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The dynamic adsorption process of waste sawdust.
Figure 2d is a typical spectrum of waste sawdust.
Fig. 12 The TG curves of waste sawdust, CPCMs-1-4, and PEG.
Figure 4 shows scanning electron microscope photographs of waste sawdust and CPCMs-1-4.
0.6 g of waste sawdust, CPCMs-1, CPCMs-2, CPCMs-3, and CPCMs-4 and PEG were accurately weighed.
The results clearly indicate that adding PEG into waste sawdust not only can improve the thermal stability of waste sawdust but can also enhance the humidity resistance of the waste sawdust, so its use can be applied in the real world.
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On the basis of the thermal conductivity meter (TCM), the thermal conductivity of the optimal sample increased by 23.8% compared to when there was no expanded graphite in the composites with a mass ratio of PEG to waste sawdust of 4 1.
As shown in Fig. 3a, the steep peak at 26.5° was attributed to the crystal structure of EG. Two distinct steep peaks at about 19.3° and 23.2° were allocated to PEG crystal (Fig. 3b) while 22.2° was assigned to waste sawdust (curve e). Figure 3d displays the characteristic diffraction peaks of PEG and waste sawdust.
Figure 5 presents the SEM photography of CPCMs-4 with EG. Figure 4c distinctly shows the microstructure of the waste sawdust.
An FTIR analysis was used to estimate the chemical structures of the PEG, waste sawdust, and EG. The FTIR spectrums of (a) PEG, (b) CPCMs-4, (c) CPCMs-4 with 5% EG, and (d) waste sawdust are displayed in Fig. 2.
The mass fractions of the PEG, waste sawdust, and EG in these samples are presented in Table 1.
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