“…The values obtained were in line with the values presented in previous studies, namely those by Demirbaş (2002) for almond husks [88], by Torreiro et al (2020) for kiwifruit pruning [89], by San José et al (2013) for vine pruning [90], by Nunes et al (2020) for olive pomace [91], for the pine chip [92], and Sá et al (2020) [93] For the same materials, after being subjected to the heat treatment process by torrefaction, there was an expected increase in the fixed carbon content, as described in several previous works for biomass materials-namely, the works of Faizal et al (2018), Lau et al (2018), and Conag et al (2017) [94][95][96]-with the smallest percentage increase corresponded to the increase seen in vine pruning, which stood at 63.57%, while the remaining materials had an average of 70.51 ± 3.96%. These values were also in line with the values obtained in previous studies, namely those developed by Chiou et al (2018) for almond shells [97], by Margaritis et al (2020) for vine pruning [98], by Volpe et al (2015) for olive pomace [99], Phanphanich and Mani (2011) for pine chip [35], and Sá et al (2020) [93] In the case of kiwifruit pruning, the only works found in the bibliographic research referred to its characterization as a fuel after drying, without any other type of thermal processing such as torrefaction (see, e.g., the works developed by Dyjakon and García-Galindo (2019) or Boumancher et al (2019) [100,101]). With reference to works carried out on the application of thermochemical conversion technologies (in this case, pyrolysis), we found a work developed by Rene et al (2020), which was carried out with the aim of studying the production of biochar from kiwifruit pruning employed as an amendment aiming to evaluate its remediation potential in smelter-and mining-contaminated soils [102]; therefore, the data from this study was not used for comparison, as the methodological assumptions related to sample preparation ...…”