As the production of soybeans has increased, the resulting byproducts of soybeans generated during its processing have also increased. In general, 1 ton of soybean residues (at 10% moisture content) are generated with 820 kg of soybean (30 bushels) production, which is lower than corn or grain sorghum (40 bushels, 1,090 kg) but higher than wheat (20 bushels, 545 kg) (Wortmann et al., 2012). Some soybean straw is potentially utilized as agricultural fertilizer, animal feedstock, and energy resource for rural energy; however high lignin (>20% w/w in straw) and anti-nutritional components in waste restrict their direct use. For better utilization of soybean wastes, an efficient pretreatment step is required to alleviate biomass recalcitrance because of the complex crystalline structure between cellulose-hemicellulose-lignin in the lignocellulosic biomass, including soybean straw (Kim et al., 2022, 2018). It is well-established that a pretreatment process can facilitate biomass saccharification by solubilizing hemicellulose and/or lignin and disrupting the crystalline structure of cellulose (Cao et al., 2015; Kim et al., 2016). Previous studies with different pretreatments such as supercritical water (Vedovatto et al., 2021), ball milling (Liu et al., 2016), and alkaline and acid pretreatments (Qing et al., 2017) were shown to disrupt the crystalline structure of soybean straw and enhance its enzymatic hydrolysis. Unutilized soybean residuals are often discarded/burned onto land or water which causes environmental issues with their high biochemical oxygen demand and toxic compounds; therefore, effective utilization of these residues is required (Liu et al., 2015).