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The effects of operational parameters such as mobile phase modifier concentrations, mobile phase flow rate, heating block temperature and drying gas flow rate were evaluated by the 24 − 1 fractional factorial experimental design, resolution IV, in the screening phase and by Doehlert experimental design.
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The responses of these detectors were systematically investigated under changing experimental and instrumental parameters, such as the mobile phase flow-rate, analyte concentration, mobile phase composition, nebulizer temperature, evaporator temperature, evaporator gas flow-rate and instrumental signal filtering after detection.
Modifications in mobile phase concentration, mobile phase volume, mobile phase saturation time, and temperature were examined to check the robustness.
Though the materials typically have very large concentrations of mobile oxygen ion defects, the transition metals impart electron (or hole) conduction that prevents their use as solid electrolytes.
Preliminary separations were performed with standard solution of salmon DNA at different pH values and different NaCl concentrations in mobile phase.
These surprisingly high selectivities cannot be explained by current models of ionic conduction in graphene nanopores, motivating the development of a new model in which elevated concentrations of mobile cations near the graphene surface generate additional ion selectivity.
The process of ion transfer in passivating film on iron containing high concentrations of mobile protons are investigated in acid sulfate solutions by virtue of chronoamperometric, capacity and ellipsometric methods.
The aim of this investigation was to determine the allocation between carbon dioxide concentrations, by mobile measurements at 1.5 m a.g.l., within the urban canopy layer regarding different conditions: anticyclonic and cyclonic weather situations, on weekdays, at different times of the day and in different seasons.
Other explanatory variables (EV) influencing damage include concentrations of mobile homes, often referred to as "trailer parks".
The propagation of oyster mushroom in wheat straw substrate and heavy metal-polluted pyritic mine waste, reduced considerably the concentrations of mobile heavy metals in the waste by 1.2 mg kg−1 (98%); 2.0 mg kg−1 (79%); 13.1 mg kg−1 (93%); 7.7 mg kg−1 (78%); and 6.5 mg kg−1 (88%) for Mn2+; Cr2+; Pb2+; Fe3+; and Cd2+, respectively.
Since etching at the tip of the Si nanostructures can be mainly attributed to metal ion re-nucleation and hole diffusion, this correlation is reasonable as higher [H2O2] values with respect to [HF] lead to greater concentrations of mobile Ag+ ions [15, 17] and injected holes [31, 32].
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