/L, anhydrous sodium sulfate concentration is 1mol/L, sodium fluoride concentration is the mixed solution system of 0.6wt%, makes with the titanium sheet after step (1) process The anode and the platinum sheet were used as the cathode, anodized at 30V for 2h, and then annealed at 450°C for 5h in a muffle furnace to obtain a titanium dioxide nanotube array photoelectrode doped with carbon nitride in the graphite phase.
利用双室光电催化降解土霉素Photocatalytic Degradation of Oxytetracycline Using Dual Chambers
S1:构建双室光电催化体系S1: Construction of a dual-chamber photocatalytic system
将两个直径为3cm、高度为10cm底部带有连通管的石英反应器连接,中间加阳离子交换膜,将制备好的石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极分别用作光电催化体系的阳极和阴极,阳极和阴极接通电源,阳极用100W氙灯照射,氙灯距离阳极反应器的距离为2cm。Connect two quartz reactors with a diameter of 3 cm and a height of 10 cm with connecting tubes at the bottom, add a cation exchange membrane in the middle, and use the prepared graphite-phase carbon nitride-doped titanium dioxide nanotube array photoelectrodes as photoelectrocatalysts. The anode and cathode of the system, the anode and the cathode are powered on, the anode is irradiated with a 100W xenon lamp, and the distance between the xenon lamp and the anode reactor is 2cm.
S2:氙灯下光电催化体系降解土霉素S2: Degradation of Oxytetracycline by Photocatalytic System under Xenon Lamp
双室光电催化体系的反应器内加入浓度为10mg/L的土霉素溶液,打开氙灯,调整外接偏压为1V,反应温度为25℃下对土霉素进行降解,用紫外可见分光光度计在356nm波长下的吸光度计算土霉素的浓度和降解效率。Add oxytetracycline solution with a concentration of 10mg/L into the reactor of the double-chamber photocatalytic system, turn on the xenon lamp, adjust the external bias voltage to 1V, and degrade the oxytetracycline at a reaction temperature of 25°C, and use a UV-visible spectrophotometer The absorbance at 356nm wavelength was used to calculate the concentration and degradation efficiency of oxytetracycline.
对比例1Comparative example 1
单独光催化下的石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极对土霉素的降解:Degradation of oxytetracycline by graphitic carbon nitride-doped titania nanotube array photoelectrode under photocatalysis alone:
(1)将钛片用氢氟酸洗去表面氧化层,用清水冲洗后用砂纸打磨,打磨完的钛片用乙醇、丙酮、去离子水清洗;(1) Wash the titanium sheet with hydrofluoric acid to remove the surface oxide layer, polish it with sandpaper after rinsing with clear water, and clean the polished titanium sheet with ethanol, acetone, and deionized water;
(2)制备石墨相氮化碳(2) Preparation of graphite phase carbon nitride
将三聚氰胺400℃煅烧,冷却至室温后,研磨粉碎得到石墨相氮化碳;Calcining melamine at 400°C, cooling to room temperature, grinding and pulverizing to obtain graphite phase carbon nitride;
(6)配制石墨相氮化碳浓度为0.5g/L、无水硫酸钠浓度为1mol/L、氟化钠浓度为0.6wt%的混合溶液体系,用步骤(1)处理后的钛片做阳极,铂片做为阴极,在30V的电压条件下阳极氧化2h,再置于马弗炉中450℃退火5h,从而得到石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极。(6) preparation graphite phase carbon nitride concentration is 0.5g/L, anhydrous sodium sulfate concentration is 1mol/L, sodium fluoride concentration is the mixed solution system of 0.6wt%, makes with the titanium plate after step (1) process The anode and the platinum sheet were used as the cathode, anodized at 30V for 2h, and then annealed at 450°C for 5h in a muffle furnace to obtain a titanium dioxide nanotube array photoelectrode doped with carbon nitride in the graphite phase.
利用双室光催化降解土霉素Photocatalytic Degradation of Oxytetracycline Using Dual Chambers
S1:构建双室光催化体系S1: Construction of a dual-chamber photocatalytic system
将两个直径为3cm、高度为10cm底部带有连通管的石英反应器连接,中间加阳离子交换膜,将制备好的石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极分别用作光电催化体系的阳极和阴极,阳极用100W氙灯照射,氙灯距离阳极反应器的距离为2cm。Connect two quartz reactors with a diameter of 3 cm and a height of 10 cm with connecting tubes at the bottom, add a cation exchange membrane in the middle, and use the prepared graphite-phase carbon nitride-doped titanium dioxide nanotube array photoelectrodes as photoelectrocatalysts. The anode and cathode of the system, the anode is irradiated with a 100W xenon lamp, and the distance between the xenon lamp and the anode reactor is 2cm.
S2:氙灯下光催化体系降解土霉素S2: Degradation of oxytetracycline by photocatalytic system under xenon lamp
双室光催化体系的反应器内加入浓度为10mg/L的土霉素溶液,打开氙灯,反应温度为25℃下对土霉素进行降解,用紫外可见分光光度计在356nm波长下的吸光度计算土霉素的浓度和降解效率。Add oxytetracycline solution with a concentration of 10mg/L into the reactor of the dual-chamber photocatalytic system, turn on the xenon lamp, and degrade oxytetracycline at a reaction temperature of 25°C, and calculate the absorbance at 356nm wavelength with a UV-visible spectrophotometer Oxytetracycline concentration and degradation efficiency.
对比例2Comparative example 2
单独电催化下的石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极对土霉素的降解Degradation of oxytetracycline by graphitic carbon nitride-doped titania nanotube array photoelectrode under separate electrocatalysis
(1)将钛片用氢氟酸洗去表面氧化层,用清水冲洗后用砂纸打磨,打磨完的钛片用乙醇、丙酮、去离子水清洗;(1) Wash the titanium sheet with hydrofluoric acid to remove the surface oxide layer, polish it with sandpaper after rinsing with clear water, and clean the polished titanium sheet with ethanol, acetone, and deionized water;
(2)制备石墨相氮化碳(2) Preparation of graphite phase carbon nitride
将三聚氰胺400℃煅烧,冷却至室温后,研磨粉碎得到石墨相氮化碳;Calcining melamine at 400°C, cooling to room temperature, grinding and pulverizing to obtain graphite phase carbon nitride;
(7)配制石墨相氮化碳浓度为0.2g/L、无水硫酸钠浓度为1mol/L、氟化钠浓度为0.6wt%的混合溶液体系,用步骤(1)处理后的钛片做阳极,铂片做为阴极,在30V的电压条件下阳极氧化2h,再置于马弗炉中500℃退火6h,从而得到石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极。(7) preparation graphite phase carbon nitride concentration is 0.2g/L, anhydrous sodium sulfate concentration is 1mol/L, sodium fluoride concentration is the mixed solution system of 0.6wt%, makes with the titanium plate after step (1) process The anode and the platinum sheet were used as the cathode, anodized at 30V for 2h, and then annealed at 500°C for 6h in a muffle furnace to obtain a titanium dioxide nanotube array photoelectrode doped with carbon nitride in the graphite phase.
利用双室电催化降解土霉素Degradation of oxytetracycline by double-chamber electrocatalysis
S1:构建双室电催化体系S1: Construction of a dual-chamber electrocatalytic system
将两个直径为3cm、高度为10cm底部带有连通管的石英反应器连接,中间加阳离子交换膜,将制备好的石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极分别用作电催化体系的阳极和阴极,阳极和阴极接通电源。Connect two quartz reactors with a diameter of 3 cm and a height of 10 cm with connecting pipes at the bottom, add a cation exchange membrane in the middle, and use the prepared graphite-phase carbon nitride-doped titanium dioxide nanotube array photoelectrodes as electrocatalysts. The anode and cathode of the system are connected to the power supply.
S2:氙灯下电催化体系降解土霉素S2: Degradation of oxytetracycline by electrocatalytic system under xenon lamp
双室光电催化体系的反应器内加入浓度为10mg/L的土霉素溶液,调整外接偏压为1V,反应温度为25℃下对土霉素进行降解,用紫外可见分光光度计在356nm波长下的吸光度计算土霉素的浓度和降解效率。Add oxytetracycline solution with a concentration of 10mg/L into the reactor of the dual-chamber photocatalytic system, adjust the external bias voltage to 1V, and degrade oxytetracycline at a reaction temperature of 25°C. Calculate the concentration and degradation efficiency of oxytetracycline under the absorbance.
对比例2Comparative example 2
无外加偏压的光电催化下的石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极对土霉素的降解Degradation of oxytetracycline by graphitic carbon nitride-doped titania nanotube array photoelectrode under photoelectrocatalysis without external bias
一步法制备石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极One-step preparation of graphitic carbon nitride-doped titanium dioxide nanotube array photoelectrodes
(1)将钛片用氢氟酸洗去表面氧化层,用清水冲洗后用砂纸打磨,打磨完的钛片用乙醇、丙酮、去离子水清洗;(1) Wash the titanium sheet with hydrofluoric acid to remove the surface oxide layer, polish it with sandpaper after rinsing with clear water, and clean the polished titanium sheet with ethanol, acetone, and deionized water;
(2)制备石墨相氮化碳(2) Preparation of graphite phase carbon nitride
将三聚氰胺400℃煅烧,冷却至室温后,研磨粉碎得到石墨相氮化碳;Calcining melamine at 400°C, cooling to room temperature, grinding and pulverizing to obtain graphite phase carbon nitride;
(8)配制石墨相氮化碳浓度为0.2g/L、无水硫酸钠浓度为1mol/L、氟化钠浓度为0.6wt%的混合溶液体系,用步骤(1)处理后的钛片做阳极,铂片做为阴极,在30V的电压条件下阳极氧化2h,再置于马弗炉中500℃退火6h,从而得到石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极。(8) It is 0.2g/L that the concentration of graphite phase carbon nitride is prepared, the concentration of anhydrous sodium sulfate is 1mol/L, and the mixed solution system that sodium fluoride concentration is 0.6wt% is made with the titanium plate after step (1) processing The anode and the platinum sheet were used as the cathode, anodized at 30V for 2h, and then annealed at 500°C for 6h in a muffle furnace to obtain a titanium dioxide nanotube array photoelectrode doped with carbon nitride in the graphite phase.
利用双室光电催化降解土霉素Photocatalytic Degradation of Oxytetracycline Using Dual Chambers
S1:构建双室光电催化体系S1: Construction of a dual-chamber photocatalytic system
将两个直径为3cm、高度为10cm底部带有连通管的石英反应器连接,中间加阳离子交换膜,将制备好的石墨相氮化碳掺杂的二氧化钛纳米管阵列光电极分别用作光电催化体系的阳极和阴极,阳极和阴极用导线连接,阳极用150W氙灯照射,氙灯距离阳极反应器的距离为3cm。Connect two quartz reactors with a diameter of 3 cm and a height of 10 cm with connecting tubes at the bottom, add a cation exchange membrane in the middle, and use the prepared graphite-phase carbon nitride-doped titanium dioxide nanotube array photoelectrodes as photoelectrocatalysts. The anode and cathode of the system are connected by wires, the anode is irradiated with a 150W xenon lamp, and the distance between the xenon lamp and the anode reactor is 3cm.
S2:氙灯下光电催化体系降解土霉素S2: Degradation of Oxytetracycline by Photocatalytic System under Xenon Lamp
双室光电催化体系的反应器内加入浓度为10mg/L的土霉素溶液,打开氙灯,反应温度为25℃下对土霉素进行降解,用紫外可见分光光度计在356nm波长下的吸光度计算土霉素的浓度和降解效率。Add oxytetracycline solution with a concentration of 10mg/L into the reactor of the double-chamber photocatalytic system, turn on the xenon lamp, and degrade oxytetracycline at a reaction temperature of 25°C, and calculate the absorbance at 356nm wavelength with a UV-visible spectrophotometer Oxytetracycline concentration and degradation efficiency.
根据对比例1-对比例3与双室光电催化体系对土霉素的效果比较,从图1-图2(E代表单独电催化、P代表单独光催化、PW代表无外加偏压的电催化、PE代表本发明的双室光电催化)中可以看出,相比于对比例1,阴极的降解效果提高了40%;相比于对比例2,阳极的降解效果提升了80%,阴极的降解效果提升了60%;相比于对比例3,阴极的降解效果提升了40%。由降解效果可见,本发明降解效率最高,在60min内对阳极的降解效率高达80%,对阴极的降解效率为60%,实现了土霉素在光环境和暗环境的同步降解。光环境和暗环境下,由于光生电子和外加偏压的共同作用,光生空穴和电子的分离效率提高,产生了更多的羟基自由基和超氧自由基,实现了土霉素的高效降解。对比其他工艺,降解效果提升明显。According to Comparative Example 1-Comparative Example 3 and the comparison of the effect of the dual-chamber photocatalytic system on oxytetracycline, from Figure 1-Figure 2 (E stands for electrocatalysis alone, P stands for photocatalysis alone, PW stands for electrocatalysis without external bias voltage , PE represents the dual-chamber photocatalysis of the present invention) as can be seen, compared to Comparative Example 1, the degradation effect of the cathode has improved by 40%; compared to Comparative Example 2, the degradation effect of the anode has improved by 80%, and the degradation effect of the cathode The degradation effect was increased by 60%; compared with Comparative Example 3, the degradation effect of the cathode was increased by 40%. It can be seen from the degradation effect that the degradation efficiency of the present invention is the highest, the degradation efficiency of the anode is as high as 80%, and the degradation efficiency of the cathode is 60% within 60 minutes, realizing the simultaneous degradation of oxytetracycline in light environment and dark environment. Under light environment and dark environment, due to the joint action of photogenerated electrons and external bias voltage, the separation efficiency of photogenerated holes and electrons is improved, and more hydroxyl radicals and superoxide radicals are generated, realizing the efficient degradation of oxytetracycline . Compared with other processes, the degradation effect is significantly improved.
从图3-图4可以看出,不同PH,不同电压下双室光电催化体系对土霉素的降解效果差距较大,在碱性环境下更有利于土霉素的降解,其主要作用物种是羟基自由基和超氧自由基。外加偏压为正电压时对阴极的降解效果有很大的提升,是因为外加偏压为正值时,外加电源可以促进光生电子和空穴的分离、抑制电子空穴对的复合,从而提高降解效率。From Figure 3-Figure 4, it can be seen that the degradation effect of the dual-chamber photocatalytic system on oxytetracycline under different pH and different voltages is quite different, and the degradation of oxytetracycline is more conducive to the degradation of oxytetracycline in alkaline environment, and its main active species are hydroxyl radicals and superoxide radicals. When the applied bias voltage is a positive voltage, the degradation effect of the cathode is greatly improved, because when the applied bias voltage is positive, the external power supply can promote the separation of photogenerated electrons and holes, and inhibit the recombination of electron-hole pairs, thereby improving degradation efficiency.
综上,本发明构建了有效的双室光电催化体系用于降解土霉素,实现土霉素在阴极和阳极上的同步降解,制备出电极稳定性好,光电转换效率高,光催化活性高,绿色无污染,具有可见光光催化活性的二氧化钛纳米管阵列光电极,将其应用于双室光电催化体系中实现土霉素的高效降解In summary, the present invention constructs an effective dual-chamber photocatalytic system for degrading oxytetracycline, realizes simultaneous degradation of oxytetracycline on the cathode and anode, and prepares electrodes with good stability, high photoelectric conversion efficiency, and high photocatalytic activity , green and pollution-free, titanium dioxide nanotube array photoelectrode with visible light photocatalytic activity, which is applied in a dual-chamber photocatalytic system to achieve efficient degradation of oxytetracycline
最后应说明的是:以上所述仅为本发明的优选实施例而已,并不用于限制本发明,尽管参照前述实施例对本发明进行了详细的说明,对于本领域的技术人员来说,其依然可以对前述各实施例所记载的技术方案进行修改,或者对其中部分技术特征进行等同替换。凡在本发明的精神和原则之内,所作的任何修改、等同替换、改进等,均应包含在本发明的保护范围之内。Finally, it should be noted that: the above is only a preferred embodiment of the present invention, and is not intended to limit the present invention. Although the present invention has been described in detail with reference to the foregoing embodiments, for those skilled in the art, it still The technical solutions recorded in the foregoing embodiments may be modified, or some technical features thereof may be equivalently replaced. Any modifications, equivalent replacements, improvements, etc. made within the spirit and principles of the present invention shall be included within the protection scope of the present invention.
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