Fe3O4@MnO2 inorganic magnetic sorbent: Preparation, characterization and application for Ru(III) ions sorption

Author(s):  
Iga Zuba ◽  
Andrzej Pawlukojć ◽  
Janusz Waliszewski ◽  
Olya Ivanshina
2013 ◽  
Vol 73 (1) ◽  
pp. 46-52 ◽  
Author(s):  
Pavel Janoš ◽  
Martin Kormunda ◽  
František Novák ◽  
Ondřej Životský ◽  
Jitka Fuitová ◽  
...  

RSC Advances ◽  
2016 ◽  
Vol 6 (4) ◽  
pp. 3350-3361 ◽  
Author(s):  
K. Z. Elwakeel ◽  
A. A. El-Bindary ◽  
A. Z. El-Sonbati ◽  
A. R. Hawas

Magnetic sorbent microgranules with magnetite (Fe3O4) core and glycidyl methacrylate/N,N′​-methylenebisacrylamide shell were prepared. The sorbent was tested for Acid Yellow 99 dye removal from aqueous solution.


2018 ◽  
Vol 54 (3-4) ◽  
pp. 273-277
Author(s):  
I. V. Dolbnya ◽  
E. A. Tatarintseva ◽  
E. A. Bukharova ◽  
L. N. Ol’shanskaya

RSC Advances ◽  
2017 ◽  
Vol 7 (14) ◽  
pp. 8718-8726 ◽  
Author(s):  
Kouroush Salimi ◽  
Duygu Deniz Usta ◽  
İlkay Koçer ◽  
Eda Çelik ◽  
Ali Tuncel

A magnetic sorbent based on monodisperse-porous silica microspheres was developed for His-tagged protein purification by immobilized metal affinity chromatography.


2002 ◽  
Vol 37 (16) ◽  
pp. 3673-3691 ◽  
Author(s):  
F. Macášek ◽  
J. D. Navratil ◽  
S. Dulanská

2019 ◽  
Vol 80 (6) ◽  
pp. 1063-1075 ◽  
Author(s):  
Suhe Li ◽  
Ying Yao ◽  
Tuo Zhao ◽  
Meiling Wang ◽  
Feng Wu

Abstract This study prepared nine biochars from three biomass wastes (CompostA, CompostB and Sludge) through different carbonization conditions. The adsorption behaviors and mechanisms of these biochars for Pb(II) were tested by a series of adsorption experiments and properties analysis. Preliminary experiments showed biochars obtained from CompostA and Sludge had better Pb(II) adsorption performance than CompostB and the optimum carbonization temperature of CompostA was lower than that of Sludge. Adsorption experimental results demonstrated that CompostA600 (numbers represent carbonization temperatures) had the largest adsorption capacity of 57.34 mg/g for Pb(II) among samples, followed by Sludge800 of 50.00 mg/g. The kinetic adsorption of CompostA600 and Sludge800 were both described by the Nth-order model very well. Pb(II) adsorption of CompostA600 most appropriately followed the Langmuir–Freundlich model and the Redlich–Peterson model. Characterization analysis suggested diverse carbonization temperatures and precursors caused discrepant pore size distributions and element contents, which determined the deposition of lead compound crystals on materials. This study examined the effects of raw materials and carbonization temperatures on obtained biochars and provided an inexpensive and environmental-friendly way for biochar sorbent preparation and heavy metal wastewater treatment.


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