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摘要
采用农业废弃物棉杆改性处理含铬废水,研究其对废水中Cr6+的吸附性能,考察了废液pH、棉杆用量、吸附时间、温度以及废液浓度等对Cr6+去除率的影响。结果表明,将棉杆置于0.015mol/L高锰酸钾溶液中改性4h,当废液pH=1、棉杆用量为0.3g、吸附温度为45℃、吸附时间为60min时,废水中Cr6+离子的去除率可达99.9%,较未改性的棉杆提高了26.3%。扫描电镜观察发现,改性前后棉杆吸附位点数量明显增加。采用Lagergren准二级动力学模型和Langmuir等温吸附模型可准确描述吸附模型,拟合实验数据所得平衡吸附量为3.08mg/g,与实验结果相符。这种改性处理含铬废水的方法操作简单、价格低廉,适合于低浓度废水处理,有利于固体废弃物的资源化利用。
Abstract
Chromium-containing wastewater was treated with modified agricultural waste cotton stalk to study the adsorption performance for Cr6+. The effects of pH value,amount of cotton stalk,adsorption time,temperature and concentration of waste liquid on the removal rate of Cr6+ were investigated.The results showed that when the pH value of the waste liquid was 1,the amount of cotton stem was 0.3g,the adsorption temperature was 45℃,the adsorption time was 60 min,The removal rate of Cr6+ was up to 99.9%,which was 26.3% higher than that of unmodified cotton.At the same time,the scanning electron microscope scanning showed that the number of adsorption sites increased obviously.The adsorption model can be accurately described by the Lagergren quasi-second-order kinetics model and Langmuir isothermal adsorption model.The equilibrium adsorption capacity was 3.08mg/g,which was in accordance with the experimental data.The modified chromium-containing wastewater treatment method was simple in operation and low in cost,and was suitable for the treatment of low concentration waste water and was favorable for the utilization of solid wastes.
关键词
废水处理
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六价铬
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改性棉杆
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吸附模型
Key words
waste water treatment
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Cr6+
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modified cotton stalk
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absorbance model
棉杆改性处理含铬废水及其吸附模型研究[J].
化工新型材料, 2018, 46(5): 274-277 DOI:
[1] 王帅,商建英,胡克林,等.溶液初始pH值及裂解温度对玉米秸秆基生物炭吸附Cr6+的影响[J].农业资源与环境学报,2016,33(5):443-448.
[2] 孙金香,王海增.废弃Mg(OH)2/AC焙烧产物对染料吸附性能研究[J].中国环境科学,2014,34(2):390-395.
[3] 高嘉敏,毛媛媛,施莉莉,等.植物在废水重金属离子吸附中的应用[J].化学工程师,2013(9):41-43.
[4] 王忆娟.三种农业废弃物对废水中Pb2+吸附性能的比较[J].化学与生物工程,2013,30(7):79-82.
[5] 赵梅青,马子川,吴银素,等.KMnO4改性活性炭对Zn2+和Cd2+的吸附研究[J].东北师大学报(自然科学版),2010,42(2):97-100.
[6] 黄色燕,刘云凤,曹威,等.改性稻草对Cr6+的吸附动力学[J].环境化学,2013,32(2):240-248.
[7] 孙凤,臧传峰,闫腾,等.HBP-NH2改性棉纤维吸附剂的制备及性能研究[J].国际纺织导报,2014(3):83-86.
[8] 赵业军,苏远安,王莹莹.花生壳改性处理含铅废水及吸附机理研究[J].应用化工,2016,45(3):453-455;460.
[9] 雷娟,易筱筠,杨琛,等.改性花生壳对Cd(Ⅱ)和Pb(Ⅱ)的吸附机理[J].环境工程学报,2014,9(5):1775-1783.
[10] 李文斌,孟昭福,吴琼,等.添加复合吸附剂对塿土吸附菲和Cr(Ⅵ)的影响[J].环境科学,2016,37(11):4419-4427.
[11] Shaaban A,Se S M,Dimin M F,et al.Influence of heating temperature and holding time on biochars derived from rubber wood sawdust via slow pyrolysis[J].Journal of Analytical and Applied Pyrolysis,2014,107:31-39.
[12] 李紫薇,李小敏,袁圣银,等.棉杆对水中碱性品红的吸附研究[J].水处理技术,2015,41(4):66-70.
基金资助
塔里木大学校长基金(TDZKQNZD201501),北京化工大学化工资源有效利用国家重点实验室开放课题(CRE-2015-C-111)