the Creative Commons Attribution 4.0 License.
the Creative Commons Attribution 4.0 License.
Evaluating L-band InSAR snow water equivalent retrievals with repeat ground-penetrating radar and terrestrial lidar surveys in northern Colorado
Randall Bonnell
Daniel McGrath
Jack Tarricone
Hans-Peter Marshall
Ella Bump
Caroline Duncan
Stephanie Kampf
Yunling Lou
Alex Olsen-Mikitowicz
Megan Sears
Keith Williams
Lucas Zeller
Yang Zheng
Snow provides critical water resources for billions of people, making the remote sensing of snow water equivalent (SWE) a highly prioritized endeavor, particularly given ongoing climate change impacts. Synthetic aperture radar (SAR) is a promising method for remote sensing of SWE because radar penetrates snow, and SAR interferometry (InSAR) can be used to estimate changes in SWE (ΔSWE) between SAR acquisitions. We calculated ΔSWE retrievals from 10 NASA L-band (1–2 GHz, ∼25 cm wavelength) uninhabited aerial vehicle SAR (UAVSAR) acquisitions covering a ∼640 km2 swath in northern Colorado during the winters of 2020 and 2021. UAVSAR acquisitions coincided with ∼117 mm of accumulation in 2020 and ∼282 mm of accumulation in 2021. ΔSWE retrievals were evaluated against measurements of SWE from repeat ground-penetrating radar (GPR) and terrestrial lidar scans (TLSs) collected during the NASA SnowEx time series campaigns at two field sites (total area km2) as well as SWE measurements from seven automated stations distributed throughout the UAVSAR swath. For single InSAR pairs, UAVSAR ΔSWE retrievals yielded an overall r of 0.72–0.79 and an RMSE of 19–22 mm when compared with TLS and GPR ΔSWE retrievals. UAVSAR ΔSWE showed some scatter with ΔSWE measured at automated stations for both study years, but cumulative UAVSAR SWE yielded a r of 0.92 and an RMSE of 42 mm when compared to total SWE measured by the stations. Further, UAVSAR ΔSWE RMSEs differed by <10 mm for coherences (i.e., the complex interferometric coherence) of 0.10 to 0.90, suggesting that coherence has only a small influence on the ΔSWE retrieval accuracy. Given the evaluations presented here and in other recent studies, the upcoming NASA-ISRO SAR (NISAR) satellite mission, with a 12 d revisit period, offers an exciting opportunity to apply this methodology globally.
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In snow-dominated watersheds, melt from seasonal snow drives streamflow and groundwater recharge (Li et al., 2017; Lorenzi et al., 2024). Globally, snowmelt supplies water resources for more than one-sixth of the population (Barnett et al., 2005). However, warming temperatures are decreasing the probability of snowfall in historically snow-dominated watersheds (Klos et al., 2014; McCrystall et al., 2021), shifting snowpacks to higher elevations and more poleward latitudes, effectively decreasing the predictability of streamflow in these basins (Siirila-Woodburn et al., 2021). Mountains store a disproportionately large amount of snow despite comprising a small fraction of the global land surface (Wrzesien et al., 2019). Yet, in the mountains of the western United States, climate change has driven a 15 %–30 % decline in snow water equivalent (SWE), the defining snowpack hydrologic variable, and SWE is expected to decline by an additional 25 % by 2050 (Mote et al., 2018; Siirila-Woodburn et al., 2021). The projected changes are acute globally: by 2100, snowmelt is projected to decline in the European Alps by 50 % (Moraga et al., 2021), while basins in the Himalayas may see snowfall declines of 30 %–70 % for the warmest climate scenarios (Viste and Sorteberg, 2015). Although snowpack monitoring via automated stations exists in some countries (e.g., SNOTEL stations in the United States; Fleming et al., 2023), location bias, limited elevational range, and large spatial variability in snow over short length scales result in an incomplete characterization of this resource (Dozier et al., 2016). Thus, satellite remote sensing methods for snowpack monitoring at high resolution (<500 m, < weekly) have been set as a high priority for study and development by the National Academies of Sciences, Engineering, and Medicine (National Academies of Sciences, Engineering, and Medicine, 2018).
The remote sensing of SWE is challenged by environmental factors (i.e., topography, vegetation) and by the spatiotemporally varying physical parameters of the snowpack (i.e., SWE, density, liquid water content, snow grain size). The NASA SnowEx campaigns were conducted from 2017–2023 in the western United States to evaluate and develop remote sensing methods for snowpack monitoring, with the retrieval of SWE set as a primary goal (Durand et al., 2018). SWE is calculated as the product of snow depth and snow density, and there are two primary groups of techniques for remote sensing of SWE at high spatial resolutions (<500 m): (i) depth-based optical–infrared methods and (ii) radar-based methods. Depth-based optical–infrared methods (e.g., stereo satellite imagery, lidar) require cloud-free conditions and derive snow depths by differencing a snow-off digital elevation model (DEM) from a snow-on DEM (Currier et al., 2019; Hu et al., 2023). Snow density model estimates or in situ measurements are required to convert the snow depths to SWE (e.g., Hedrick et al., 2018), which adds to the uncertainty of this technique (Raleigh and Small, 2017). Both satellite lidar (e.g., Besso et al., 2024) and very-high-resolution stereo satellite imagery (e.g., Hu et al., 2023) are being explored as depth-based methods for the remote sensing of SWE. Radar approaches are distinct from depth-based approaches because the radar signal penetrates the snowpack. Satellite radar approaches for snow depth and SWE retrievals are implemented from synthetic aperture radar (SAR) platforms, and the techniques for snow depth and SWE remote sensing are primarily grouped into backscatter approaches, which use the amplitude component of the radar signal to derive snow depth and/or SWE, and time-of-flight approaches, which derive SWE from the signal path length and include SAR interferometry (InSAR). A third approach, which uses the co-polar phase difference, has also been tested. Readers interested in the co-polar phase difference methodology are referred to Leinss et al. (2014) and Patil et al. (2020).
Unlike optical–infrared methods, SAR approaches for snow remote sensing are not limited by cloud cover, primarily due to low atmospheric absorption at radar frequencies (Woodhouse, 2017). For SAR backscatter approaches, the radar signal is transmitted through the snowpack, and the signal is backscattered to the sensor via volume scattering from snow grains and rough scattering from the snow–ground interface (Tsang et al., 2022). Early backscatter work found that combined X-band (8–12 GHz, ∼3 cm wavelength) and C-band (4–8 GHz, ∼5 cm wavelength) SAR acquisitions were capable of measuring snow depths from 0.5–2.5 m (RMSE =0.34 m; Shi and Dozier, 2000). More recent efforts have emphasized combined X-band and Ku-band (12–18 GHz, ∼1.8 cm wavelength) SARs; these backscatter approaches are promising methods for measuring SWE in shallow snowpacks (<150 mm; Tsang et al., 2022), with the potential for retrieving SWE in deeper conditions (Borah et al., 2023). C-band backscatter approaches are capable of measuring snow depths in deeper snowpacks (>1 m), albeit with higher uncertainty (Lievens et al., 2019, 2022). Backscatter approaches have known uncertainties in wet snow conditions, at large incidence angles, and in forests (Lievens et al., 2022; Tsang et al., 2022). InSAR is a unique method for retrieving SWE because the interferometric phase change has a near-linear relation to SWE change (Guneriussen et al., 2001). In dry snow, this characteristic can be used to retrieve changes in SWE without a priori information on snowpack density with an estimated 7 % uncertainty related to the linear approximation (Leinss et al., 2015). Applying the InSAR technique at low frequency (e.g., L-band, ∼25 cm wavelength) limits interaction between the radar signal and snow grains, increases the signal penetration in forests and in wet snow (Naderpour et al., 2022), and promotes increased coherence (described below) over longer temporal baselines (Ruiz et al., 2022). A review of the transmissibility of L-band radar in snow is provided in Appendix A1. With the upcoming launches of L-band SAR satellites, such as the NASA-ISRO SAR satellite (NISAR), the Radar Observing System for Europe satellite (ROSE-L), and the Tandem-L Interferometric Radar Mission, radar products will be publicly available at high spatial and temporal resolution across the globe (NISAR: 80 m spatial resolution, 12 d repeat; ISRO Space Applications Centre, 2023).
InSAR is a change detection method that measures the phase change between repeat SAR acquisitions and relies upon a coherent reflection from the snow–ground interface (Appendix A2; Guneriussen et al., 2001). The InSAR SWE retrieval technique was first established at the C-band from the European Remote-Sensing Satellite (ERS) platform at a field site in Norway. The study showed that snowfall could be mistaken as a deformation signal in interferograms (i.e., the interferometric phase change data product; Guneriussen et al., 2001). Deeb et al. (2011) applied this technique to the ERS using repeat acquisitions over the North Slope of Alaska, United States, to measure changes in SWE (ΔSWE), revealing ΔSWE spatial patterns that were correlated with the prevailing wind direction. Since then, the technique has been tested for multi-year, season-long ΔSWE retrievals from tower-mounted platforms in Finland at Ku-, X-, C-, and L-band frequencies (Leinss et al., 2015; Ruiz et al., 2022), by several studies emphasizing one or two interferometric pairs (Conde et al., 2019; Marshall et al., 2021; Nagler et al., 2022; Palomaki and Sproles, 2023; Tarricone et al., 2023) and by two season-long studies that used a time series of interferometric pairs (Hoppinen et al., 2024; Oveisgharan et al., 2024). In general, these studies have found that InSAR ΔSWE retrievals are highly correlated with in situ measurements, but accuracy has varied on a case-by-case basis, and in situ measurements for validation have been limited to point-based measurements that likely do not capture the spatial complexity of the snowpack. Additionally, only three of these studies have considered atmospheric signal delays, which represent a source of uncertainty because changes in atmospheric pressure and water content can further affect the ΔSWE retrieval accuracy (Gong et al., 2013).
We use the term coherence to refer to the complex interferometric coherence; it is a measure of the similarity of the backscattered radar signal properties between two acquisitions (Woodhouse, 2017). Coherence is considered an index for confidence in phase change measurements. Typically, phase changes with higher coherences are considered more accurate, and coherence must be maintained for the accurate unwrapping of interferograms. Coherence is affected by forest cover, changes in soil conditions (e.g., soil moisture changes or freeze–thaw changes), changes in the dielectric permittivity of the snowpack (e.g., melt–refreeze cycles), snow metamorphism (Brangers et al., 2024), and significant snow accumulation or ablation events (Ruiz et al., 2022). Collectively, these factors indicate that as the temporal baseline (i.e., time interval) between interferometric pairs is extended and/or major snowpack changes occur, coherence will degrade (Deeb et al., 2011), particularly at higher frequencies (Ruiz et al., 2022). A review of the calculation of coherence is provided in Appendix A2.
Here, we calculated ΔSWE retrievals from 10 L-band NASA uninhabited aerial vehicle SAR (UAVSAR; Rosen et al., 2006) InSAR pairs collected during the NASA SnowEx time series campaigns in 2020 and 2021 over north-central Colorado. During UAVSAR acquisitions, we collected spatially distributed ground-penetrating radar (GPR) at a very similar frequency to UAVSAR (UAVSAR =1.26 GHz, GPR =1.0 GHz) for all InSAR pairs, and we performed terrestrial lidar scans (TLSs) for two InSAR pairs. Our study examines three components of InSAR ΔSWE retrievals. First, we leveraged our ground observations to evaluate the accuracy of the L-band InSAR technique for ΔSWE retrievals for two accumulation seasons in a dry continental subalpine snowpack. We then evaluated UAVSAR ΔSWE retrieval errors against coherence to examine it as a potential metric for ΔSWE retrieval accuracy. Finally, UAVSAR ΔSWE retrievals are summed across each individual winter season and compared with total SWE measured at seven automated stations to evaluate the accuracy of the technique across a time series.
The SnowEx 2020 time series campaign was originally planned for a single season at 13 field sites (Marshall et al., 2019), but it was cut short due to the COVID-19 pandemic and subsequently restarted in 2021 at seven field sites. Weekly to biweekly surveys were performed at Cameron Pass, Colorado (Fig. 1a), coinciding with UAVSAR flights (Table 1). The flight line was typically ∼40 km in length with a swath width of 16 km, but deviations from the spatial baseline and poor GNSS accuracy caused data acquisitions to be shortened for a few dates. The primary flight heading was southeast (141°), with a secondary northwest heading (321°) flown when time allowed. For the analysis, we used the 141° heading for all InSAR pairs except the 27 January to 3 February 2021 interval, which used the 321° heading.
The region has a continental snow climate (e.g., Trujillo and Molotch, 2014), with a prairie snowpack at lower elevation (<2800 m) within the North Park region and montane and alpine snowpacks in the higher-elevation Medicine Bow Mountains and Never Summer Range. Four SNOTEL stations and three automated stations that measured snow depth were located within the flight line (Fig. 1a). The Joe Wright SNOTEL station, which was within 1.5 km of our field sites, receives a median peak SWE of 632 mm that occurs on a median date of 5 May (1979–2023). Vegetation within the flight line primarily consists of evergreen forest (58 %) and shrubs (32 %; Buchhorn et al., 2020). Englemann spruce (Picea engelmannii), subalpine fir (Abies lasiocarpa), and lodgepole pine (Pinus contorta) are the primary constituents of the forest, with interspersed aspen (Populus tremuloides) groves (Fassnacht et al., 2018). From August to November 2020, the Cameron Peak fire burned >80 km2 of the flight line, including the Cameron Peak field site region (CP; Fig. 1a; McGrath et al., 2023), which is not accounted for in these land cover estimates.
During SnowEx 2020, we surveyed the Michigan River field site (MR; Fig. 1b), located in mostly open meadows vegetated by willows and grasses, though spruce–fir forests with <70 % canopy cover inhabited portions of the northern and southern extent of the GPR transects. We measured stratigraphy, density, snow depth, and snow temperature in two snow pits (MR1, MR2; Fig. 1b), following the SnowEx methodology outlined by Mason et al. (2023). Interval boards, which captured snow accumulation between surveys, were installed within 10 m of MR1 and at the nearby Joe Wright SNOTEL station. We recorded new snow depth, SWE, and density at each interval board on each site visit. Repeat GPR surveys (∼1.6 km in length; McGrath et al., 2021) were performed using a Sensors & Software pulseEKKO 1.0 GHz GPR coupled to the snow surface via a sled and pulled behind and to the side of a snowshoer. Snow depths were probed every ∼3 m along the GPR transect. Two snow-on terrestrial lidar scans were performed on 26 February and 12 March 2020, in addition to a snow-off UAV-borne lidar scan performed in August 2020 (Williams, 2021).
For SnowEx 2021, we expanded our surveys to include the Cameron Peak field site (CP; Fig. 1c). At MR, GPR surveys (0.8 km in length; Bonnell et al., 2022) were altered to form a loop around the primary meadow, with a co-located snow pit (MR1) and interval board. Snow pits and interval boards were surveyed following the SnowEx methodology. Snow depths were manually probed along the eastern portion of the GPR transect at ∼5 m intervals. We expanded to CP to leverage the reduced vegetation due to the Cameron Peak fire. CP has severely burned spruce–fir forest to the north and east, with an unburned stand in the central to southern portion (Fig. 1c). A single snow pit and interval board was surveyed near the GPR transect (1.6 km in length) in the burned section. Snow depths were probed every ∼5 m along the southeastern GPR transect, with ∼200 m in the forest and ∼200 m in the burned area. An automated station was installed near the CP snow pit, which measured snow depth, wind speed and direction, radiation, temperature, and soil moisture. Two snow-on terrestrial lidar scans were performed at both field sites on 10 February and 24 February 2021, with a snow-off terrestrial lidar scan performed on 27 May 2021 at CP (Williams, 2021).
3.1 UAVSAR processing
Here, we provide an overview of the key UAVSAR processing steps. For additional and more detailed information, we direct readers to Appendix A1–A2. During the 2020 and 2021 airborne campaigns, UAVSAR deployed a fully polarized L-band (1.26 GHz center frequency, 0.24 m wavelength), 80 MHz bandwidth, left-looking InSAR. The instrument was flown at an altitude of ∼12 500 m and acquired data along a ∼40 km stretch with a 16 km swath width (area km2; Fig. 1a; NASA UAVSAR, 2023). In 2020, overpasses were performed with a temporal baseline of 7 d for the first three acquisitions (12, 19, and 26 February) and 15 d for the final acquisition (12 March). In 2021, overpasses had varying temporal baselines (typically 5 to 8 d); due to other aircraft commitments, one acquisition had a longer baseline (20 d for 3–23 February). Poor coherence prevented phase unwrapping at the field sites for one InSAR pair (10–16 March 2021). The UAVSAR team at the NASA Jet Propulsion Laboratory processed the UAVSAR data and generated geocoded amplitude, interferogram, unwrapped interferogram, and coherence products at ∼5 m spatial resolution. We accessed the products from the Alaska Satellite Facility (ASF; NASA UAVSAR, 2020, 2021) and converted the products to GeoTIFFs using uavsar_pytools (Hoppinen and Tarricone, 2022). InSAR measures phase deformation within a single ±π rad phase cycle, which equates to about ±108 mm SWE. Interferograms where ΔSWE exceeded a full phase cycle for some pixels require unwrapping for the accurate estimation of ΔSWE. Therefore, we focused on the unwrapped interferogram and coherence products and outline key workflow steps for calculating ΔSWE, rather than total SWE, in Fig. 2. Although we included all four polarizations, we present the horizontal-transmit and horizontal-receive polarization (HH) for all intervals except the 3–23 February 2021 interval, which used the vertical-transmit and horizontal-receive polarization (VH) due to incomplete phase unwrapping in the HH data product. Detailed radar SWE retrieval methodology is outlined in Appendix A2.
We tested for atmospheric delays following methods developed by Tarricone et al. (2023). We identified snow-free pixels in the unwrapped interferograms using the normalized difference snow index (NDSI; Dozier, 1989) calculated from Sentinel-2 imagery (Fig. S1; European Space Agency, 2022) and regressed snow-free unwrapped phase pixels against the corresponding signal path lengths. Importantly, this method assumes that snow-free pixels are not undergoing any physical changes that would lead to a phase change. We tested whether an atmospheric correction was needed using the three criteria outlined in Appendix A2.2. Importantly, no unwrapped interferograms met all three criteria (Table S1). Therefore, we conclude that stratified atmospheric artifacts are either limited for all interferometric pairs or were more complicated than what our linear model identified. See Appendix A2.2 for a more detailed description of the atmospheric correction.
For these flights, UAVSAR had average look angles of 26–70° from the near to far range. We calculated incidence angles in uavsar_pytools (Eq. A4; Hoppinen and Tarricone, 2022) from the Copernicus 30 m DEM (rescaled to the UAVSAR grid) and the UAVSAR-provided look vector. The Copernicus DEM was chosen because it is the primary DEM used within the processing flow of ASF HyP3 and will be the basis for NISAR interferometric products. We evaluated incidence angles derived from the Copernicus DEM and the ΔSWE retrieval uncertainty caused by these incidence angles in Appendix A2.5.
UAVSAR acquisitions were collected during the winter over relatively short temporal baselines (<21 d). Therefore, we consider changes at the snowpack surface to be the primary driver of phase deformation in the unwrapped interferograms, but we provide a discussion of other potential sources of phase deformation in Appendix A2.1. Changes at the snow surface may include new snow accumulation, sublimation, redistribution, or melt. For both study periods, we conclude that the snowpack is dry, based on results presented in Sect. 4.1. Thus, for ΔSWE retrievals, we consider only the density of snow that accumulated between UAVSAR acquisitions. Surface densities were estimated by averaging density measurements of the snow that accumulated on the interval boards between UAVSAR acquisitions (Sect. 3.2). For instances where snow accumulation had occurred but had been removed from the interval board by, for example, wind redistribution, we used an average of the uppermost 10 cm of the snow pit-measured densities. For each interferometric pair, we converted surface densities to relative permittivity (Eq. A5). Relative permittivities, unwrapped phase, and incidence angles were then used to calculate snow depth changes (Eq. A6), which were subsequently converted to ΔSWE using the surface snow density (Eq. A7). Because the InSAR phase is relative (Woodhouse, 2017), we estimated the absolute phase as the median difference between a 20 % set of randomly selected GPR ΔSWE retrievals (Sect. 3.2) and coincident UAVSAR ΔSWE retrievals for each interval. The median differences were then subtracted from the UAVSAR ΔSWE retrievals for each interval, and the 20 % of the GPR observations used in this step were removed from subsequent analyses. Finally, we supplemented our analysis by evaluating an InSAR ΔSWE retrieval method that approximates ΔSWE from the InSAR phase change and the incidence angle (Leinss et al., 2015) and is thus independent of snow density and relative permittivity measurements. The methods and results of this analysis are reviewed in Appendix A2.4.
UAVSAR coherence values from corresponding TLS and GPR pixels were used to evaluate coherence as a measure of noise for ΔSWE retrievals. Coincident GPR and UAVSAR ΔSWE retrievals were binned by coherence, and the root mean square error (RMSE) of the UAVSAR ΔSWE retrievals was calculated for each bin. The effect of temporal baseline upon coherence and UAVSAR ΔSWE retrieval accuracy was then evaluated by calculating the median coherence and RMSE for UAVSAR ΔSWE retrievals across all temporal baselines used in this analysis.
3.2 Processing ground-based measurements
3.2.1 In situ measurements
Key in situ measurements included snow pit temperatures, pit-measured densities, pit-measured depths, interval board densities and SWE, and manually probed depths. Pit-measured temperatures were used to detect the possible presence of liquid water within the snowpack. Pit-measured densities were averaged to estimate bulk density, which was used in SWE calculations for the snow pits, GPR, TLSs, and probed depths. Interval board densities were used for ΔSWE calculations in the UAVSAR workflow. However, for some dates, the interval boards yielded little to no accumulation due to wind redistribution or a lack of precipitation. For these dates, the pit-measured densities from the upper 0.10 m of the snowpack were averaged and used in the UAVSAR workflow. Probed depths were not repeated in identical locations but were geocoded using a Geode GNS2 receiver mounted on top of the probe and converted to SWE using the bulk snow densities. Because the probed depths had a sampling of 1–2 measurements per UAVSAR pixel and were not collected in repeated locations, we used the depth probe dataset to evaluate the GPR and TLS SWE accuracy, rather than evaluating the UAVSAR ΔSWE retrievals directly.
3.2.2 GPR
GPR locations were collected via an Emlid RS2 GNSS receiver on board the GPR sled and post-processed with an Emlid base station located at the MR field site to ensure a spatial accuracy of <0.25 m. High accuracy is important, given that these transects were repeated and the product of interest is ΔSWE, which is sensitive to geolocation errors. Radargrams were processed in ReflexW (Sandmeier, 2019) in four general steps: (1) application of a time-varying time-zero correction, (2) one-dimensional de-wow filter to remove low-frequency noise, (3) trace interpolation to ∼0.10 m, and (4) two-dimensional filter to remove instrument noise. After processing the radargrams, the ground reflector, identified as the highest-magnitude positive-amplitude reflector at depth, was picked; its corresponding two-way travel time (twt), representing the time-of-flight through the snowpack, was exported. Further GPR collection and radargram processing details are presented in McGrath et al. (2021) and Bonnell et al. (2022). Bulk snow density was then estimated as the average bulk density between available snow pits and used to estimate bulk relative permittivity (Eq. A5) and, thereby, the velocity of the radar signal (Eq. A9). Using the estimated velocity, we converted twt to SWE (Eqs. A10, A7). A detailed summary of the GPR theory and methods is provided in Appendix A3. We evaluated the accuracy of GPR SWE retrievals through a comparison with SWE from probed depths by calculating the median GPR SWE retrieval within a 1.5 m radius around each probed depth. GPR SWE retrievals were then binned at the spatial resolution of the UAVSAR grid by taking the median value of all points within each grid cell. SWE retrievals from corresponding dates were then differenced to generate GPR ΔSWE. The GPR workflow is summarized in Fig. 2.
3.2.3 Lidar scans
Repeat snow-on terrestrial lidar scans were performed in 2020 on 26 February and 12 March at the MR site and in 2021 on 10 and 24 February at the MR and CP sites. Snow-off lidar scans include a UAV-borne lidar scan that was performed for the MR site in August 2020 and a terrestrial lidar scan performed for the CP site on 27 May 2021. Terrestrial lidar scans were aligned and georeferenced by UNAVCO, Inc. (Williams, 2021). The USGS processed a bare-earth digital elevation model (DEM) from the UAV-borne lidar scan (Bauer et al., 2023). Lidar point clouds were reprojected, and surface or bare ground returns were classified. These points were then converted to rasters, gridded, and aligned to the UAVSAR grid, using the average elevation value per pixel. We derived snow depths for each snow-on scan date by subtracting snow-free rasters from snow-on rasters. Snow depth rasters were converted to SWE using the bulk density from the snow pits. ΔSWE was calculated for 26 February to 12 March 2020 and for 10–24 February 2021 by differencing the corresponding SWE rasters. To align TLS datasets with the 3–23 February 2021 InSAR pair, we subtracted the SWE measured on the interval board between 2–10 February 2021 from the UAVSAR ΔSWE retrievals. TLS ΔSWE was then directly compared with the UAVSAR ΔSWE retrievals. The terrestrial lidar workflow is summarized in Fig. 2.
3.3 Comparison between UAVSAR and automated stations
We obtained daily observations of snow depth, SWE, and air temperature from the Joe Wright SNOTEL station (ID 551) and daily observations of SWE from an additional three SNOTEL stations within the UAVSAR swath for the 2020 and 2021 seasons (Fig. 1a; Table S2). Daily snow depths were obtained from three automated stations (two with sonic sensors and one with a snow stake paired with a time-lapse camera) within 4.5 km of the Joe Wright SNOTEL station (Table S2). We converted the snow depths to SWE by calculating density from Joe Wright SNOTEL station measurements of SWE and snow depth. SWE estimates were then smoothed with a 5 d moving median filter to reduce the effects of new snow settlement.
We expanded our UAVSAR analysis beyond our relatively small field sites (∼0.2 km2 total area) to include measurements from the four SNOTEL stations and three automated stations within the swath (Table S2). We calculated the median UAVSAR ΔSWE within a 3×3 pixel grid (∼ 15 m × ∼15 m) around each station, added the ΔSWE retrievals for each interval, and matched the ΔSWE time series to the station time series by adding the station's SWE at the start of the UAVSAR flights to the UAVSAR ΔSWE time series. Because of spatially extensive missing data within the 10–16 March 2021 interferometric pair, we adjusted the UAVSAR ΔSWE time series at each station with the ΔSWE measured by the station. Median coherence was calculated within each 3×3 grid for the SNOTEL stations to evaluate the effects of coherence on the ΔSWE retrieval time series. Lastly, station-measured SWE was compared with cumulative InSAR SWE for the final dates of the 2020 and 2021 UAVSAR acquisitions.
4.1 Field observations of SWE and snow density
UAVSAR flights coincided with 117 mm of SWE accumulation (18 % of peak SWE; Fig. 3a) during the 2020 campaign (4 weeks) and 282 mm of accumulation (48 % of peak SWE; Fig. 3b) during the 2021 campaign (9 weeks). SWE at the in situ interval boards increased on average by 34±12 mm and 31±29 mm per flight interval during the 2020 and 2021 campaigns, indicating that ΔSWE at the field sites was likely within a full phase cycle (±108 mm; Appendix A2.3) for most UAVSAR acquisitions. New snow density, used for UAVSAR ΔSWE calculations, ranged between 106 and 145 kg m−3 across all study dates in 2020 (Fig. 3c) and over a larger range, 118–219 kg m−3, in 2021 (Fig. 3d). Bulk density, used for GPR and TLS SWE calculations, increased minimally between most flights (mean kg m−3; Fig. 3c–d), with a notable exception being the 12–19 February 2020 pair (mean kg m−3).
Surface melting can lead to significant decorrelation of the radar signal and cause increased uncertainty in the ΔSWE retrievals. There were three notable warm periods during the campaigns (7–9 March 2020, 2–10 March 2021, and 21–22 March 2021), but median snow pit temperatures during our survey dates remained °C (Fig. 3e–f). We did observe near-surface melt–freeze crusts in the snow pits during certain surveys, but our observations suggest that liquid water content was absent or minimal during UAVSAR flight times (Table 1) at our study sites throughout the campaigns.
GPR SWE retrievals from the 2020 MR field site showed that median SWE increased by 127 mm between 12 February and 11 March (Fig. 4a), with the largest median ΔSWE occurring during the 12–19 February interval (+99 mm). The 2021 MR (Fig. 4b) and CP (Fig. 4c) field sites showed similar dynamic ranges, with GPR SWE retrievals increasing by 249 mm at the MR site and 233 mm at the CP site between 15 January and 22 March. For both sites, the largest median ΔSWE occurred during the 2–24 February interval (MR mm, CP mm). GPR SWE retrievals and SWE converted from depth probe measurements are highly correlated, with an overall Pearson's correlation coefficient (r) of 0.97 and an overall RMSE of 35 mm (Fig. S2).
4.2 UAVSAR ΔSWE retrievals at the field sites
UAVSAR ΔSWE retrievals along the GPR transect at the 2020 MR field site saw a mean cumulative increase of 40 mm for the three intervals (Fig. 5c–e; Table S3). The largest median ΔSWE occurred during the 12–19 February interval (median mm), with modest SWE increases observed for both the 19–26 February (median mm) and 26 February to 12 March (median mm) intervals. The largest ΔSWE retrieval range was observed for the 12–19 February interval (minimum mm, maximum mm). The expanded 2.7 km × 3.6 km region around the MR site reveals a somewhat different pattern than ΔSWE retrievals along the transect, with less accumulation for 12–19 February (+67 mm) and negligible SWE changes for 19–26 February (0 mm) and 26 February to 12 March (+1 mm; Fig. 5c–e).
UAVSAR ΔSWE retrievals along the GPR transects at the 2021 MR field site saw a median cumulative increase of 104 mm for six of the seven 2021 intervals (no data for 3–23 February 2021), whereas the median cumulative increase for the expanded 2.7 km × 3.6 km region was +143 mm (Fig. 5f–l). At the CP site, the median cumulative SWE across the seven surveys was 203 mm along the GPR transect and 171 mm from the 2.2 km × 3 km expanded region around the CP field site (Fig. 6c–i). The largest median ΔSWE for the expanded regions occurred during the 3–23 February interval (MR median mm, CP median mm). Minimum UAVSAR ΔSWE retrieval medians from the expanded regions were observed from 27 January to 3 February at CP (median ΔSWE mm) and 3–10 March at MR (median ΔSWE mm).
UAVSAR ΔSWE retrievals appear to capture detailed spatial distributions of ΔSWE across all dates at each field site. In particular, larger SWE accumulation is observed in the open meadows and avalanche paths in the MR study area than in the surrounding forests (mean difference =66 %, range of mean differences to +29 mm; Fig. 5). These patterns are particularly noticeable at the MR site for the 12–19 February 2020 interval (Fig. 5c), which recorded a median ΔSWE increase of +98 mm in open meadows and avalanche paths, whereas ΔSWE in the surrounding forests increased by a median of +69 mm. A similar spatial pattern exists at the CP site, as the burned area consistently recorded a larger ΔSWE than adjacent unburned forests. This is best observed in the 20–27 January 2021 interval (Fig. 6d). During this interval, we calculated an average of 31 mm ΔSWE in the burned area and 15 mm ΔSWE in the unburned forests. Median coherence across the time series is somewhat higher for unforested areas in both the MR and CP field sites (+0.05; Figs. 5b, 6b). This subtle difference is further illustrated within the CP field site, where median coherence of the 7 d baseline InSAR pairs increased from 0.56 in 2020 pre-burned forests to 0.60 in 2021 post-burned areas ().
4.3 Evaluating UAVSAR ΔSWE retrievals with GPR
UAVSAR ΔSWE retrievals have a relatively low pixelwise correlation with GPR ΔSWE retrievals for any single InSAR pair ( to 0.20; Table S4). However, compiling the measurements across all surveys increases the ΔSWE dynamic range and correlation substantially (r=0.79; Fig. 7a). Here, we present a time series that includes only InSAR pairs from the HH polarization for all dates except the 3–23 February 2021 pair, which is represented by the VH polarization. For this time series, we observe RMSEs from 16–34 mm (Table S4) for single InSAR pairs, with an overall RMSE =22 mm (Fig. 7a). Although pixelwise comparisons between UAVSAR and GPR ΔSWE retrievals exhibit scatter, the box plot distributions for ΔSWE at co-located GPR–UAVSAR pixels are nearly identical, yielding absolute median differences between median GPR ΔSWE and median UAVSAR ΔSWE of 0–4 mm (Fig. 7b, c; Table S2). Although we primarily present analyses based on the HH polarization, we find that UAVSAR ΔSWE retrievals have nearly equivalent RMSE values across all four polarizations (RMSE =19–22 mm; Table S4).
We explored the possibility of coherence as an error metric for UAVSAR ΔSWE retrievals and found that RMSE exhibited a narrow range (21–25 mm) for coherence bins between 0.1 and 0.7 (Fig. 8a). However, the RMSE at very low coherence (0.0–0.1) is double the RMSE at very high coherence (0.9–1.0). Average coherence was highest for ∼ weekly baselines, but average coherence for the 15 d baseline (0.51) was within the range of average coherence for the 5-to-8 d temporal baselines (Fig. 8b). Of note, the 20 d baseline had average coherence >0.40 (Fig. 7d) but yielded the highest RMSE (33 mm; Fig. 8b).
4.4 Evaluating UAVSAR ΔSWE retrievals with TLSs
TLS ΔSWE retrievals had median values of +9 mm for the MR field site during the 26 February to 12 March 2020 interval and +55 and +39 mm at the MR and CP field sites during the 10–24 February 2021 surveys (Fig. 9a, d, g). TLS SWE retrievals have a high correlation with SWE converted from depth probes, with an r of 0.83 and an RMSE of 66 mm (n=189; Fig. S3). For each set of TLS acquisitions, UAVSAR ΔSWE retrievals had median values of +6, +60, and +45 mm, respectively (Fig. 9b, e, h). Spatial patterns were similar between the two methods of ΔSWE retrievals. Large portions of data are missing in Fig. 9e due to coherence-related phase unwrapping errors. RMSEs were comparable between the 2020 survey (MR =20 mm) and the 2021 surveys (MR =15 mm, CP =20 mm). UAVSAR ΔSWE retrievals have an overall RMSE of 19 mm and an r of 0.72 when compared with TLSs. Coherence was used to color points on the UAVSAR–TLS comparison plots (Fig. 9c, f, i) and shows that scatter is approximately equal throughout the range of observed coherences.
4.5 Evaluation of UAVSAR time series at automated stations
UAVSAR SWE retrievals overestimated SWE accumulation for the 12–19 February 2020 InSAR pair by an average of 163 % at the automated stations but underestimated SWE accumulation by an average of 88 % between 19 February and 12 March (Fig. 10a–e). The 2021 cumulative UAVSAR SWE retrievals record net increases at all seven sites (+109 to +219 mm), which is similar to the net increases recorded by the stations (+101 to +242 mm; Fig. 10a–g). Median coherence for the 2020 season was lowest at the Lake Irene SNOTEL station (median coherence =0.30) and highest at the Phantom Valley SNOTEL station (median coherence =0.63), whereas median coherence for the 2021 season was lowest at the Montgomery Snow Stake (median coherence =0.49) and highest at the Lake Irene SNOTEL station (median coherence =0.60). The lowest median coherence for all sites was observed for the 26 February to 12 March 2020 interval (median coherence =0.31), an interval that yielded negative SWE retrievals for three of the five operating stations (−17 to −3 mm). At the end of the UAVSAR campaigns, cumulative UAVSAR SWE retrievals from the seven stations (n=12) yielded an RMSE =42 mm and an r=0.92 (Fig. 10h).
5.1 Accuracy of L-band InSAR ΔSWE retrievals
From our evaluation with GPR and TLSs, we established the RMSE for L-band InSAR ΔSWE retrievals as 19–22 mm for single InSAR pairs (Figs. 7, 9). For cumulative InSAR SWE, we estimated an RMSE of 42 mm at seven automated stations (Fig. 10). Previous studies have established that UAVSAR ΔSWE retrievals resemble the spatial patterns of lidar-derived ΔSWE retrievals, but differences between the two datasets were not systematic (Marshall et al., 2021; Palomaki and Sproles, 2023). Marshall et al. (2021) evaluated UAVSAR ΔSWE retrievals over a 4 km2 relatively flat and non-forested region of Grand Mesa, Colorado, using airborne lidar and found very low error for the technique (RMSE = 9 mm). UAVSAR ΔSWE retrievals have been evaluated using GPR and automated station measurements in Valles Caldera, New Mexico (Tarricone et al., 2023), and from in situ and SNOTEL measurements of ΔSWE in the mountains of Idaho (Hoppinen et al., 2024). Both studies identified and corrected significant atmospheric artifacts and contained at least one InSAR pair that was collected when liquid water content was present in the snowpack but estimated study-wide errors of similar magnitude found by our study (RMSE =15–40 mm; Table S4).
UAVSAR ΔSWE retrievals had higher RMSE in 2020 than in 2021 (Table S4), and the agreement between the InSAR time series and the automated stations was poorer in 2020 than in 2021 (Fig. 10). One potential explanation for the lower agreement in 2020 was the significant deviation (>10 m) from the cross-track and vertical baselines of the aircraft during the 2020 flights (Jones et al., 2016; NASA UAVSAR, 2023). UAVSAR ΔSWE spatial patterns are similar to those of TLS ΔSWE (Fig. 9), and the comparison of UAVSAR and GPR ΔSWE site-wide distributions reveals nearly identical medians (absolute median difference =2 mm; Fig. 7b–c). We found that low coherence did not substantially increase the RMSE of UAVSAR ΔSWE retrievals as the RMSE was less than 35 mm for >10 d temporal baselines (Fig. 8). However, lower coherence for InSAR pairs with >10 d temporal baselines exhibited issues with phase unwrapping. Collectively, these findings suggest a high degree of accuracy and reliability for InSAR ΔSWE retrievals, particularly in relatively simpler environments (i.e., dry snow conditions, non-forested areas, slopes <20°) and when atmospheric delays are limited.
5.2 Considerations for future evaluations of InSAR ΔSWE retrievals
The NISAR satellite mission holds promise for global repeat 12 d ΔSWE retrievals, providing the opportunity to evaluate the L-band InSAR technique in a range of environments and to better assess its uncertainties. In our evaluation, we used two ground-based methods that many snow community researchers have access to and showed that both methods are capable of assessing InSAR ΔSWE retrieval accuracy. Both methods can be used to derive spatially continuous SWE measurements over large areas and are therefore advantageous over standard in situ SWE measurement methods (Holbrook et al., 2016; McGrath et al., 2019). Below we outline advantages, considerations, and challenges of GPR and TLSs for InSAR evaluation.
Few methods match the sophistication of InSAR for change detection. Of the two techniques we employed in our evaluation, lidar is the most applicable for change detection (Deems et al., 2013), but its methodology for ΔSWE retrievals is not straightforward. There are two conceptual paths for ΔSWE retrievals from lidar: (1) subtraction of two repeat snow-on lidar elevation surveys or (2) subtraction of two bulk SWE datasets derived from lidar. The first option is complicated by snow compaction, while the second option requires accurate bulk snow densities and a snow-off bare-earth digital terrain model, which may be difficult to acquire in densely vegetated areas. We chose the second option because bulk density variability is less of a concern for the relatively small areas surveyed by the TLSs (Bonnell et al., 2023). We found the best agreement between UAVSAR and TLS ΔSWE retrievals for surveys that were aligned on the same date, as differential SWE accumulation/redistribution increased uncertainty (Fig. 9). Note that if the TLS platform is set up on top of the snowpack, accurate TLS ΔSWE retrievals may be hindered by small shifts in the TLS platform as it settles in the snow (Currier et al., 2019).
Repeat GPR transects also have several challenges. Our survey methodology involved marking our transects and post-processing the onboard GPS sensor (±0.25 m accuracy), but it is likely that our tracks were offset by ±1–2 m from the transect for some surveys. Further, as SWE increases throughout a season, the twt to the ground reflector increases, effectively increasing both the GPR horizontal footprint and the potential for clutter in the radargram (Daniels, 2004). Surface-coupled GPR has the potential to both compact the snow below the sled and remove snow from the surface (e.g., McGrath et al., 2019), which may further increase the uncertainty of GPR ΔSWE retrievals, particularly in low-density snow on the surface of the snowpack. These complications may explain the low Pearson’s correlation coefficients observed between UAVSAR and GPR ΔSWE retrievals for single InSAR pairs ( to +0.2; Table S4), as well as the low GPR–UAVSAR ΔSWE retrieval relation (r2<0.1) described by Tarricone et al. (2023). However, as our analysis shows, repeat GPR transects are effective at evaluating the InSAR technique if there are enough data collected across a range of SWE accumulation magnitudes (Fig. 7).
A major difference between UAVSAR and planned NISAR interferograms is the spatial resolution (∼5 vs. 80 m), which may complicate future NISAR ΔSWE retrieval ground-based evaluations. GPR surveyed along transects scaled well to the resolution of UAVSAR, but a different survey design (i.e., spiral or grid) may be required to provide sufficient coverage of the NISAR pixels. Thus, GPR may have increased uncertainty in its scalability due to a difficulty of repeating complicated survey designs. Lidar is scalable to coarser resolutions (e.g., 50 m; Painter et al., 2016), and TLS and drone-mounted lidar (e.g., Feng et al., 2023) may be valuable tools for evaluating InSAR ΔSWE retrievals at small field sites. However, at larger scales, comprehensive airborne lidar surveys will be required to fully evaluate NISAR ΔSWE retrievals.
5.3 Remaining questions for the L-band InSAR ΔSWE retrieval technique
L-band InSAR has been seen as a promising technique for high-resolution snow monitoring for over a decade (Deeb et al., 2011), yet insufficient opportunities existed for robust evaluations. In the last few years, airborne InSAR campaigns over seasonal snowpacks have created opportunities for a more thorough evaluation of this technique. Our study and others show that this technique can have a high accuracy, but there are several areas of uncertainty that need to be considered, including forested environments, wet snowpacks, complex topography that results in steep incidence angles, spatially varying atmospheric delays, and the integration of InSAR ΔSWE retrievals with other remote sensing methods and models.
Recent UAVSAR studies (Hoppinen et al., 2024; Marshall et al., 2021; Palomaki and Sproles, 2023; Tarricone et al., 2023), including this study, have largely focused on ΔSWE retrievals in open environments. We found that ΔSWE retrievals were 66 % higher on average in the open areas around the MR field site than below forest cover. Forest canopy interception and sublimation may play a role in this signal, because this process is known to drive a 20 %–30 % reduction of total snowfall at the nearby Fraser Experimental Forest (Montesi et al., 2004). On the other hand, a contrast between lower snow surface densities in the forest compared with the potentially higher densities we measured in the open could explain a similar magnitude of the signal. Unfortunately, we are unable to validate the forest ΔSWE retrievals as only 20 % of GPR observations in 2020 and 10 % of GPR observations in 2021 were collected below spruce–fir canopy (15 %–70 % canopy cover). Forests interfere with the radar signal, reducing coherence and potentially biasing retrievals, particularly for longer temporal baselines (Li et al., 2022; Ruiz et al., 2022). However, coherence only improved by +0.05 from forests to open areas at our field sites, and even the removal of canopy due to the Cameron Peak wildfire only increased coherence by +0.04. Thus, because of its canopy penetrative capabilities, the L-band InSAR ΔSWE retrieval technique may be the first satellite-based technique viable for SWE monitoring in forests.
At our site, UAVSAR flights occurred during the accumulation season when the snowpack was likely dry (Fig. 3e–f). However, SWE monitoring is needed for snowpacks that accumulate at or near 0 °C and for the melt season, making ΔSWE retrieval evaluation prioritized in wet snowpacks. Liquid water in the snowpack raises both the real and imaginary components of relative permittivity, which decreases the snowpack radar velocity and increases absorption of the radar signal, causing decreased signal penetration (Tsai et al., 2019). Even if the backscattering interface is unchanged, reduced radar velocity causes ΔSWE retrieval overestimation if the liquid water content is not considered (Bonnell et al., 2021; Tarricone et al., 2023). Tarricone et al. (2023) evaluated ΔSWE retrievals with the Landsat fractional snow-covered area product and found reasonable snowpack ablation over a 14 d period in Valles Caldera, New Mexico, but Hoppinen et al. (2024) found reduced ΔSWE retrieval accuracy in wet snowpacks. Wet snow detection techniques have been developed and implemented at the C-band (e.g., Gagliano et al., 2023; Nagler and Rott, 2000; Nagler et al., 2016), and similar techniques should be evaluated at L-band frequencies (e.g., Park et al., 2014).
During the winters of 2020 and 2021, UAVSAR collected L-band InSAR datasets over 12 mountainous regions of the western United States, including continental snowpacks of Colorado, intermountain snowpacks of Idaho and Montana, maritime snowpacks of California, and shallow mountain snowpacks in New Mexico. At the Cameron Pass field site, we used extensive GPR and TLSs to evaluate UAVSAR ΔSWE retrievals over a three-pair time series (4 weeks) that saw 121 mm SWE accumulation in 2020 and a seven-pair time series (9 weeks) that saw 206 mm SWE accumulation in 2021. Our analysis was not complicated by the presence of liquid water within the snowpack, and we emphasized GPR and TLS collection in open areas at our field sites. Our results indicate accurate statistical distributions for the L-band InSAR method for areas without forest cover (absolute median difference =2 mm compared to GPR), but low correlation coefficients ( to +0.2) for individual InSAR pairs warrant caution for ΔSWE interpretation at the single-pixel scale. UAVSAR ΔSWE retrievals exhibited distinct and repeated spatial patterns relating to the land cover, as forests averaged 66 % less ΔSWE per InSAR pair than open meadows, burned forests, and avalanche alleyways in forests. We expanded our in situ SWE observations to include seven automated weather stations distributed throughout the swath and highlighted the utility of the InSAR method for measuring cumulative SWE (RMSE =42 mm), a requirement for any SWE remote sensing method. We found that the range in RMSE from coherences of 0.10–0.90 was <10 mm, indicating that low coherence does not necessarily inhibit the accurate retrieval of ΔSWE. Although our ground observations did not target forested areas, we found the median coherence in the forests averaged 0.05 less than in the open meadows, suggesting ΔSWE retrievals may be viable in these environments, but the location of the amplitude center as forest cover increases remains an active question. Collectively, our study supports the use of L-band InSAR for measuring SWE in mountain snowpacks, further highlighting the potential of NISAR and other upcoming L-band SAR satellites to contribute substantially to global SWE monitoring.
A1 L-band transmissibility
At L-band frequencies (1–2 GHz, ∼0.25 m wavelength), dry snow is fully transmissible because of limited interactions between snow grains and the radar signal (Tsai et al., 2019). The bulk of reflected energy is returned from the snow–ground interface for areas without dense vegetation (Nagler et al., 2022), but uncertainty regarding the source of the primary backscattering surface increases with increased vegetation density because the L-band signal interacts with tree trunks, large branches, and dense vegetation (Ottinger and Kuenzer, 2020).
A2 The InSAR technique for ΔSWE retrievals
A2.1 Introduction to the InSAR technique
SAR emits polarized radar signals at a given frequency and narrow bandwidth and records the amplitude and phase of backscattered signal (Woodhouse, 2017). InSAR is a change detection technique that calculates the phase change between two radar signals operating at identical wavelengths and polarizations. Guneriussen et al. (2001) proposed a method for removing the snow accumulation signal from interferometric pairs where at least one of the acquisitions occurred during the snow season. Their proposed method forms the basis for most published InSAR ΔSWE retrieval techniques and is the one we implement. We applied this technique to repeat airborne acquisitions and assume the phase deformation is primarily due to the accumulation or redistribution of snow. We accessed unwrapped interferograms from the ASF Distributed Active Archive Center (DAAC). Interferograms were unwrapped by the UAVSAR team, following the integrated and correlation unwrapping method (Goldstein and Werner, 1998). This technique relies on the interferometric coherence (γ), which is calculated as
where E is the expected value of a given variable, and u1 and u2 are the amplitudes for the two image pairs (Woodhouse, 2017).
In the case of snow, the amplitude center is assumed to be the snow–ground interface, and any deformation in phase is expressed as
where the total interferometric phase change (ϕ) is expressed as the sum of the phase changes that arise from changes in the relative distance between the radar platform and the ground target for flat Earth (ϕflat) and topography (ϕtopo), changes in the atmospheric conditions that cause signal delays (ϕatm), the changes in phase caused by the change in snow depth or SWE (ϕs), and phase changes caused by instrument noise (ϕerr; Deeb et al., 2011). Instrument noise can manifest as random error or systematic error, which can result from a non-constant flight track (Jones et al., 2016). Topographic corrections are minimized by the UAVSAR instrument, as it performs acquisitions within a repeated 10 m tube, but both the topographic and flat-Earth contributions towards total phase change are accounted for in the UAVSAR unwrapped interferograms. However, atmospheric delays, caused by changes in atmospheric pressure and water vapor mass that occur between acquisitions, may influence the interferometric phase change (Bevis et al., 1992).
A2.2 Atmospheric correction for UAVSAR
Atmospheric delays are generally described as stratified or turbulent, where stratified delays are manifested as phase ramps or are correlated with topography and occur due to relatively homogeneous differences in atmospheric conditions, whereas turbulent delays are more difficult to identify and are caused by heterogeneous differences in atmospheric conditions (Hu and Mallorquí, 2019). Modeling atmospheric delays from airborne platforms is complicated, primarily due to the relatively coarse vertical resolution of most atmospheric reanalysis/forecast products that extends higher than the UAVSAR flight altitude (∼12.5 km). Three recently developed methods may be applicable for our study: (1) a statistical approach that models delays assuming a stratified atmosphere (Tarricone et al., 2023), (2) an approach that integrates phase delays along the signal path using ERA5 atmospheric data (Hoppinen et al., 2024), and (3) modeling the turbulent delay from atmospheric pressure and precipitable water using the High-Resolution Rapid Refresh Model (HRRR; Gong et al., 2013). We chose the Tarricone et al. (2023) approach, which has higher spatial resolution than either the ERA5 or HRRR methods, and developed a workflow to evaluate the need for a stratified atmospheric correction.
The workflow estimates an atmospheric correction as a best-fit plane across the UAVSAR scene, by regressing the unwrapped phase at snow-free pixels with the radar signal path length. Before the analysis, we defined requirements that the atmospheric correction had to meet in order to be implemented: (1) regression slope estimators needed to be identical across all four polarizations, and the estimator's p value needed to be <0.05; (2) coefficients of determination (r2) were required to be >0.20; and (3) the root mean square error (RMSE) of atmospherically corrected ΔSWE had to improve the RMSE of uncorrected ΔSWE by >20 %.
Sentinel-2 Level 2A (surface reflectance) 2020 and 2021 products were accessed in Google Earth Engine at 10 m resolution. Clouds were removed for each image, and an average image was composited for all Sentinel-2 acquisitions between UAVSAR flights. The normalized difference snow index (NDSI; Dozier, 1989) between green and shortwave infrared (SWIR) bands was calculated as
We then masked out forests from the scene using the Copernicus Global Land Cover 100 m dataset (Figure S1). Snow-free pixels were identified as NDSI <0.2, based on visual inspection of the optical imagery. We then regressed the unwrapped phase at snow-free pixels against the radar signal path length to estimate a phase ramp for each InSAR pair. We calculated RMSE for both atmospherically corrected and uncorrected datasets using SNOTEL ΔSWE calculated from the four SNOTEL stations (Table S2) where we took the median of the nearest nine UAVSAR ΔSWE pixels but removed stations that had coherence <0.5. No single interferogram met our listed requirements (Table S1). We conclude that stratified atmospheric delays may be present but do not substantially affect the accuracy of ΔSWE retrievals.
A2.3 Calculating InSAR ΔSWE retrievals
Assuming all other phase terms are accounted for (Eq. A2), ΔSWE can be calculated from the snow phase term, the radar wavelength (λ; ∼0.238 m), the local incidence angle (θinc), and the relative permittivity (ϵs). Because the radar signal intersects the snowpack obliquely, the unwrapped phase must be projected to the surface normal using the local incidence angle. We calculated incidence angles in uavsar_pytools (Hoppinen and Tarricone, 2022) as
where is the dot product of the surface normal calculated from a DEM and the magnitude of the UAVSAR-provided look vector (containing the east, north, and up components).
Relative permittivity describes the ratio of the dielectric permittivity of a material to the dielectric permittivity of free space (Daniels, 2004). In dry snow, relative permittivity is determined primarily by the snow density, whereas liquid water content becomes the defining variable in wet snow (Bonnell et al., 2021; Koch et al., 2014). We concluded that the snowpack was dry throughout our field campaigns (Sect. 4.1). We calculated relative permittivity from the Kovacs et al. (1995) equation, which was found to have an RMSE =54 kg m−3 for densities derived in Colorado (Bonnell et al., 2023). The equation
calculates the relative permittivity of snow from the snow density (ρs) in kg m−3 and represents the median of published dry snow relative permittivity equations (Di Paolo et al., 2020). We estimated the relative permittivity of the snowpack surface using an estimate of the snowpack surface density. The change in snow depth (Δds) is given as
At the UAVSAR wavelength and for a given θinc=1.2 rad and a snow surface ϵs=1.270 (ρs=150 kg m−3), phase wrapping occurs at Δds=0.72 m or ΔSWE =108 mm. Finally, ΔSWE is calculated by multiplying the snow depth by the surface density:
A2.4 Evaluation of the Leinss et al. (2015) linear approximation for InSAR ΔSWE retrievals
For dry snow, InSAR phase change has a near-linear dependence upon the change in SWE (Guneriussen et al., 2001; Leinss et al., 2015; Oveisgharan et al., 2024), and such a relation can be leveraged to derive InSAR ΔSWE independent of density or relative permittivity measurements. In our study, we calculated ΔSWE using the density-dependent method (Eqs. A6–A7) because surface density was a target variable during the surveys (Fig. 3), and several previous studies have opted to use the density-dependent method because airborne platforms yield a much larger range of incidence angles than satellite platforms (e.g., Hoppinen et al., 2024; Marshall et al., 2021; Nagler et al., 2022; Tarricone et al., 2023). We evaluated the utility of the Leinss et al. (2015) approximation for ΔSWE using the 16–22 March 2021 HH InSAR pair. The equation
modifies Eq. (A6) using the Matzler (1996) permittivity model such that ΔSWE is calculated from the phase change, the radar wavelength, the incidence angle, and an optimization parameter (α). Readers are referred to Leinss et al. (2015) for a review of the optimization parameter. Given the range of incidence angles and snow densities at our field sites, we chose α=1.02. The linear approximation results in nearly identical ΔSWE retrievals (r=0.99; Fig. S4a–c), and the comparison with GPR ΔSWE retrievals yields nearly identical statistical distributions and performance statistics (Fig. S4d–f). We conclude that the Leinss et al. (2015) approximation may be an appropriate alternative for ΔSWE retrievals from airborne platforms.
A2.5 Incidence angle analysis
The incidence angles used to calculate ΔSWE from the UAVSAR unwrapped phase datasets were derived by downsampling from the Copernicus 30 m DEM. The Copernicus 30 m DEM was derived from TanDEM-X acquisitions, which operates at 9.6 GHz center frequency, and the DEM has increased uncertainty over forested landscapes. Here, we evaluated the uncertainty for ΔSWE retrievals caused by errors in the Copernicus-derived incidence angles by calculating incidence angles from a 0.5 m lidar digital terrain model collected in September 2021 (Adebisi et al., 2022) over a subset of the UAVSAR swath that includes our field sites. Although the Copernicus-derived incidence angles display similar trends compared to the lidar-derived incidence angles, a comparison between the two products reveals high variability between the two products (r=0.08, RMSE =20°; Fig. S5a–c). ΔSWE retrieval uncertainty was estimated through a Monte Carlo simulation with 100 000 realizations around a mean incidence angle of 52.8° and a 20° standard deviation, approximated from the RMSE of the Copernicus-derived incidence angles (Fig. S5d). A density of 150 kg m−3 and phase change of 0.5π were used for the ΔSWE inversion (Fig. S5e). From the standard deviation of simulated ΔSWE, we estimate a ΔSWE retrieval uncertainty of ±7 mm that can be attributed to the use of the Copernicus-derived incidence angles in this region.
A3 GPR for SWE retrievals
GPR is a geophysical method for subsurface imaging that, when set up in the common-offset configuration, can measure the twt from the antennas to a reflector of interest. We used an L-band GPR with a 1.0 GHz center frequency and a 1.0 GHz bandwidth. GPR is a well-validated tool for estimating spatially distributed snow depth and SWE (Koh et al., 1996; Lundberg et al., 2006; McGrath et al., 2019). GPR surveys aggregate signal traces to form radargrams, which map reflection amplitudes with corresponding twt. For SWE retrievals, the reflector of interest is the snow–ground interface, which manifests as the highest magnitude reflector at depth, due to the high contrast between snow and soil permittivity. The radar velocity (vs) of the snowpack can be estimated from the snowpack relative permittivity (Eq. A5):
where c is the velocity of electromagnetic waves in free space (Daniels, 2004). Then, the twt of the ground reflector can be converted to snow depth:
which is subsequently converted to SWE (Eq. A7).
UAVSAR ΔSWE products are archived with Dryad (https://doi.org/10.5061/dryad.mkkwh7189, Bonnell et al., 2024). GPR datasets used in this analysis are archived with the NSIDC (https://doi.org/10.5067/SRWGLYCB6ZC4, Bonnell et al., 2022; McGrath et al., 2021). Snow pits are archived at the NSIDC (https://doi.org/10.5067/POT9E0FFUUD1, Mason et al., 2023; https://doi.org/10.5067/QIANJYJGRWOV, Mason et al., 2024), while probed snow depths from both seasons are under review at the NSIDC. SNOTEL station data are publicly available from the NRCS and were used for the following stations: Joe Wright (https://wcc.sc.egov.usda.gov/nwcc/site?sitenum=551, USDA, 2024a), Lake Irene (https://wcc.sc.egov.usda.gov/nwcc/site?sitenum=565, USDA, 2024b), Willow Park (https://wcc.sc.egov.usda.gov/nwcc/site?sitenum=870, USDA, 2024c), and Phantom Valley (https://wcc.sc.egov.usda.gov/nwcc/site?sitenum=688, USDA, 2024d). CPWS weather station data are archived at HydroShare (https://www.hydroshare.org/resource/a15f503ab00b4980a4bfbe7e8552f9a3, Kampf et al., 2022). TLS point clouds are available at UNAVCO Inc. (https://tls.unavco.org/projects/U-077/, Williams, 2021). NASA UAVSAR datasets are available from UAVSAR or the ASF DAAC, including InSAR pair products (i.e., unwrapped phase, coherence) and SLC products (i.e., look vectors; https://doi.org/10.5067/7PEQV8SVR4DM, NASA UAVSAR, 2020, 2021). The Copernicus 30 m DEM, the Copernicus Global 100 m Land Cover Dataset, and the Sentinel-2 Level 2A imagery were accessed via Google Earth Engine (Gorelick et al., 2017).
The supplement related to this article is available online at: https://doi.org/10.5194/tc-18-3765-2024-supplement.
Conceptualization: HPM, DM, and RB. Data curation: RB, DM, KW, YL, YZ, MS, and SK. Formal analysis: RB. Funding acquisition: RB, DM, and HPM. Investigation: RB, DM, YL, YZ, LZ, AOM, EB, CD, KW, MS, and SK. Methodology: RB, DM, JT, and HPM. Visualization: RB. Writing (original draft preparation): RB. Writing (review and editing): RB, DM, JT, HPM, SK, KW, MS, EB, CD, and YL.
The contact author has declared that none of the authors has any competing interests.
Publisher's note: Copernicus Publications remains neutral with regard to jurisdictional claims made in the text, published maps, institutional affiliations, or any other geographical representation in this paper. While Copernicus Publications makes every effort to include appropriate place names, the final responsibility lies with the authors.
Randall Bonnell acknowledges NASA FINESST award 80NSSC20K1624 for fieldwork and data analysis support. Randall Bonnell and Daniel McGrath acknowledge NASA THP award 80NSSC18K1405 for fieldwork support. A portion of data analysis was performed using the RMACC Summit supercomputer, which is supported by the NSF (awards ACI-1532235 and ACI-1532236), the University of Colorado – Boulder, and Colorado State University. We thank the NASA SnowEx leadership team for designing and implementing the 2020 and 2021 time series campaigns. We thank the NSIDC and Megan Mason for data archiving support. We thank the NASA UAVSAR team for their data collection and processing efforts. We acknowledge the services provided by the GAGE Facility, operated by UNAVCO, Inc., with support from the NSF and NASA under NSF cooperative agreement EAR-1724794. We thank Ethan Greene and the CAIC for sharing the CAIC Cameron Pass weather station data. We acknowledge Wyatt Reis, Coleman Kane, Jens Christoph Suhr, Brendan Auer, John Nelson, and Katie Snelling for their assistance with fieldwork. We thank Jeff Dozier, two anonymous reviewers, and Giacomo Medici for their insightful comments and constructive feedback provided during the open review process through EGUsphere, which led to an improved manuscript.
This research has been supported by the National Aeronautics and Space Administration, Earth Sciences Division (grant nos. 80NSSC18K1405 and 80NSSC20k1624).
This paper was edited by John Yackel and reviewed by Jeff Dozier and two anonymous referees.
Adebisi, N., Marshall, H., O'Neel, S., Vuyovich, C. M., Hiemstra, C., and Elder, K.: SnowEx20-21 QSI Lidar DEM 0.5m UTM Grid, Version 1, Boulder, Colorado USA, NASA National Snow and Ice Data Center Distributed Active Archive Center [data set], https://doi.org/10.5067/YO583L7ZOLOO, 2022. a
Barnett, T. P., Adam, J. C., and Lettenmaier, D. P.: Potential impacts of a warming climate on water availability in snow-dominated regions, Nature, 438, 303–309, https://doi.org/10.1038/nature04141, 2005. a
Bauer, M. A., Burgess, M. A., Adams, J. D., Sexstone, G. A., Fulton, J. W., McDermott, W. R., and Brady, L. R.: Lidar point clouds (LPCs), digital elevation models (DEMs), and snow depth raster maps derived from lidar data collected on small, uncrewed aircraft systems in the Upper Colorado River Basin, Colorado, 2020–22, U.S. Geological Survey Data Release [data set], https://doi.org/10.5066/P9LF15AE, 2023. a
Besso, H., Shean, D., and Lundquist, J. D.: Mountain snow depth retrievals from customized processing of ICESat-2 satellite laser altimetry, Remote Sens. Environ., 300, 113843, https://doi.org/10.1016/j.rse.2023.113843, 2024. a
Bevis, M., Businger, S., Herring, T. A., Rocken, C., Anthes, R. A., and Ware, R. H.: GPS meteorology: Remote sensing of atmospheric water vapor using the global positioning system, J. Geophys. Res.-Atmos., 97, 15787–15801, https://doi.org/10.1029/92JD01517, 1992. a
Bonnell, R., McGrath, D., Williams, K., Webb, R., Fassnacht, S. R., and Marshall, H.-P.: Spatiotemporal Variations in Liquid Water Content in a Seasonal Snowpack: Implications for Radar Remote Sensing, Remote Sens., 13, 4223, https://doi.org/10.3390/rs13214223, 2021. a, b
Bonnell, R., McGrath, D., Zeller, L., Bump, E., and Olsen-Mikitowicz, A.: SnowEx21 Cameron Pass Ground Penetrating Radar, Version 1, National Snow and Ice Data Center Distributed Active Archive Center [data set], https://doi.org/10.5067/SRWGLYCB6ZC4, 2022. a, b, c
Bonnell, R., McGrath, D., Hedrick, A. R., Trujillo, E., Meehan, T. G., Williams, K., Marshall, H.-P., Sexstone, G., Fulton, J., Ronayne, M. J., Fassnacht, S. R., Webb, R. W., and Hale, K. E.: Snowpack relative permittivity and density derived from near-coincident lidar and ground-penetrating radar, Hydrol. Process., 37, e14996, https://doi.org/10.1002/hyp.14996, 2023. a, b
Bonnell, R., McGrath, D., and Tarricone, J.: Data from: L-band InSAR SWE retrievals over Northern Colorado, Dryad [data set], https://doi.org/10.5061/dryad.mkkwh7189, 2024. a
Borah, F. K., Tsang, L., and Kim, E.: SWE Retrieval Algorithms Based on the Parameterized BI-Continuous DMRT Model Without Priors on Grain Size Or Scattering Albedo, Prog. Electromagn. Res., 178, 129–147, https://doi.org/10.2528/PIER23071101, 2023. a
Brangers, I., Marshall, H.-P., De Lannoy, G., Dunmire, D., Mätzler, C., and Lievens, H.: Tower-based C-band radar measurements of an alpine snowpack, The Cryosphere, 18, 3177–3193, https://doi.org/10.5194/tc-18-3177-2024, 2024. a
Buchhorn, M., Smets, B., Bertels, L., Roo, B. D., Lesiv, M., Tsendbazar, N.-E., Herold, M., and Fritz, S.: Copernicus Global Land Service: Land Cover 100m: collection 3: epoch 2019: Globe (Version V3.0.1), Zenodo [data set], https://doi.org/10.5281/zenodo.6789624, 2020. a
Conde, V., Nico, G., Mateus, P., Catalão, J., Kontu, A., and Gritsevich, M.: On The Estimation of Temporal Changes of Snow Water Equivalent by Spaceborne Sar Interferometry: A New Application for the Sentinel-1 Mission, J. Hydrol. Hydromech., 67, 93–100, https://doi.org/10.2478/johh-2018-0003, 2019. a
Currier, W. R., Pflug, J., Mazzotti, G., Jonas, T., Deems, J. S., Bormann, K. J., Painter, T. H., Hiemstra, C. A., Gelvin, A., Uhlmann, Z., Spaete, L., Glenn, N. F., and Lundquist, J. D.: Comparing Aerial Lidar Observations With Terrestrial Lidar and Snow-Probe Transects From NASA’s 2017 SnowEx Campaign, Water Resour. Res., 55, 6285–6294, https://doi.org/10.1029/2018WR024533, 2019. a, b
Daniels, D. J. (Ed.): Ground Penetrating Radar, Volume 1, The Institution of Electrical Engineers, ISBN-10 0863413609, ISBN-13 978-0863413605, 2004. a, b, c
Deeb, E. J., Forster, R. R., and Kane, D. L.: Monitoring snowpack evolution using interferometric synthetic aperture radar on the North Slope of Alaska, USA, Int. J. Remote Sens., 32, 3985–4003, https://doi.org/10.1080/01431161003801351, 2011. a, b, c, d
Deems, J. S., Painter, T. H., and Finnegan, D. C.: Lidar measurement of snow depth: a review, J. Glaciol., 59, 467–479, https://doi.org/10.3189/2013JoG12J154, 2013. a
Di Paolo, F., Cosciotti, B., Lauro, S. E., Mattei, E., and Pettinelli, E.: A critical analysis on the uncertainty computation in ground-penetrating radar-retrieved dry snow parameters, Geophysics, 85, H39–H49, https://doi.org/10.1190/geo2019-0683.1, 2020. a
Dozier, J.: Spectral signature of alpine snow cover from the landsat thematic mapper, Remote Sens, Environ,, 28, 9–22, https://doi.org/10.1016/0034-4257(89)90101-6, 1989. a, b
Dozier, J., Bair, E. H., and Davis, R. E.: Estimating the spatial distribution of snow water equivalent in the world's mountains, WIREs Water, 3, 461–474, https://doi.org/10.1002/wat2.1140, 2016. a
Durand, M., Gatebe, C., Kim, E., Molotch, N., Painter, T. H., Raleigh, M., Sandells, M., and Vuyovich, C.: NASA SnowEx Science Plan: Assessing Approaches for Measuring Water in Earth’s Seasonal Snow, version 1.6, Science Plan, https://snow.nasa.gov/sites/default/files/SnowEx_Science_Plan_v1.6.pdf (last access: 1 May 2023), 2018. a
European Space Agency: Copernicus Global Digital Elevation Model, Distributed by Google Earth Engine [data set], https://doi.org/10.5270/ESA-c5d3d65, 2021. a
European Space Agency: Copernicus Sentinel data, Distributed by Google Earth Engine [data set], https://doi.org/10.5270/S2_-6eb6imz, 2022. a
Fassnacht, S. R., Venable, N. B., McGrath, D., and Patterson, G. G.: Sub-seasonal snowpack trends in the Rocky Mountain National Park area, Colorado, USA, Water, 10, 562, https://doi.org/10.3390/w10050562, 2018. a
Feng, T., Hao, X., Wang, J., Luo, S., Huang, G., Li, H., and Zhao, Q.: Applicability of alpine snow depth estimation based on multitemporal UAV-LiDAR data: A case study in the Maxian Mountains, Northwest China, J. Hydrol., 617, 129006, https://doi.org/10.1016/j.jhydrol.2022.129006, 2023. a
Fleming, S. W., Zukiewicz, L., Strobel, M. L., Hofman, H., and Goodbody, G. G.: SNOTEL, the soil climate analysis network, and water supply forecasting at the natural resources conservation service: Past, present, and future, JAWRA J. Am. Water Resour. A., 59, 585–599, https://doi.org/10.1111/1752-1688.13104, 2023. a
Gagliano, E., Shean, D., Henderson, S., and Vanderwilt, S.: Capturing the Onset of Mountain Snowmelt Runoff Using Satellite Synthetic Aperture Radar, Geophys. Res. Lett., 50, e2023GL105303, https://doi.org/10.1029/2023GL105303, 2023. a
Goldstein, R. M., and Werner, C. L.: Radar interferogram filtering for geophysical applications, Geophy. Res. Lett., 25, 4035–4038, https://doi.org/10.1029/1998GL900033, 1998. a
Gong, W., Meyer, F. J., Webley, P., and Morton, D.: Performance of the high-resolution atmospheric model HRRR-AK for correcting geodetic observations from spaceborne radars, J. Geophys. Res.-Atmos., 118, 11611–11624, https://doi.org/10.1002/2013JD020170, 2013. a, b
Gorelick, N., Hancher, M., Dixon, M., Ilyushchenko, S., Thau, D., and Moore, R.: Google Earth Engine: Planetary-scale geospatial analysis for everyone, Remote Sens. Environ., 202, 18–27, https://doi.org/10.1016/j.rse.2017.06.031, 2017. a
Guneriussen, T., Hogda, K. A., Johnsen, H., and Lauknes, I.: InSAR for estimation of changes in snow water equivalent of dry snow, IEEE T. Geosci. Remote, 39, 2101–2108, https://doi.org/10.1109/36.957273, 2001. a, b, c, d, e
Hedrick, A. R., Marks, D., Havens, S., Robertson, M., Johnson, M., Sandusky, M., Marshall, H.-P., Kormos, P. R., Bormann, K. J., and Painter, T. H.: Direct Insertion of NASA Airborne Snow Observatory-Derived Snow Depth Time Series Into the iSnobal Energy Balance Snow Model, Water Resour. Res., 54, 8045–8063, https://doi.org/10.1029/2018WR023190, 2018. a
Holbrook, W. S., Miller, S. N., and Provart, M. A.: Estimating snow water equivalent over long mountain transects using snowmobile-mounted ground-penetrating radar, Geophysics, 81, WA183–WA193, https://doi.org/10.1190/geo2015-0121.1, 2016. a
Hoppinen, Z., and Tarricone, J: uavsar_pytools (Version 0.7.0), Zenodo [code], https://doi.org/10.5281/zenodo.6789624, 2022. a, b, c
Hoppinen, Z., Oveisgharan, S., Marshall, H.-P., Mower, R., Elder, K., and Vuyovich, C.: Snow water equivalent retrieval over Idaho – Part 2: Using L-band UAVSAR repeat-pass interferometry, The Cryosphere, 18, 575–592, https://doi.org/10.5194/tc-18-575-2024, 2024. a, b, c, d, e, f
Hu, J. M., Shean, D., and Bhushan, S.: Six Consecutive Seasons of High-Resolution Mountain Snow Depth Maps From Satellite Stereo Imagery, Geophys. Res. Lett., 50, e2023GL104871, https://doi.org/10.1029/2023GL104871, 2023. a, b
Hu, Z. and Mallorquí, J. J.: An Accurate Method to Correct Atmospheric Phase Delay for InSAR with the ERA5 Global Atmospheric Model, Remote Sens., 11, 1969, https://doi.org/10.3390/rs11171969, 2019. a
ISRO Space Applications Centre: NISAR Utilisation Programme: Announcement inviting project proposals from Indian researchers, Utilization Programme Document, 36 pp., 2023. a
Jones, C. E., An, K., Blom, R. G., Kent, J. D., Ivins, E. R., and Bekaert, D.: Anthropogenic and geologic influences on subsidence in the vicinity of New Orleans, Louisiana, J. Geophys. Res.-Sol. Ea., 121, 3867–3887, https://doi.org/10.1002/2015JB012636, 2016. a, b
Kampf, S., Sears, M., Miller, Q., Puntenney-Desmond, K., Barnard, D., Green, T., Erskine, R., Sitterson, J., Kiewiet, L., Reis, W., and McGrath, D.: Cameron Peak Fire stream and weather data WY2021, HydroShare [data set], http://www.hydroshare.org/resource/a15f503ab00b4980a4bfbe7e8552f9a3 (last access: 1 November 2023), 2022. a
Klos, P. Z., Link, T. E., and Abatzoglou, J. T.: Extent of the rain-snow transition zone in the western US under historic and projected climate, Geophys. Res. Lett., 41, 4560–4568, https://doi.org/10.1002/2014GL060500, 2014. a
Koch, F., Prasch, M., Schmid, L., Schweizer, J., and Mauser, W.: Measuring snow liquid water content with low-cost GPS receivers, Sensors, 14, 20975–20999, https://doi.org/10.3390/s141120975, 2014. a
Koh, G., Yankielun, N. E., and Baptista, A. I.: Snow cover characterization using multiband FMCW radars, Hydrol. Process., 10, 1609–1617, https://doi.org/10.1002/(SICI)1099-1085(199612)10:12<1609::AID-HYP504>3.0.CO;2-O, 1996. a
Kovacs, A., Gow, A. J., and Morey, R. M.: The in-situ dielectric constant of polar firn revisited, Cold Reg. Sci. Technol., 23, 245–256, https://doi.org/10.1016/0165-232X(94)00016-Q, 1995. a
Leinss, S., Parrella, G., and Hajnsek, I: Snow height determination by polarimetric phase differences in X-band SAR data, IEEE J. Sel. Top. Appl. Earth Obs., 7, 3794–3810, https://doi.org/10.1109/JSTARS.2014.2323199, 2014. a
Leinss, S., Wiesmann, A., Lemmetyinen, J., and Hajnsek, I.: Snow water equivalent of dry snow measured by differential interferometry, IEEE J. Sel. Top. Appl. Earth Obs., 8, 3773–3790, https://doi.org/10.1109/JSTARS.2015.2432031, 2015. a, b, c, d, e, f, g, h
Li, D., Wrzesien, M. L., Durand, M., Adam, J., and Lettenmaier, D. P.: How much runoff originates as snow in the western United States, and how will that change in the future?, Geophys. Res. Lett., 44, 6163–6172, https://doi.org/10.1002/2017GL073551, 2017. a
Li, Y., Zhao, X., and Zhao, Q.: Snow Depth Inversion in Forested Areas from Sentinel-1 Data Based on Phase Deviation Correction, Remote Sens., 14, 5930, https://doi.org/10.3390/rs14235930, 2022. a
Lievens, H., Demuzere, M., Marshall, H.-P., Reichle, R. H., Brucker, L., Brangers, I., de Rosnay, P., Dumont, M., Girotto, M., Immerzeel, W. W., Jonas, T., Kim, E. J., Koch, I., Marty, C., Saloranta, T., Schöber, J., and De Lannoy, G. J. M.: Snow depth variability in the Northern Hemisphere mountains observed from space, Nat. Commun., 10, 4629, https://doi.org/10.1038/s41467-019-12566-y, 2019. a
Lievens, H., Brangers, I., Marshall, H.-P., Jonas, T., Olefs, M., and De Lannoy, G.: Sentinel-1 snow depth retrieval at sub-kilometer resolution over the European Alps, The Cryosphere, 16, 159–177, https://doi.org/10.5194/tc-16-159-2022, 2022. a, b
Lorenzi, V., Banzato, F., Barberio, M. D., Goeppert, N., Goldscheider, N., Gori, F., Lacchini, A., Manetta, M., Medici, G., Rusi, S., and Petitta, M.: Tracking flowpaths in a complex karst system through tracer test and hydrogeochemical monitoring: Implications for groundwater protection (Gran Sasso, Italy), Heliyon, 10, e24663, https://doi.org/10.1016/j.heliyon.2024.e24663, 2024. a
Lundberg, A., Richardson-Näslund, C., and Andersson, C.: Snow density variations: consequences for ground-penetrating radar, Hydrol. Process., 20, 1483–1495, https://doi.org/10.1002/hyp.5944, 2006. a
Marshall, H.-P., Vuyovich, C., Hiemstra, C., Brucker, L., Elder, K., Deems, J., and Newlin, J.: NASA SnowEx 2020 Experiment Plan, Science Plan, NASA SnowEx, https://snow.nasa.gov/sites/default/files/users/user354/SNEX-Campaigns/2020/NASASnowEx20_ExperimentPlan_v15.pdf (last access: 1 May 2023), 2019. a
Marshall, H. P., Deeb, E., Forster, R., Vuyovich, C., Elder, K., Hiemstra, C., and Lund, J.: L-Band InSAR Depth Retrieval During the NASA SnowEx 2020 Campaign: Grand Mesa, Colorado, in: 2021 IEEE International Geoscience and Remote Sensing Symposium IGARSS, 2021 IEEE International Geoscience and Remote Sensing Symposium IGARSS, 625–627, https://doi.org/10.1109/IGARSS47720.2021.9553852, 2021. a, b, c, d, e
Mason, M., Marshall, H., McCormick, M., Craaybeek, D., Elder, K., and Vuyovich, C. M.: SnowEx20 Time Series Snow Pit Measurements, Version 1, NASA National Snow and Ice Data Center Distributed Active Archive Center [data set], https://doi.org/10.5067/POT9E0FFUUD1, 2023. a, b
Mason, M., Marshall, H., Craaybeek, D., Elder, K., and Vuyovich, C. M.: SnowEx21 Time Series Snow Pits, Version 1, NASA National Snow and Ice Data Center Distributed Active Archive Center [data set], https://doi.org/10.5067/QIANJYJGRWOV, 2024. a
Matzler, C.: Microwave permittivity of dry snow, IEEE T. Geosci. Remote, 34, 573–581, https://doi.org/10.1109/36.485133, 1996. a
McCrystall, M. R., Stroeve, J., Serreze, M., Forbes, B. C., and Screen, J. A.: New climate models reveal faster and larger increases in Arctic precipitation than previously projected, Nat. Commun., 12, 6765, https://doi.org/10.1038/s41467-021-27031-y, 2021. a
McGrath, D., Webb, R., Shean, D., Bonnell, R., Marshall, H.-P., Painter, T. H., Molotch, N. P., Elder, K., Hiemstra, C., and Brucker, L.: Spatially Extensive Ground-Penetrating Radar Snow Depth Observations During NASA’s 2017 SnowEx Campaign: Comparison With In Situ, Airborne, and Satellite Observations, Water Resour. Res., 55, 10026–10036, https://doi.org/10.1029/2019WR024907, 2019. a, b, c
McGrath, D., Bonnell, R., Olsen-Mikitowicz, A., Duncan, C., and Grabowski, J.: SnowEx20 Cameron Pass Ground Penetrating Radar, Version 1, NASA National Snow and Ice Data Center Distributed Active Archive Center [data set], https://doi.org/10.5067/U4Q3X27BMRR4, 2021. a, b, c
McGrath, D., Zeller, L., Bonnell, R., Reis, W., Kampf, S., Williams, K., Okal, M., Olsen-Mikitowicz, A., Bump, E., Sears, M., and Rittger, K.: Declines in Peak Snow Water Equivalent and Elevated Snowmelt Rates Following the 2020 Cameron Peak Wildfire in Northern Colorado, Geophys. Res. Lett., 50, e2022GL101294, https://doi.org/10.1029/2022GL101294, 2023. a
Montesi, J., Elder, K., Schmidt, R. A., and Davis, R. E.: Sublimation of Intercepted Snow within a Subalpine Forest Canopy at Two Elevations, J. Hydrometeorol., 5, 763–773, https://doi.org/10.1175/1525-7541(2004)005<0763:SOISWA>2.0.CO;2, 2004. a
Moraga, J. S., Peleg, N., Fatichi, S., Molnar, P., and Burlando, P.: Revealing the impacts of climate change on mountainous catchments through high-resolution modelling, J. Hydrol., 603, 126806, https://doi.org/10.1016/j.jhydrol.2021.126806, 2021. a
Mote, P. W., Li, S., Lettenmaier, D. P., Xiao, M., and Engel, R.: Dramatic declines in snowpack in the western US, NPJ Climate and Atmospheric Science, 1, 2, https://doi.org/10.1038/s41612-018-0012-1, 2018 a
Naderpour, R., Schwank, M., Houtz, D., Werner, C., and Mätzler, C.: Wideband backscattering from alpine snow cover: A full-season study, IEEE T. Geosci. Remote, 60, 1–15, https://doi.org/10.1109/TGRS.2021.3112772, 2022. a
Nagler, T. and Rott, H.: Retrieval of wet snow by means of multitemporal SAR data, IEEE T. Geosci. Remote, 38, 754–765, https://doi.org/10.1109/36.842004, 2000. a
Nagler, T., Rott, H., Ripper, E., Bippus, G., and Hetzenecker, M.: Advancements for Snowmelt Monitoring by Means of Sentinel-1 SAR, Remote Sens., 8, 348, https://doi.org/10.3390/rs8040348, 2016. a
Nagler, T., Rott, H., Scheiblauer, S., Libert, L., Mölg, N., Horn, R., Fischer, J., Keller, M., Moreira, A., and Kubanek, J.: Airborne Experiment on Insar Snow Mass Retrieval in Alpine Environment, in: IGARSS 2022 – 2022 IEEE International Geoscience and Remote Sensing Symposium, IGARSS 2022 – 2022 IEEE International Geoscience and Remote Sensing Symposium, 4549–4552, https://doi.org/10.1109/IGARSS46834.2022.9883809, 2022. a, b, c
NASA UAVSAR: Rocky Mountains, Colorado Flight Line, Alaska Satellite Facility Distributed Active Archive Center [data set], https://doi.org/10.5067/7PEQV8SVR4DM, 2020. a, b
NASA UAVSAR: Rocky Mountains, Colorado Flight Line, Alaska Satellite Facility Distributed Active Archive Center [data set], https://doi.org/10.5067/7PEQV8SVR4DM, 2021. a, b
NASA UAVSAR: Product: rockmt_14107_01, Coregistered SLC Stack of Rocky Mountains NP, CO, NASA Jet Propulsion Laboratory [data set], https://uavsar.jpl.nasa.gov/cgi-bin/product.pl?jobName=rockmt_14107_01#data, 2023. a, b
National Academies of Sciences, Engineering, and Medicine: Thriving on Our Changing Planet: A Decadal Strategy for Earth Observation from Space, National Academies Press, https://doi.org/10.17226/24938, 2018. a
Ottinger, M. and Kuenzer, C.: Spaceborne L-Band Synthetic Aperture Radar Data for Geoscientific Analyses in Coastal Land Applications: A Review, Remote Sens., 12, 2228, https://doi.org/10.3390/rs12142228, 2020. a
Oveisgharan, S., Zinke, R., Hoppinen, Z., and Marshall, H. P.: Snow water equivalent retrieval over Idaho – Part 1: Using Sentinel-1 repeat-pass interferometry, The Cryosphere, 18, 559–574, https://doi.org/10.5194/tc-18-559-2024, 2024. a, b
Painter, T. H., Berisford, D. F., Boardman, J. W., Bormann, K. J., Deems, J. S., Gehrke, F., Hedrick, A., Joyce, M., Laidlaw, R., Marks, D., Mattmann, C., McGurk, B., Ramirez, P., Richardson, M., Skiles, S. M., Seidel, F. C., and Winstral, A.: The Airborne Snow Observatory: Fusion of scanning lidar, imaging spectrometer, and physically-based modeling for mapping snow water equivalent and snow albedo, Remote Sens. Environ., 184, 139–152, https://doi.org/10.1016/j.rse.2016.06.018, 2016. a
Palomaki, R. T. and Sproles, E. A.: Assessment of L-band InSAR snow estimation techniques over a shallow, heterogeneous prairie snowpack, Remote Sens. Environ., 296, 113744, https://doi.org/10.1016/j.rse.2023.113744, 2023. a, b, c
Park, S.-E., Yamaguchi, Y., Singh, G., Yamaguchi, S., and Whitaker, A. C.: Polarimetric SAR Response of Snow-Covered Area Observed by Multi-Temporal ALOS PALSAR Fully Polarimetric Mode, IEEE T. Geosci. Remote, 52, 329–340, https://doi.org/10.1109/TGRS.2013.2240000, 2014. a
Patil, A., Singh, G., and Rüdiger, C.: Retrieval of Snow Depth and Snow Water Equivalent Using Dual Polarization SAR Data, Remote Sens., 12, 1183, https://doi.org/10.3390/rs12071183, 2020. a
Raleigh, M. S. and Small, E. E.: Snowpack density modeling is the primary source of uncertainty when mapping basin-wide SWE with lidar, Geophys. Res. Lett., 44, 3700–3709, https://doi.org/10.1002/2016GL071999, 2017. a
Rosen, P. A., Hensley, S., Wheeler, K., Sadowy, G., Miller, T., Shaffer, S., Muellerschoen, R., Jones, C., Zebker, H., and Madsen, S.: UAVSAR: a new NASA airborne SAR system for science and technology research, in: 2006 IEEE Conference on Radar, 2006 IEEE Conference on Radar, 8 pp., https://doi.org/10.1109/RADAR.2006.1631770, 2006. a
Ruiz, J. J., Lemmetyinen, J., Kontu, A., Tarvainen, R., Vehmas, R., Pulliainen, J., and Praks, J.: Investigation of Environmental Effects on Coherence Loss in SAR Interferometry for Snow Water Equivalent Retrieval, IEEE T. Geosci. Remote, 60, 1–15, https://doi.org/10.1109/TGRS.2022.3223760, 2022. a, b, c, d, e
Sandmeier, K. J.: ReflexW–GPR and Seismic Processing Software, Sandmeier [software], https://www.sandmeier-geo.de/reflexw.html (last access: 1 January 2021), 2019. a
Shi, J. and Dozier, J.: Estimation of Snow Water Equivalence Using SIR-C/X-SAR, Part II: Inferring Snow Depth and Particle Size, IEEE T. Geosci. Remote, 38, 2475–2488, https://doi.org/10.1109/36.885196, 2000. a
Siirila-Woodburn, E. R., Rhoades, A. M., Hatchett, B. J., Huning, L. S., Szinai, J., Tague, C., Nico, P. S., Feldman, D. R., Jones, A. D., Collins, W. D., and Kaatz, L.: A low-to-no snow future and its impacts on water resources in the western United States, Nat. Rev. Earth Environ., 2, 800–819, https://doi.org/10.1038/s43017-021-00219-y, 2021. a, b
Tarricone, J., Webb, R. W., Marshall, H.-P., Nolin, A. W., and Meyer, F. J.: Estimating snow accumulation and ablation with L-band interferometric synthetic aperture radar (InSAR), The Cryosphere, 17, 1997–2019, https://doi.org/10.5194/tc-17-1997-2023, 2023. a, b, c, d, e, f, g, h, i, j
Trujillo, E. and Molotch, N. P.: Snowpack regimes of the Western United States, Water Resour. Res., 50, 5611–5623, https://doi.org/10.1002/2013WR014753, 2014. a
Tsai, Y.-L. S., Dietz, A., Oppelt, N., and Kuenzer, C.: Remote Sensing of Snow Cover Using Spaceborne SAR: A Review, Remote Sens., 11, 1456, https://doi.org/10.3390/rs11121456, 2019. a, b
Tsang, L., Durand, M., Derksen, C., Barros, A. P., Kang, D.-H., Lievens, H., Marshall, H.-P., Zhu, J., Johnson, J., King, J., Lemmetyinen, J., Sandells, M., Rutter, N., Siqueira, P., Nolin, A., Osmanoglu, B., Vuyovich, C., Kim, E., Taylor, D., Merkouriadi, I., Brucker, L., Navari, M., Dumont, M., Kelly, R., Kim, R. S., Liao, T.-H., Borah, F., and Xu, X.: Review article: Global monitoring of snow water equivalent using high-frequency radar remote sensing, The Cryosphere, 16, 3531–3573, https://doi.org/10.5194/tc-16-3531-2022, 2022. a, b, c
USDA: Joe Wright, USDA Natural Resources Conservation Service [data set], https://wcc.sc.egov.usda.gov/nwcc/site?sitenum=551 (last access: 1 November 2023), 2024a. a
USDA: Lake Irene, USDA Natural Resources Conservation Service [data set] https://wcc.sc.egov.usda.gov/nwcc/site?sitenum=565 (last access: 1 November 2023), 2024b. a
USDA: Willow Park, USDA Natural Resources Conservation Service [data set] https://wcc.sc.egov.usda.gov/nwcc/site?sitenum=870 (last access: 1 November 2023), 2024c. a
USDA: Phantom Valley, USDA Natural Resources Conservation Service [data set] https://wcc.sc.egov.usda.gov/nwcc/site?sitenum=688 (last access: 1 November 2023), 2024d. a
Viste, E. and Sorteberg, A.: Snowfall in the Himalayas: an uncertain future from a little-known past, The Cryosphere, 9, 1147–1167, https://doi.org/10.5194/tc-9-1147-2015, 2015. a
Williams, K.: Cameron Pass NASA SnowEx, UNAVCO Inc. [data set], https://tls.unavco.org/projects/U-077/ (last access: 1 November 2022), 2021. a, b, c, d
Woodhouse, I. H.: Introduction to Microwave Remote Sensing, CRC Press, ISBN 036722514X, 2017. a, b, c, d, e
Wrzesien, M. L., Pavelsky, T. M., Durand, M. T., Dozier, J., and Lundquist, J. D.: Characterizing Biases in Mountain Snow Accumulation From Global Data Sets, Water Resour. Res., 55, 9873–9891, https://doi.org/10.1029/2019WR025350, 2019. a