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For comparative purposes, diverse solids were also obtained by the conventional sol-gel method (P-series).
The effects of the physical characteristics of the solids were also included in the four correlations so proposed.
The surface acid base/redox properties of the solids were also evaluated by using 2-propanol conversion and pyridine chemisorption.
Using the Fourier transform infrared spectrophotometer (FT-IR, Nicolet Nexus 470), all solids were also analyzed in KBr pellets within 4000 400 cm−1.
The obtained solids were also analyzed by X-ray diffraction (XRD) with a SIEMENS D-500 using Cu Kα radiation (1.54056 Å).
Solids were also present in the OA and LC treatments, but in both cases the collected solids re-dissolved in the ethanol used for washing, and could not be subsequently characterized by XRD or SEM.
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The moisture content of the undissolved solids was also determined.
The influence of packing on charge transport in organic solids was also analyzed using Monte Carlo methods[6].
The thermal stability of the solids was also investigated up to 800 °C.
For comparison, the phenomenological Tsai Wu strength criterion for anisotropic solids is also implemented.
A significant generation of water pollution (including BOD, COD, Suspended Solids and Dissolved Solids) is also expected.
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