Abstract

While western U.S. wildfires have increased in intensity and scale, their impacts on soil chemical composition and hydraulic processes have received little attention, despite increasing erosion, surface runoff and flooding. The relationships between biomass-burning emissions, composition of the soil, fire heat, and soil water repellency are fragmental and sometimes contradictory. Here, we characterized the water repellency of sand (soil surrogate) exposed to Jeffrey pine duff smoke under controlled laboratory conditions. Water drop penetration time (WDPT), effective contact angle, and relative sorptivity of exposed silica sand (soil surrogate) were determined. Sand samples treated with smoke and heat or with cold smoke showed severe-to-extreme water repellency (WDPT > 1020 s). Sand samples exposed to fulvic acid (surrogate for soil organic matter) showed strong water repellency (WDPT = 81 s) that increased to become severe (WDPT = 2305 s) after subsequent heating to 200 °C for two hours. All sand samples exposed to either fire emissions or fulvic acid showed WDPTs >81 s, effective contact angles between 78° and 87°, and relative sorptivities between 0.31 and 0.49 compared with the untreated sand samples, with a WDPT <0.5 s, effective contact angle of 48°, and relative sorptivity of 1. This indicates that the sorptivity-controlled water infiltration into treated sand is less than half of that into untreated sand.

Highlights

  • The results showed that Fire-induced soil water repellency (FISWR) was caused by the movement of volatile organic compounds (VOCs) from the burning fuel into the soil during the burn

  • Water drop penetration time (WDPT) classification according to Doerr and Shakesby [66] was used to assess the level of soil water repellency (SWR) in the current discussion

  • We investigated how biomass-burning emissions and the heat of and relative sorptivities decreased with the increasing WDPT

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Summary

Introduction

Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations. In the last two decades, the frequency, size, and severity of fires in the western U.S. have increased [1,2,3,4], with dry conifer forests being greatly affected by these fires [5,6,7,8]. In. 2020, the western U.S experienced a series of mega-sized wildfires [9] across California, Oregon, Nevada, and Washington. A hot and dry climate [10,11,12] fueled these recordbreaking fires that burned over 32,000 km , according to a National Interagency Fire

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