Soil water infiltration rates post wildfire
Data files
Aug 05, 2026 version files 57.09 KB
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Minatre_soil_repellency_data_Oct2025_VR.xlsx
51.38 KB
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README.md
5.70 KB
Abstract
Wildfires can increase soil water repellency (SWR), reducing water infiltration and elevating risks of runoff, erosion, and flooding. This report describes methods and data from a study measuring relative soil water infiltration rates at 10 sites across nine recently burned areas in the Sierra Nevada range of California and Nevada, spanning a chronosequence of fires that occurred between 2015 and 2021. Field measurements, conducted in summer 2022, used a handheld tension infiltrometer to assess relative infiltration at the soil surface and at 3 cm depth along transects located in areas of moderate and high burn severity. In total, 80 individual infiltration measurements were collected per burned area, alongside supporting environmental data including soil moisture, temperature, aspect, slope, and vegetation type. Results show that infiltration rates are consistently lower at depth than at the surface.
Dataset DOI: 10.5061/dryad.1c59zw4cg
Description of the data and file structure
infiltration measurements at each sampling location, volumetric soil water content (%), soil temperature (°C) were measured with a handheld probe (TEROS 11, METER Group, Pullman, WA) at a 1 cm depth. The other environmental variables recorded for each sample location were the aspect, slope, and vegetation type.
Files and variables
File: Minatre_soil_repellency_data_Oct2025_VR.xlsx
Sheet: Tamarack (2021)
Description: This sheet presents the data for the Tamarack 2021 burn area sites.
Variables
| Item | Unit | Descriptor |
|---|---|---|
| Fire Name | Name of fire | |
| Sample ID | Sample identification | |
| Latitude | N | Latitude of sampling location in decimal degree |
| Longitude | W | Longitude of sampling location in decimal degree |
| Soil Burn Severity | Soil burn severity of sampling location, either moderate or high | |
| Aspect | Aspect of sampling location | |
| Slope | degree | Slope of sampling location |
| Depth | cm | Depth of reading, either 1 or 3 cm |
| Start Reading | mL | Start reading of test 1 |
| End Reading | mL | End reading of test 1 after 1 minute |
| Test 1 Volume | mL | Volume of test 1 |
| Start Reading | mL | Start reading of test 2 |
| End Reading | mL | End reading of test 2 after 1 minute |
| Test 2 Volume | mL | Volume of test 2 |
| Start Reading | mL | Start reading of test 3 |
| End Reading | mL | End reading of test 3 after 1 minute |
| Test 3 Volume | mL | Volume of test 3 |
| Start Reading | mL | Start reading of test 4 |
| End Reading | mL | End reading of test 4 after 1 minute |
| Test 4 Volume | mL | Volume of test 4 |
| Mean | mL | Mean of volume for the four tests |
| Strong Repellency 0<3 | *=yes | Strong repellency when mean of volume is 0 to <3 |
| Weak Repellency ≥3 to <8 | *=yes | Weak repellency when mean of volume is ≥3 to <8 |
| No Repellency ≥8 | *=yes | No repellency when mean of volume ≥8 |
| Vegetation | Vegetation type of sampling location | |
| Volumetric Moisture | % | Volumetric moisture of sampling location for 1 cm depth only |
| Temperature | °C | Temperature of sampling location for 1 cm depth only |
| Fire Year | Fire year | |
| Year Analyzed | Year analyzed |
n.m. = not measured. At some points along the transect the 3rd and 4th readings were not conducted and temperature and volumetric moisture was not measured for the 3 cm depth samples.
Sheet: Washington (2015)
Description: This sheet presents the data for the Washington 2015 burn area. See variables description above.
Sheet: Slinkard (2017)
Description: This sheet presents the data for the Slinkard 2017 burn area sites. See variables description above.
Sheet: Dixie west (2021)
Description: This sheet presents the data for the Dixie west 2021 burn area. See variables description above.
Sheet: Loyalton (2020)
Description: This sheet presents the data for the Loyalton 2020 burn area. See variables description above.
Sheet: Little Valley (2016)
Description: This sheet presents the data for the Little Valley 2016 burn area. See variables description above.
Sheet: Dixie east (2021)
Description: This sheet presents the data for the Dixie east 2021 burn area. See variables description above.
Sheet: Beckwourth (2021)
Description: This sheet presents the data for the Beckwourth 2021 burn area. See variables description above.
Sheet: Walker (2019)
Description: This sheet presents the data for the Walker 2019 burn area. See variables description above.
Sheet: Donnell (2018)
Description:This sheet presents the data for the Donnell 2018 burn area. See variables description above.
Study sites
Nine recently burned areas were selected for analysis. One area from each fire was selected for the study except for the Dixie Fire, where two areas were selected, for a total of 10 study sites. All of the burned areas are in the Sierra Nevada range of Nevada and California, and the environmental variables were kept as constant as possible to allow for comparison among the sample locations. The fires occurred from 2015 to 2021, and all field measurements were completed in the summer of 2022.
Two transect sites were selected for each of the 10 study sites: one in a moderate burn severity area and one in a high burn severity area. These sites were selected using burn severity maps.
Infiltration and soil measurements
For both moderate and high burn severity, a 100 m transect was set up (two transects total for each study site). Transects were located within ~50 m of each other to maintain site similarities. Measurements were conducted at 0 m, 10 m, 30 m, 60 m, and 100 m along each transect (n = 5 for each transect, two transects per burned area). At each measurement location, a handheld tension infiltrometer (Mini Disk Infiltrometer, METER Group, Pullman, WA) was used to measure the relative infiltration rate at the surface and at a 3 cm depth. This method measures the amount of water that leaves the infiltrometer through its porous base and enters the soil over one minute at a specific tension (1 cm). For example, when the infiltrometer is placed on a highly water repellant soil, the water surface tension at the bottom of the infiltrometer is not broken and no water infiltrates the soil. The result is a measurement of the relative infiltration in mL min-1 (for the example above, the result would be 0 mL min -1).
The measurement was repeated four times at the soil surface and four times at the 3 cm depth at each of the five locations along the transect. For consistency, any post-fire ash, organic material, or rocks were removed from the surface before measurements were taken. This amounts to 80 individual relative infiltration rate measurements per burned area. The four relative infiltration measurements were averaged for each location along the transect. The results were then classified as either strong water repellency (0 to < 3 mL min -1), weak water repellency (3 to < 8 mL min -1), or no water repellency (≥8 mL min -1).
