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鸡内金活性炭对酸碱性染料的吸附 被引量:3

Adsorption of Acidic and Basic Dyes by Endothelium Corneum Gigeriae Galli Activated Carbon
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摘要 以鸡内金(ECGG)为原料,在氩气保护下,先在450℃下高温炭化,后添加KOH作为活化剂,分别选取800、900、1 000℃作为活化温度,制备出3种类型活性炭(ECGG-800、EGGG-900和EGGG-1000).对3种类型活性炭表征分析,并选取ECGG-900做酸性品红和亚甲基蓝的吸附饱和,进行2种最常用的吸附模型Freundlich和Langmuir的拟合.结果表明,用Freundlich吸附等温线模型能解释鸡内金活性炭对酸性染料的吸附;而对于碱性染料的吸附,则Langmuir吸附等温线模型更有说服力;且该活性炭对酸性品红、亚甲基蓝的吸附量分别可达1.682 g/g和2.045 g/g.随着吸附时间的延长,3种活性炭对染料的去除率也随即增大.鸡内金活性炭对处理酸性和碱性染料效果均佳,是一种具有发展潜力的吸附剂. Activated carbon was prepared from endothelium corneum gigeriae galli (ECGG) by preliminary carbonization at 450 and final KOH activation at high temperatures (ECGG-800 ℃, ECGG-900℃ and ECGG-1 000 ℃ ). The surface and structural properties were analyzed with SEM and BET. And then selected ECGG-900 to draw its adsorption isotherms for acidic and basic dyes, the adsorption isotherm data were fitted by the two most used models, the Freundlich and Langmuir models. Results show that adsorption isotherm to acid fuchsin is best fitted with Freundlich model, while to methylene blue is more accord with Langmuir model. The adsorption capacity of acid fuchsin and methylene blue reached 1. 682 g/g, 2. 045 g/g. As the adsorption time sessions, the removal rates of three kinds of activated carbon for dyes also immediately increased. The results indicated that the Endothelium corneum gigeriae galli activated carbon is effective for removing the acid fuchsin and methylene blue in the water solution and is a potent adsorbent.
出处 《华南师范大学学报(自然科学版)》 CAS 北大核心 2015年第3期51-56,共6页 Journal of South China Normal University(Natural Science Edition)
基金 国家自然科学基金项目(21203067)
关键词 鸡内金活性炭 酸性品红 亚甲基蓝 吸附平衡 endothelium corneum gigeriae galli acid fuchsin methylene blue adsorption equilibrium
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参考文献18

  • 1Zhang L, Zhou X,Guo X,et al. Investigation on thedegradation of acid fuchsin induced oxidation by Mg-Fe204 under microwave irradiation [ J ]. Journal of Mo-lecular Catalysis A: Chemical,2011,335( 1 ) :31 -37.
  • 2Arulkumar M, Sathishkumar P, Palvannan T. Optimiza-tion of Orange G dye adsorption by activated carbon ofThespesia populnea pods using response surface method-ology [ J ] . Journal of Hazardous Materials, 2011, 186(1) :827 -834.
  • 3Stadler L B, Su L,Moline C J, et al. Effect of redoxconditions on pharmaceutical loss during biologicalwastewater treatment using sequencing batch reactors[J]. Journal of Hazardous Materials, 2014, 282 ( 23 ):105-115.
  • 4方晓波,成文,黄华坚,方战强.吸附电解氧化去除水中邻苯二甲酸二丁酯[J].华南师范大学学报(自然科学版),2013,45(3):78-81. 被引量:1
  • 5Aber S, Sheydaei M. Removal of COD from industrial ef-fluent containing indigo dye using adsorption method byactivated carbon cloth : Optimization, kinetic and iso-therm studies [ J ]. Clean-Soil, Air,Water, 2012, 40(1):87 -94.
  • 6Li Y, Du Q, Liu T, et al. Comparative study of methyl-ene blue dye adsorption onto activated carbon, grapheneoxide,and carbon nanotubes[ J]. Chemical EngineeringResearch and Design,2013 , 91(2) :361 - 368.
  • 7Summers R S, Kim S M,Shimabuku K, et al. Granularactivated carbon adsorption of MIB in the presence of dis-solved organic matter [ J ]. Water Research, 2013 , 47(10):3507 -3513.
  • 8Park K H, Balathanigaimani M, Shim W G, et al. Ad-sorption characteristics of phenol on novel corn grain-based activated carbons [ J ]. Microporous and Meso-porous Materials, 2010,127(1) :1-8.
  • 9Mohamad N N, Lau L C, Lee K T, et al. Synthesis ofactivated carbon from lignocellulosic biomass and its ap-plications in air pollution control - A review [ J ]. Journalof Environmental Chemical Engineering, 2013, 1(4):658 -666.
  • 10Rathinam A, Rao J R,Nair B U. Adsorption of phenolonto activated carbon from seaweed : Determination of theoptimal experimental parameters using factorial design[J]. Journal of the Taiwan Institute of Chemical Engi-neers, 2011, 42(6) :952 -956.

二级参考文献14

  • 1庄毅璇,王枫,赵振业,杨小毛.活性炭的电解氧化再生研究[J].环境科学与技术,2011,34(S2):17-19. 被引量:3
  • 2张辉,郭玉鹏,刘艳华,赵旭,邓艳辉,王子忱,江雷.稻壳制备多孔炭对肌酐的吸附[J].物理化学学报,2007,23(6):825-829. 被引量:3
  • 3SONNENSCHEIN C, SOTO A M. An updated review of environmental estrogens and androgen mimics and antago- nists[J]. J Steroid Biochem Molec Biol, 1998,65( 16): 143 - 150.
  • 4XU G, LI F S, WANG Q H. Occurrence and degradation characteristics of dibutyl phthalate (DBP) and di-(2-eth- ylhexyl) phthalate (DEHP) in typical agricultural soils of China [ J]. Sei Total Environ, 2008,393 (2/3) : 333 - 340.
  • 5ZENG F, CUI K Y, XIE Z Y, et al. Phthalate esters ( PAEs ) : Emerging organic contaminants in agricultural soils in peg-urban areas around Guangzhou, China[J]. Environ Pollut, 2008,156 (2) :425 - 434.
  • 6PEIJNENBURG W J G M, STRUIJS J. Occurrence of phthalate esters in the environment of the Netherlands [J]. Eeotox Environm Safe,2006,63 (2) :204 - 215.
  • 7EMA M, MIYAWAKI E, KAWASHIMA K. Effects of dibutyl phthalate on reproductive function in pregnant and pseudopregnant rats[ J]. Reprod Toxicol, 2000,14 ( 1 ) : 13 -19.
  • 8FOSTER P M D, CATI'LEY R C, MYLCHREEST E. Effects of di-n-butyl phthalate (DBP) on male reproduc-tire development in the rat: Implications for human risk assessment [ J ]. Food Chem Toxicol, 2000, 38 : $97 - $99.
  • 9CADOGAN D. Health and environmental impact of phthalates [ J ]. Plastics Additives & Compounding, 2002, 4(6) : 28 -29.
  • 10ROSLEV P, VORKAMP K, AARUP J, et al. Degrada- tion of phthalate esters in an activated sludge wastewater treatment plant [ J ]. Water Res, 2007,41 ( 5 ) : 969 - 976.

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