欢迎登录材料期刊网

材料期刊网

高级检索

以活性炭纤维毡为阳极,不锈钢片为阴极,在Na_2SO_4介质中用恒定的电流强度进行电解,一定时间后将活性炭纤维毡取出用蒸馏水冲洗干净,在110℃下干燥12h,在干燥器中冷却至室温后,进行称重和红外、比表面积及孔分布测试.同时,以石墨片为阳极进行对比实验.结果显示,在电化学氧化过程中,活性炭纤维阳极表面的含氧活性基团量增加;与石墨电极相比,活性炭纤维电极具有更好的抗氧化性能和更高的析氧电位.因此,在难降解有机物的电氧化处理过程中活性炭纤维毡比石墨片更适宜作阳极.

The electrochemical oxidation process was performed using an activated carbon fiber (ACF) felt as an anode under constant current in Na_2SO_4 solution.After electrolyzing different times,ACFs were taken out and washed with distilled water and dried for 12h in vacuum at 110℃.After cooling to room temperature in desiccator,ACFs were weighed and analyzed by means of FT-IR spectroscopy and nitrogen adsorption method.At the same time,the contrast experiment was carried out using a graphite flake as an anode.The results showed that the amount of oxygen-containing groups on the ACF surface is increased in the process of electrochemical oxidation and ACF anode has better oxidation resistance performance and higher oxygen evolution potential compared with graphite anode.So,ACF is more appropriate to be the anode than graphite flake in the electrochemical oxidation process of refractory organics.

参考文献

[1] 曾汉民;郭锡坤 .[J].中大科研情报,1981,1:1-18.
[2] 曾汉民;符若文 .[J].功能材料,1991,22(06):321-328.
[3] 曾汉民;陆耘 .[J].离子交换与吸附,1993,9(05):464-477.
[4] 王茂章;贺福.碳纤维的制备、性质及其应用[M].北京:科学出版社,1984
[5] 王茂章.碳纤维及其复合材料[M].北京:科学出版社,1997
[6] 贾金平;杨骥;廖军 .[J].上海环境科学,1997,16(04):19-22,25.
[7] 徐咏蓝,李春喜,吕荣湖,王子镐.活性炭纤维电极法降解水中有机物的研究[J].工业水处理,2002(08):7-9.
[8] 郑春燕,易芬云,陈水挟.活性炭纤维电极法处理含酚废水的研究[J].功能材料,2007(03):451-454.
[9] Fenyun Yi;Shuixia Chen .Electrochemical Treatment Of Alizarin Red S Dye Wastewater Using An Activated Carbon Fiber As Anode Material[J].Journal of porous materials,2008(5):565-569.
[10] Li Fan;Yanwei Zhou;Weishen Yang .Electrochemical degradation of aqueous solution of Amaranth azo dye on ACF under potentiostatic model[J].Dyes and Pigments,2008(2):440-446.
[11] 李乃稳,曾抗美,肖芳,张超.活性炭多维电极法去除水中腐殖酸的探讨[J].四川大学学报(工程科学版),2002(03):57-61.
上一张 下一张
上一张 下一张
计量
  • 下载量()
  • 访问量()
文章评分
  • 您的评分:
  • 1
    0%
  • 2
    0%
  • 3
    0%
  • 4
    0%
  • 5
    0%