“…The high carbon supply provided by the lignocellulosic residues in the studied mixture requires a steady breakdown of structural sugars and lignin to support the microbial metabolism. Correspondingly, most of the abundant identified genera in both the control and the glyphosate treatment (Figure 2) feature members known to have functions in the transformation of lignocellulosic materials such as Thermobifida , Thermobacillus , Microbacterium , Paenibacillus , Bacillus , Cellvibrio , Streptomyces , Saccharomonospora , Devosia , Solibacillus , Ureibacillus , Thermoactinomyces , Thermomonospora , Brevibacillus , Geobacillus , Demequina , Laceyella , Truepera , Thermobispora , Lysinibacillus , Luteimonas and Sphingobacterium which are capable of degrading cellulose, hemicelluloses or both types of structural sugars (Albuquerque et al, 2018; Ali et al, 2019; Han et al, 2018; Huang et al, 2012; Irfan et al, 2018; Liolios et al, 2010; Lykidis et al, 2007; Meng et al, 2009; Mokrane et al, 2016; Morohoshi et al, 2012; Photphisutthiphong & Vatanyoopaisarn, 2019; Rawway et al, 2018; Roberts et al, 1990; Singh et al, 2013; Stutzenberger, 1972; Suarez et al, 2014; Touzel & Prensier, 2015; Wang et al, 2011). Some others, such as Microbacterium , Thermobifida , Brevibacillus , Ureibacillus , Thermomonospora , Pseudomonas , Streptomyces , Sphingobacterium and Pedomicrobium , have the required machinery to degrade lignin (Chen et al, 2015; Hadad et al, 2005; Larsen et al, 1999; Majumdar et al, 2014; Manaia & Moore, 2002; Okuda et al, 2008; Rahmanpour et al, 2016; Stein, 2014; Taylor et al, 2012).…”