Hostname: page-component-cd9895bd7-8ctnn Total loading time: 0 Render date: 2024-12-29T12:33:57.944Z Has data issue: false hasContentIssue false

Adsorption of Low-Concentration Ammonium Onto Vermiculite from Hebei Province, China

Published online by Cambridge University Press:  01 January 2024

Mingshan Wang
Affiliation:
School of Material Sciences and Technology, China University of Geosciences, Beijing, 100083, China
Libing Liao*
Affiliation:
School of Material Sciences and Technology, China University of Geosciences, Beijing, 100083, China
Xiuli Zhang
Affiliation:
School of Material Sciences and Technology, China University of Geosciences, Beijing, 100083, China
Zhaohui Li
Affiliation:
Department of Geosciences, University of Wisconsin — Parkside, 900 Wood Road, Kenosha, WI 53144, USA
Zhiguo Xia
Affiliation:
School of Material Sciences and Technology, China University of Geosciences, Beijing, 100083, China
Weida Cao
Affiliation:
School of Material Sciences and Technology, China University of Geosciences, Beijing, 100083, China
*
* E-mail address of corresponding author: lbliao@cugb.edu.cn
Rights & Permissions [Opens in a new window]

Abstract

Core share and HTML view are not available for this content. However, as you have access to this content, a full PDF is available via the ‘Save PDF’ action button.

Vermiculite is a common layered silicate clay mineral which has good adsorption and ion-exchange properties, and which is used to remove pollutants from groundwater. The adsorption by vermiculite from Heibei Province, China, of low-concentration ammonium in water was assessed here to evaluate the effects of adsorption time, particle size, adsorbent dose, pH, and temperature. Using Fourier-transform infrared spectroscopy, the concentration of NH4+ at 1430 cm−1 was evaluated after ammonium was adsorbed by vermiculite. Based on Langmuir-model analysis, the adsorption capacity of the Chinese vermiculite (in the particle-size range 0.025–0.075 mm) for ammonium was 18 mg/g after 3 h of equilibration. Optimal adsorption occurred at pH 6–7 and 60°C, which is different from that at high ammonium concentrations. Smaller particle-size fractions showed greater degrees of adsorption. Increase in Mg2+, K+, or Na+ concentrations influenced ammonium adsorption and, therefore, indicated that cation exchange was the mechanism for ammonium uptake from low-concentration solutions.

Type
Article
Copyright
Copyright © Clay Minerals Society 2011

References

Arun, R.G., 1999 Design and construction techniques for permeable reactive barriers Journal of Hazardous Materials 68 4171 10.1016/S0304-3894(99)00031-X.Google Scholar
Boumer, E.J. and Crowe, P.B., 1988 Biological process in drinking water treatment Journal of the American Water Works Association 80 8293.Google Scholar
David, H.B. Nicholas, A.H. and Richard, A.B., 2000 Performance of air sparging systems: a review of case studies Journal of Hazardous Materials 72 101119 10.1016/S0304-3894(99)00136-3.Google Scholar
Evangelou, V.P. and Lumbanraja, J., 2002 Ammoniumpotassium-calcium exchange on vermiculite and hydroxyaluminum vermiculite Soil Science Society of America Journal 66 445455 10.2136/sssaj2002.4450.Google Scholar
Famer, V.C., 1974 Monograph Infrared Spectra of Minerals 4 262288.Google Scholar
Fetter, C.W., 1993 Contaminant Hydrogeology New York Macmillan Publishing Company.Google Scholar
Gilberto, A. and Jorge, C.M., 2003 Influence of pH and ionic strength on removal processes ofa sedimentary humic acid in a suspension of vermiculite Colloids and Surfaces A: Physicochemical and Engineering Aspects 226 2534 10.1016/S0927-7757(03)00418-7.Google Scholar
Gilberto, A. and Jorge, C.M., 2005 Influence of pH, ionic strength and humic acid on adsorption ofCd(II) and Pb(II) onto vermiculite Colloids and Surfaces A: Physicochemical and Engineering Aspects 262 3339 10.1016/j.colsurfa.2005.04.005.Google Scholar
Grim, R.E., 1953 Clay Mineralogy New York McGraw-Hill Book Co., Inc. 10.1097/00010694-195310000-00009.CrossRefGoogle Scholar
Hu, Y.L. Wu, X.F. and Nie, F.H., 2004 Study ofremov al rate ofammoni um by vermiculite adsorption Journal of Central South Forestry University 24 3033.Google Scholar
James, L.C. and Judith, W., 2006 An Apatite II permeable reactive barrier next term to remediate groundwater containing Zn, Pb and Cd Applied Geochemistry 21 21882200 10.1016/j.apgeochem.2006.08.018.Google Scholar
Karadag, D. Koc, Y. Turan, M. and Armagan, B., 2006 Removal ofammoni um ion from aqueous solution using natural Turkish clinoptilolite Journal of Hazardous Materials 136 604609 10.1016/j.jhazmat.2005.12.042.CrossRefGoogle Scholar
Langwaldt, J.H. and Puhakka, J.A., 2000 On-site biological remediation ofcontaminated groundwater: a review Environmental Pollution 107 187197 10.1016/S0269-7491(99)00137-2.CrossRefGoogle Scholar
Lin, L. Chan, G.Y.S. Jiang, B.L. and Lan, C.Y., 2007 Use of ammoniacal nitrogen-tolerant microalgae in landfill leachate treatment Waste Management 27 13761382 10.1016/j.wasman.2006.09.001.CrossRefGoogle ScholarPubMed
Marinos, Y.S., 2007 Removal ofCu(II) in fixed bed and batch reactors using natural zeolite and exfoliated vermiculite as adsorbents Desalination 215 133142 10.1016/j.desal.2006.10.031.Google Scholar
Mitsch, W.J. and Cronk, J.K., 1992 Creation and restoration ofwet lands: some design consideration for ecological engineering Advances in Soil Science 17 217255 10.1007/978-1-4612-2820-2_8.CrossRefGoogle Scholar
Panuccio, M.R., 2009 Cadmium adsorption on vermiculite, zeolite and pumice: Batch experimental studies Journal of Environmental Management 90 364374 10.1016/j.jenvman.2007.10.005.CrossRefGoogle ScholarPubMed
Reddy, K.R. and Smith, W.H., 1987 Aquatic Plants for Water Treatment and Resource Recovery Orlando, Florida, USA Magnolia Publishing Inc.Google Scholar
Saha, U.K. Taniguchi, S. and Sakurai, K., 2001 K/Ca and NH4/Ca selectivity ofhydroxyalum inum-interlayered vermiculite and montmorillonite: Contribution from regular and frayed edge exchange sites Soil Science and Plant Nutrition 47 455466 10.1080/00380768.2001.10408410.CrossRefGoogle Scholar
Schroeder, P.A. and Ingall, E.D., 1994 A method for the determination ofnitrogen in clays, with application to the burial diagenesis ofshales Journal of Sedimentary Research 64 694697 10.1306/D4267E79-2B26-11D7-8648000102C1865D.CrossRefGoogle Scholar
Scott, A.D. Hanway, J.J. and Edwards, A.P., 1958 Replaceability ofammonium in vermiculite with acid solutions Soil Science Society of America Journal 22 388392 10.2136/sssaj1958.03615995002200050006x.CrossRefGoogle Scholar
Socías-Viciana, M.M. Hermosin, M.C. and Cornejo, J., 1998 Removing prometrone from water by clays and organic clays Chemosphere 37 289300 10.1016/S0045-6535(98)00047-2.CrossRefGoogle Scholar
Sawhney, B.L., 1970 Potassium and cesium ion selectivity in relation to clay mineral structure Clays and Clay Minerals 18 4752 10.1346/CCMN.1970.0180106.CrossRefGoogle Scholar
Vogan, J.L. Focht, R.M. Clark, D.K. and Graham, S.L., 1997 Performance evaluation of a permeable reactive barrier for remediation of dissolved chlorinated solvents in groundwater Journal of Hazardous Materials 68 97108 10.1016/S0304-3894(99)00033-3.CrossRefGoogle Scholar
Wu, P.X., 2005 Existing status ofint erlayer water in vermiculite mineral material Journal of the Ceramic Society 33 209214.Google Scholar
Wu, X.F. Zhao, F. Chen, M.L. Ji, Z.H. and Ma, Q., 2009 A simple way ofcalcu lating the change in the Gibbs’ free energy ofion adsorption reactions Adsorption Science & Technology 27 118 10.1260/0263-6174.27.10.907.Google Scholar
Zheng, H. Han, L.J. and Ma, H.W., 2008 Adsorption characteristics ofammonium ion by zeolite 13X Journal of Hazardous Materials 158 577584 10.1016/j.jhazmat.2008.01.115.CrossRefGoogle ScholarPubMed