Complexation of valinomycin with some univalent organic cations in nitrobenzene saturated with water

2013 ◽  
Vol 177 ◽  
pp. 432-435
Author(s):  
Emanuel Makrlík ◽  
Petr Vaňura ◽  
Pavel Selucký
1979 ◽  
Vol 44 (6) ◽  
pp. 1931-1941
Author(s):  
Jiří Vacík ◽  
Larisa K. Shataeva ◽  
Georgii V. Samsonov ◽  
Jaroslav Kálal ◽  
Jindřich Kopeček

Porous crosslinked copolymers of methacrylic acid with N-(2-hydroxypropyl) methacrylamide (HPMA) or (2-hydroxyethyl) methacrylate were prepared, and the relationship between their structure and the sorption of papain, bovine serumalbumin, chymotrypsinogen, pepsin, ovalbumin, insulin, novocain and oleandomycin were investigated. The presence of hydrophilic components in the gel structure makes possible additional interactions between sorbent and the compound sorbed. The occurrence of additional interactions (probably hydrogen bonds) is more pronounced with cation exchangers containing the (2-hydroxyethyl) methacrylate monomeric unit, which favourably affects the sorption of univalent organic cations but at the same time contributes to the denaturation of sorbed proteins. In contrast to univalent organic cations, cation exchangers containing the N-(2-hydroxypropyl) methacrylamide monomeric unit are more advantageous in the sorption of proteins, because due to the lower extent of additional interactions no irreversible denaturation of sorbed labile proteins takes place in this case.


2019 ◽  
Author(s):  
Eva M. Barea ◽  
Jesús Rodríguez-Romero ◽  
Bruno Clasen Hames ◽  
Iván Mora-Seró

2020 ◽  
Vol 86 (1) ◽  
pp. 254-263
Author(s):  
Wei You ◽  
Kristina M. Hugar ◽  
Ryan C. Selhorst ◽  
Megan Treichel ◽  
Cheyenne R. Peltier ◽  
...  

1983 ◽  
Vol 38 (1) ◽  
pp. 57-61 ◽  
Author(s):  
Hans Hartl ◽  
Farbod Mahdjour-Hassan-Abadi

N-Methylpyridinium-diiodocuprate(I), C6H8NCuI2 and dimethyl(3-dimethylamino-2-aza-2-propenyliden)ammonium-diiodocuprate(I), C6H14N3CuI2, are obtained by reacting Cu with C6H8NI3 or C6H14N3I3 in acetone. Both compounds are built up by the organic cations and chains of edge sharing tetrahedra1∞[Cul4/2-]. The iodocuprate(I) anions are in intimate contact with the cations via intermolecular I···C interactions. Though nearly the same average Cu-I distance of 267.2 or 268.2 pm was found for both iodocuprate(I) anions there are different Cu-Cu distances (301-354 pm).


Minerals ◽  
2020 ◽  
Vol 11 (1) ◽  
pp. 9
Author(s):  
Tomas Undabeytia ◽  
Uri Shuali ◽  
Shlomo Nir ◽  
Baruch Rubin

This review deals with modification of montmorillonite and other clay-minerals and clays by interacting them with organic cations, for producing slow release formulations of herbicides, and efficient removal of pollutants from water by filtration. Elaboration is on incorporating initially the organic cations in micelles and liposomes, then producing complexes denoted micelle- or liposome-clay nano-particles. The material characteristics (XRD, Freeze-fracture electron microscopy, adsorption) of the micelle– or liposome–clay complexes are different from those of a complex of the same composition (organo-clay), which is formed by interaction of monomers of the surfactant with the clay-mineral, or clay. The resulting complexes have a large surface area per weight; they include large hydrophobic parts and (in many cases) have excess of a positive charge. The organo-clays formed by preadsorbing organic cations with long alkyl chains were also addressed for adsorption and slow release of herbicides. Another examined approach includes “adsorptive” clays modified by small quaternary cations, in which the adsorbed organic cation may open the clay layers, and consequently yield a high exposure of the siloxane surface for adsorption of organic compounds. Small scale and field experiments demonstrated that slow release formulations of herbicides prepared by the new complexes enabled reduced contamination of ground water due to leaching, and exhibited enhanced herbicidal activity. Pollutants removed efficiently from water by the new complexes include (i) hydrophobic and anionic organic molecules, such as herbicides, dissolved organic matter; pharmaceuticals, such as antibiotics and non-steroidal drugs; (ii) inorganic anions, e.g., perchlorate and (iii) microorganisms, such as bacteria, including cyanobacteria (and their toxins). Model calculations of adsorption and kinetics of filtration, and estimation of capacities accompany the survey of results and their discussion.


2021 ◽  
pp. 100759
Author(s):  
Hock Beng Lee ◽  
Neetesh Kumar ◽  
Barkha Tyagi ◽  
Siwei He ◽  
Rishabh Sahani ◽  
...  

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