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本文采用改性与化学再生方法,探索天然斜发沸石对氨氮吸附的最佳改性及化学再生条件.无机盐改性、热改性、有机改性试验结果表明,最佳改性方法为无机盐NaCl法,改性沸石吸附量较天然沸石提升了近20%,最佳NaCl浓度为1 mol·L-1;热改性法不能显著提高沸石的氨氮吸附容量,相反高温会破坏其结构;十二烷基苯磺酸钠改性法可以使改性沸石在其表面形成了新的阳离子吸附点,使其吸附性能提升;而十六烷基三甲基溴化铵改性沸石表面形成的是阴离子吸附点,对带正电的NH4+会产生排斥,导致其吸铵性能下降.化学再生试验表明,KCl溶液对铵饱和沸石的再生效果最显著,适宜再生浓度为0.1-0.2 mol·L-1.经KCl再生后的沸石再次通过NaCl改性,可延长沸石使用周期以及提高再生沸石的吸附能力.

Modification and chemical regeneration methods were adopted to explore the optimum condition of natural clinoptilolite for ammonium nitrogen adsorption.Salt modification,thermal modification and organic modification results indicated that inorganic salt (NaCl) solution modification method was the best and the ammonium adsorption capacity increased nearly 20%,with 1 mol· L-1 NaCl.Thermal modification method did not improve the ammonia nitrogen adsorption capacity significantly.On the contrary,the structure of clinoptilolite was destroyed by high temperature.When sodium dodecyl benzene sulfonate modification method was used,there were new positive ion adsorption sites on the surface of modified clinoptilolite and its ammonium adsorption capacity increased.However,cetyl trimethyl ammonium bromide modification increased negative ion adsorption sites,which were ammonium repellent,and decreased the ammonium adsorption capacity.Chemical regeneration tests showed that,KCl solution was the best regeneration method of ammonium saturated clinoptilolite,with suitable KCl concentration of 0.1-0.2 mol· L-1.KClmodified clinoptilolite which were remodified by NaCl solution might have longer life cycle and higher adsorption capacity than before.

参考文献

[1] 张翠玲;常青;张家利;高彩丽.天然沸石对农田退水中氨氮的去除[J].环境化学,2012(7):1063-1068.
[2] Lecheng Lei;Xiaojuan Li;Xingwang Zhang.Ammonium removal from aqueous solutions using microwave-treated natural Chinese zeolite[J].Separation and Purification Technology,20083(3):359-366.
[3] 张瑛洁;陈雷;马军;张亮;姚军;吴培瑛.微波强化NaCl改性沸石的除氨氮效果研究[J].中国给水排水,2009(1):72-74.
[4] 佟小薇;朱义年.沸石改性及其去除水中氨氮的实验研究[J].环境工程学报,2009(4):635-638.
[5] 江乐勇;林海;赵志英;贾小宇.盐热改性沸石去除氨氮的性能研究[J].水处理技术,2010(8):25-28,32.
[6] 丁真贞;孟绫;董建勋;胡晓静;宋娟娟;朱宝林;张守民;黄唯平.改性斜发沸石处理高浓度氨氮废水[J].环境化学,2012(8):1232-1237.
[7] 孙同喜;郑萌璐;蒋轶锋;陈建孟;陈浚.NaCl改性沸石对氨氮吸附性能的研究[J].环境污染与防治,2010(10):46-50,71.
[8] Lin Lin;Zhongfang Lei;Li Wang.Adsorption mechanisms of high-levels of ammonium onto natural and NaCl-modified zeolites[J].Separation and Purification Technology,2013:15-20.
[9] 张道方;王瑞璞;吕娟;曾跃.改性沸石生物滤池处理中水景观污染水体实验研究[J].水资源与水工程学报,2008(5):1-5.
[10] 陈和谦;吴志超;黄友谊.沸石联合生物吸附再生工艺可行性研究[J].环境污染治理技术与设备,2005(8):26-29.
[11] 李云辉;安莹.吸铵饱和沸石的生物再生性能[J].净水技术,2013(1):60-63.
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