Synthesis, characterization, and property test of crystalline polyferric sulfate adsorbent used in treatment of contaminated water with a high As(III) content

Ping-chao Ke , Zhi-hong Liu , Lin Li

International Journal of Minerals, Metallurgy, and Materials ›› 2018, Vol. 25 ›› Issue (10) : 1217 -1225.

PDF
International Journal of Minerals, Metallurgy, and Materials ›› 2018, Vol. 25 ›› Issue (10) : 1217 -1225. DOI: 10.1007/s12613-018-1674-8
Article

Synthesis, characterization, and property test of crystalline polyferric sulfate adsorbent used in treatment of contaminated water with a high As(III) content

Author information +
History +
PDF

Abstract

A crystalline polyferric sulfate (PFS) adsorbent was synthesized by oxidizing and precipitating ferrous ions in air atmospheric conditions. The morphology, structure, specific surface area (SSA), and adsorptive efficacy of the adsorbent to As(III) were characterized by scanning electron microscope (SEM) and transmission electron microscopy (TEM) images, X-ray diffraction (XRD) patterns, Fourier- transform infrared (FTIR) spectra, BET SSA analyses, and adsorption experiments. The adsorbent showed a near-spherical aggregate structure and had good crystallinity. A significant amount of α-goethite co-precipitated with PFS in the case of the initial ferrous concentration of 1 mol/L and increased SSA of the adsorbent. The stability region of ferric compounds in the process was drawn and applied to analyze the iron behavior during the synthesis. The adsorption of As(III) in high As(III)-containing solutions fitted the Langmuir isotherm model adequately. The absorbent with co-precipitation of α-goethite showed good adsorbability for As(III) and good filtering performance in the high As(III)-containing solution of 10–100 mg/L under acidic, neutral, and alkaline conditions (pH 2.09–9.01). After the adsorption process, the stability of the residues bearing As(III) was evaluated by toxic characteristic leaching procedure (TCLP) tests. The results indicated that the residues were extremely stable, and the concentrations of arsenic in the leaching solutions were less than 0.01 mg/L.

Keywords

polyferric sulfate / crystal structure / α-goethite / high As(III)-containing contaminated water / wide pH range / As(III) adsorption

Cite this article

Download citation ▾
Ping-chao Ke, Zhi-hong Liu, Lin Li. Synthesis, characterization, and property test of crystalline polyferric sulfate adsorbent used in treatment of contaminated water with a high As(III) content. International Journal of Minerals, Metallurgy, and Materials, 2018, 25(10): 1217-1225 DOI:10.1007/s12613-018-1674-8

登录浏览全文

4963

注册一个新账户 忘记密码

References

[1]

Nazari A.M., Radzinski R., Ghahreman A. Review of arsenic metallurgy: Treatment of arsenical minerals and the immobilization of arsenic. Hydrometallurgy, 2017, 174, 258.

[2]

Hopkin W. The problem of arsenic disposed in non–ferrous metals production. Environ. Geochem. Health, 1989, 11(3–4): 101.

[3]

Pettine M., Campampanella L., Millero F.J. Arsenite oxidation by H2O2 in aqueous solutions. Geochim. Cosmochim. Acta, 1999, 63(18): 2727.

[4]

Ouzounis K., Katsoyiannis I., Zouboulis A., Mitrakas M. Is the coagulation–filtration process with Fe(III) efficient for As(III) removal from groundwaters. Sep. Sci. Technol., 2015, 50(10): 1587.

[5]

Mohan D., Charles U.P.J. Arsenic removal from water/wastewater using adsorbents—A critical review. J. Hazard. Mater., 2007, 142(1–2): 1.

[6]

Cui J.L., Jing C.Y., Che D.S., Zhang J.F., Duan S.X. Groundwater arsenic removal by coagulation using ferric(III) sulfate and polyferric sulfate: A comparative and mechanistic study. J. Environ. Sci., 2015, 32, 42.

[7]

Mertens J., Casentini B., Masion A., Pöthig R., Wehrli B., Furrer G. Polyaluminum chloride with high Al30 content as removal agent for arsenic–contaminated well water. Water Res., 2012, 46(1): 53.

[8]

Tresintsi S., Simeonidis K., Vourlias G., Stavropoulos G., Mitrakas M. Kilogram–scale synthesis of iron oxy–hydroxides with improved arsenic removal capacity: Study of Fe(II) oxidation–precipitation parameters. Water Res., 2012, 46(16): 5255.

[9]

Zouboulis A.I., Moussas P.A., Vasiiakou F. Polyferric sulphate: Preparation, characterization and application in coagulation experiments. J. Hazard. Mater., 2008, 155(3): 459.

[10]

Zhang X., Wang X.Y., Chen Q.R., Lv Y., Han X.Z., Wei Y.X., Xu T.W. Batch preparation of high basicity polyferric sulfate by hydroxide substitution from bipolar membrane electrodialysis. ACS Sustainable Chem. Eng., 2017, 5(3): 2292.

[11]

Fan M.H., Sung S.W., Browm R.C., Wheelock T.D., Laabs F.C. Synthesis, characterization, and coagulation of polymeric ferric sulfate. J. Environ. Eng., 2002, 128(6): 483.

[12]

Zouboulis A., Katsoyiannis I. Removal of arsenates from contaminated water by coagulation–direct filtration. Sep. Sci. Technol., 2001, 37(12): 2859.

[13]

Fujita T., Fujieda S., Shinoda K., Suzuki S. Environmental leaching characteristics of scorodite synthesized with Fe(II) ions. Hydrometallurgy, 2012, 111–112, 87.

[14]

B. Harris, The removal of arsenic from process solutions: Theory and industrial practice, [in] Hydrometallurgy 2003—Fifth International Conference in Honor of Professor Ian Ritchie—Volume 2: Electrometallurgy and Environmental Hydrometallurgy, Edited by C. Young, A. Alfantazi, C. Anderson, A. James, D. Dreisinger, and B. Harris, Warrendale, 2003, p. 1889.

[15]

Paul M.R. Arsenic encapsulation using Portland cement with ferrous sulfate/lime and Terra–BandTM technologies—microcharacterization and leaching studies. Sci. Total Environ., 2012, 420, 300.

[16]

de Klerk R.J., Jia Y.F., Daenzer R., Gomez M.A., Demopoulos G.P. Continuous circuit coprecipitation of arsenic(V) with ferric iron by lime neutralization: Process parameter effects on arsenic removal and precipitate quality. Hydrometallurgy, 2012, 111–112, 65.

[17]

Demopoulos G.P., Droppert D.J., Van Weet G. Precipitation of crystalline scorodite (FeAsO4·2H2O) from chloride solutions. Hydrometallurgy, 1995, 38(3): 245.

[18]

Streat M., Hellgradt K., Newton N.L.R. Hydrous ferric oxide as an adsorbent in water treatment: Part. Preparation and physical characterization. Process Saf. Environ. Prot., 2008, 86(1): 1.

[19]

Hlavay J., Polyak K. Determination of surface properties of iron hydroxide–coated alumina adsorbent prepared for removal of arsenic from drinking water. J. Colloid Interface Sci., 2005, 284(1): 71.

[20]

Hodi M., Polyak K., Hlavay J. Removal of pollutants for drinking water by combined ion–exchange and adsorption methods. Environ. Int., 1995, 21(3): 325.

[21]

Kundu S., Gupta A.K. Analysis and modeling of fixed bed column operations on As(V) removal by adsorption onto iron oxide–coated cement (IOCC). J. Colloid Interface Sci., 2005, 290(1): 52.

[22]

Li F.T., Ji G., Xue G. The preparation of inorganic coagulant polyferric sulphate. J. Chem. Technol. Biotechnol., 1997, 123(9): 859.

[23]

Kurokawa H., Senna M. Bench scale control of the crystallite size and morphology of goethite particles by different ferrous source. Mater. Sci. Eng. B, 2006, 135(1): 55.

[24]

Liao S.J., Wang J., Zhu D.W., Ren L.Y., Zhou W.B., Ding W. Structural characteristics of goethite and its B–loaded oxides. Acta Pedolog. Sin., 2006, 43(5): 742.

[25]

Lakshmipathiraj P., Narasimhan B.R.V., Prabhskar S., Raju G.B. Adsorption of arsenate on synthetic goethite from aqueous solutions. J. Hazard. Mater., 2006, 136(2): 281.

[26]

Fujita T., Taguchi R., Abumiya M., Matsumoto M., Shibata E., Nakamura T. Effect of pH on atmospheric scorodite synthesis by oxidation of ferrous ions: Physical properties and stability of the scorodite. Hydrometallurgy, 2009, 96(3): 189.

[27]

Mukhopadhyay R., Manjaiah K.M., Datta S.C., Yadav R.K., Sarkar B. Inorganically modified clay minerals: Preparation, characterization, and arsenic adsorption in contaminated water and soil. Appl. Clay Sci., 2017, 147, 1.

[28]

Thirunavukkarasu O.S., Viraraghavan T., Subramanian K.S., Chaalal O., Islam M.R. Arsenic removal in drinking water–impacts and novel removal technologies. Energy Sources, 2005, 27(1–2): 209.

[29]

Lenoble V., Laclatre C., Deluchat V., Serpaud B., Bollinger J.C. Arsenic removal by adsorption on iron(III) phosphate. J. Hazard. Mater., 2005, 123(1–3): 262.

[30]

Min J.H., Hering J.G. Arsenate sorption by FE(III)–doped alginate gels. Water Res., 1998, 32(5): 1544.

[31]

Isao Y., Hiroshi K., Keihei U. Selective adsorption of arsenic ions on silica gel impregnated with ferric hydroxide. Anal. Lett., 1976, 9(12): 1125.

[32]

Ladeira A.C.Q., Ciminelli V.S.T. Adsorption and desorption of arsenic on an oxisol and its constituents. Water Res., 2004, 38(8): 2087.

[33]

Ke P., Liu Z. Fe(III)−As(V) precipitates obtained from a sulphate system and their leach stability. Can. Metall. Q., 2018, 57(3): 304.

AI Summary AI Mindmap
PDF

148

Accesses

0

Citation

Detail

Sections
Recommended

AI思维导图

/