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on goethite-coated sand in the presence of humic acid. Water Res 2002, 36:4943–4950.CrossRef 35. selleck products Phuengprasop T, Sittiwong J, Unob F: Removal of heavy metal ions by iron oxide coated sewage sludge. J Hazard Mater 2011, 186:502–507.CrossRef 36. Yantasee W, Warner CL, Sangvanich T: Removal of heavy metals from aqueous systems with thiol functionalized superparamagnetic nanoparticles. Environ Sci Technol 2007, 41:5114–5119.CrossRef 37. Xu P, Zeng GM, Huang DL, Lai C, Zhao MH, Wei Z, Li NJ, Huang C, Xiem GX: Adsorption of Pb(II) by iron oxide nanoparticles immobilized Phanerochaete chrysosporium : equilibrium, kinetic, thermodynamic and mechanisms analysis. Chem Eng J 2012, 203:423–431.CrossRef Competing interests The authors declare that they have no competing interests. Authors’ contributions YHK designed and analyzed the ZOCF by using measurements (SEM, TEM, XRD, and PL) and analyzing each sample. DKVR characterized the capacity of the sample to remove Pb(II) metals. The overall experiment and preparation of the manuscript were carried out under the instruction of JSY. All authors read and approved the final

manuscript.”
“Background Nowadays, plasmonic materials and structures are the subject of wide-scale studies. In addition to metals, new materials like wide bandgap semiconductors [1, 2] and glass-metal nanocomposites (GMN) Orotic acid [3–5], that are glasses embedded with metal nanoparticles, have recently been implemented in plasmonics. Since the dielectric function and, consequently, the propagation of surface plasmon polariton modes in the latter materials can be controlled by varying the volume fraction, size, and type of metal inclusions [5–7], the flexibility of GMN makes them attractive for plasmonics. The required dimensions of the majority of plasmonic structures [8–10] are in tens of nanometers scale, which compels the use electron beam lithography (EBL) in their fabrication. That is why the search for an alternative cost-effective technique for their manufacturing is of interest.

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