34 research outputs found
Amorphous Nickel Hydroxide Nanosheets with Ultrahigh Activity and Super-Long-Term Cycle Stability as Advanced Water Oxidation Catalysts
Good
conductivity is conventionally considered as a typical reference
standard in terms of selecting water electrolysis catalysts. Electrocatalyst research so far has focused on crystal rather than
amorphous due to poor conductivity. Here, we demonstrate that the
amorphous electrocatalyst made of 3D honeycomb-like amorphous nickel
hydroxide (NiÂ(OH)<sub>2</sub>) nanosheets synthesized by a simple,
facile, green, and low-cost electrochemistry technique possesses ultrahigh
activity and super-long-term cycle stability in the oxygen evolution
reaction (OER). The amorphous NiÂ(OH)<sub>2</sub> affords a current
density of 10 mA cm<sup>–2</sup> at an overpotential of a mere
0.344 V and a small Tafel slope of 46 mV/dec, while no deactivation
is detected in the CV cycles even up to 5000 times. We also establish
that the short-range order, i.e., nanophase, of amorphous creates
a lot of active sites for OER, which can greatly promote the electrochemical
performance of amorphous catalysts. These findings show that the conventional
understanding of selecting electrocatalysts with conductivity as a
typical reference standard seems out of date for developing new catalysts
at the nanometer, which opens a door ever closed to applications of
amorphous nanomaterials as advanced catalysts for water oxidation
Capillary Electrophoresis–Nanoelectrospray Ionization–Selected Reaction Monitoring Mass Spectrometry via a True Sheathless Metal-Coated Emitter Interface for Robust and High-Sensitivity Sample Quantification
A new sheathless
transient capillary isotachophoresis (CITP)/capillary
zone electrophoresis (CZE)–MS interface, based on a commercially
available capillary with an integrated metal-coated ESI emitter, was
developed in this study aiming at overcoming the reproducibility and
ruggedness problems suffered to a certain degree by almost all the
available CE–MS interfaces, and pushing the CE–MS technology
suitable for routine sample analysis with high sensitivity. The new
CITP/CZE–MS interface allows the electric contact between ESI
voltage power supply and the CE separation liquid by using a conductive
liquid that comes in contact with the metal-coated surface of the
ESI emitter, making it a true sheathless CE–MS interface. Stable
electrospray was established by avoiding the formation of gas bubbles
from electrochemical reaction inside the CE capillary. Crucial operating
parameters, such as sample loading volume, flow rate, and separation
voltage, were systematically evaluated for their effects on both CITP/CZE
separation efficiency and MS detection sensitivity. Around one hundred
CITP/CZE–MS analyses can be easily achieved by using the new
sheathless CITP/CZE interface without a noticeable loss of metal coating
on the ESI emitter surface, or degrading of the ESI emitter performance.
The reproducibility in analyte migration time and quantitative performance
of the new interface was experimentally evaluated to demonstrate a
LOQ below 5 attomole
Adsorption isotherms of La<sup>3+</sup> and Ce<sup>3+</sup> on SA-PGA gel particles.
<p>Adsorption isotherms of La<sup>3+</sup> and Ce<sup>3+</sup> on SA-PGA gel particles.</p
Adsorption of Rare Earths(â…˘) Using an Efficient Sodium Alginate Hydrogel Cross-Linked with Poly-Îł-Glutamate
<div><p>With the exploitation of rare earth ore, more and more REEs came into groundwater. This was a waste of resources and could be harmful to the organisms. This study aimed to find an efficient adsorption material to mitigate the above issue. Through doping sodium alginate (SA) with poly-Îł-glutamate (PGA), an immobilized gel particle material was produced. The composite exhibited excellent capacity for adsorbing rare earth elements (REEs). The amount of La<sup>3+</sup> adsorbed on the SA-PGA gel particles reached approximately 163.93 mg/g compared to the 81.97 mg/g adsorbed on SA alone. The factors that potentially affected the adsorption efficiency of the SA-PGA composite, including the initial concentration of REEs, the adsorbent dosage, and the pH of the solution, were investigated. 15 types of REEs in single and mixed aqueous solutions were used to explore the selective adsorption of REEs on gel particles. Scanning electron microscopy (SEM) and Fourier transform infrared (FT-IR) spectroscopy analyses of the SA and SA-PGA gel beads suggested that the carboxyl groups in the composite might play a key role in the adsorption process and the morphology of SA-PGA changed from the compact structure of SA to a porous structure after doping PGA. The kinetics and thermodynamics of the adsorption of REEs were well fit with the pseudo-second-order equation and the Langmuir adsorption isotherm model, respectively. It appears that SA-PGA is useful for recycling REEs from wastewater.</p></div
Digital photographs of SA gels (a, b, c, d) and SA-PGA gels (e, f, h, i).
<p>Digital photographs of SA gels (a, b, c, d) and SA-PGA gels (e, f, h, i).</p
Effects of the initial concentration of REEs, adsorbent dosage, and pH of solution on the adsorption by gel particles (Adsorption conditions: temperature 30°C; 150 rpm; and 3h adsorption time).
<p>Effects of the initial concentration of REEs, adsorbent dosage, and pH of solution on the adsorption by gel particles (Adsorption conditions: temperature 30°C; 150 rpm; and 3h adsorption time).</p
Adsorption kinetic curves (a) and pseudo-second-order plots (b) for the adsorption by gel particles.
<p>Adsorption kinetic curves (a) and pseudo-second-order plots (b) for the adsorption by gel particles.</p
Regeneration of these two gel particles (Adsorption conditions: 30 ml of 0.05 M hydrochloric acid solution, 30 min, 150 rpm, 30°C).
<p>Regeneration of these two gel particles (Adsorption conditions: 30 ml of 0.05 M hydrochloric acid solution, 30 min, 150 rpm, 30°C).</p
FT-IR spectra of SA, PGA, SA-PGA, SA-PAG-La, and SA-PGA-La-HCl gels.
<p>FT-IR spectra of SA, PGA, SA-PGA, SA-PAG-La, and SA-PGA-La-HCl gels.</p
Assignment of the main vibrational modes.(C<sub>HCl</sub>:0.1mol/L,50mL).
<p>Assignment of the main vibrational modes.(C<sub>HCl</sub>:0.1mol/L,50mL).</p