A variety of factors including extreme heat, drought, natural climate change, and human-driven processes have driven the occurrence of bush and seasonal fires in Australia (Pitman et al., 2007). The bushfires that occurred during the Australian summer of September 2019 through March 2020 were unprecedented in scope, possibly due to the very dry conditions over the past 2 years throughout eastern Australia due to the absence of a La Nina event (Godfree et al., 2021;King et al., 2020). This particular summer was both the hottest and the driest period recorded on the continent, over the past decade. Bushfires began in September 2019, growing in size over the following months until the heavy rains fell in mid-January and early February of 2020. During that period, roughly 65 million square kilometers, which included more than 21% of Australian forests, were burned during the Australia summer months (Boer et al., 2020).From 2019 to 2020, the vegetation changes caused by drought and fire in Australia have caused major changes in the distribution of evaporation flux and runoff flux. In areas once covered by vegetation, fires that burn vegetation cause changes in the runoff of surface water, the transpiration of vegetation, and evapotranspiration of the soil (Atchley et al., 2018;Ma et al., 2020), subsequently affecting the surface soil moisture (SSM) (Gould et al., 2016;Saksa et al., 2020). In areas with bare soil, the high temperatures brought by fires increase the water evaporation present in bare soil, resulting in decreases in SSM (Poon & Kinoshita, 2018). Previous studies of dynamic changes in vegetation growth and SSM due to fires have typically been divided into study areas according to various vegetation communities and soil texture types. Designed multiple experimental plots and control groups