Improving Pd–N–C fuel cell electrocatalysts through fluorination-driven rearrangements of local coordination environment

Nature Energy ◽  
2021 ◽  
Author(s):  
Jinfa Chang ◽  
Guanzhi Wang ◽  
Maoyu Wang ◽  
Qi Wang ◽  
Boyang Li ◽  
...  
Nano Research ◽  
2020 ◽  
Vol 13 (7) ◽  
pp. 1842-1855 ◽  
Author(s):  
Xinyuan Li ◽  
Hongpan Rong ◽  
Jiatao Zhang ◽  
Dingsheng Wang ◽  
Yadong Li

1993 ◽  
Vol 32 (25) ◽  
pp. 5868-5877 ◽  
Author(s):  
Mikyung Cha ◽  
Christine L. Gatlin ◽  
Susan C. Critchlow ◽  
Julie A. Kovacs

2010 ◽  
Vol 494 (4-6) ◽  
pp. 289-294 ◽  
Author(s):  
Konstantinos C. Christoforidis ◽  
Maria Louloudi ◽  
Yiannis Deligiannakis

2011 ◽  
Vol 40 (15) ◽  
pp. 3914 ◽  
Author(s):  
Michael P. Redmond ◽  
Stephanie M. Cornet ◽  
Sean D. Woodall ◽  
Daniel Whittaker ◽  
David Collison ◽  
...  

2020 ◽  
Author(s):  
Teresa Zahoransky ◽  
Christian Mikutta

<p>Being one of Earth´s most redox-active elements, manganese participates in a great variety of environmental processes and is recognized as a key player controlling carbon turnover and oxidative transformation of organic and inorganic pollutants in soils. Moreover, Mn(III), Mn(IV) or mixed-valence Mn(III/IV) oxides and (oxy)hydroxides are highly effective sorbents for metal pollutants and nutrients in soils. Chemical reactivity, mobility, and bioavailability of Mn depend crucially on its speciation (chemical form). Yet, speciation studies on soil Mn are scarce. Therefore, we employed Mn K-edge (6,539 eV) X-ray absorption spectroscopy (XAS) to determine the oxidation states and local coordination environment (<5 Å) of Mn in oxic bulk soils (Cambisols, Luvisols, Stagnosol) from various field sites in Germany. Our XAS analyses cover 23 soil L, O, A, B, and C horizons exhibiting total Mn concentrations of between 200 and 2,300 mg/kg. For comparison, we also analyze a suite of 31 Mn reference compounds, including Mn carbonate, phosphate, oxides and (oxy)hydroxides, silicates, organic Mn compounds as well as clay and hydroxide minerals with adsorbed Mn(II). X-ray absorption near-edge structure (XANES) spectra are evaluated for the oxidation states of soil Mn using linear combination fit (LCF) analysis. In addition, the average local coordination environment of Mn in the soil samples is assessed by shell-fitting of extended X-ray absorption fine structure (EXAFS) spectra. Based on our XAS results, we will test the following hypotheses: (1) Soil L/O horizons comprise predominantly organically complexed Mn(II) and Mn(III), dominated by the former Mn species; (2) soil A horizons are dominated by Mn(III/IV) in Mn(III/IV)-oxide structures owing to high microbial activity, release of Mn(II) from primary silicates and/or plant residues, and its subsequent (a)biotic oxidation and precipitation as Mn(III/IV) oxides; (3) soil B horizons of different genesis differ in their bulk Mn speciation; Bt horizons of Luvisols are dominated by Mn(II) associated with phyllosilicates, whereas the Stagnosol Bg horizon is dominated by layer-type Mn(III/IV) oxides. In summary, our study will provide first comprehensive data on bulk Mn speciation in three major European soil types. This knowledge is a prerequisite for a better understanding of the biogeochemical Mn cycle in soils.</p>


Clay Minerals ◽  
2002 ◽  
Vol 37 (4) ◽  
pp. 639-649 ◽  
Author(s):  
Balwant Singh ◽  
D. M. Sherman ◽  
R. J . Gilkes ◽  
M. A. Wells ◽  
J . F. W. Mosselmans

AbstractThe crystal-chemical mechanisms by which transition metals are associated with goethite are fundamental to our understanding of the solubility and bioavailability of micronutrients and heavy metals in soils, and in the formation of laterite ore deposits. Transition metals such as Cr, Mn and Ni may sorb onto goethite by forming surface precipitates, surface complexes or by replacing Fe3+ in the goethite structure. In the work reported here, we investigated the local coordination environment of Cr, Mn and Ni in synthetic goethite using EXAFS spectroscopy. We demonstrate the isomorphous substitution for Fe3+ by Cr3+ (up to 8 mol.%), Mn3+ (up to 15 mol.%) and Ni2+ (up to 5 mol.%). We find, however, that the next-nearest-neighbour coordination environment changes with composition. The perturbations are likely to be responsible for limiting the accommodation of Cr3+, Mn3+ or Ni2+ in the FeOOH structure.


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