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SOIL MOISTURE EVALUATION USING RADAR AND OPTICAL REMOTE SENSING IN SEMIARID RANGELAND, Moran et al.

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SOIL MOISTURE EVALUATION USING RADAR AND OPTICAL REMOTE SENSING IN SEMIARID RANGELAND

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M. Susan Moran, Daniel C. Hymer, Jiaguo Qi, Robert C. Marsett, Michael K. Helfert, and Edson E. Sano

USDA Agricultural Research Service, U.S. Water Conservation Laboratory, Phoenix, Arizona and EMBRAPA/CPAC, Brazil

email: moran@tucson.ars.ag.gov


Background

There is evidence that satellite-based Synthetic Aperture Radar (SAR) sensors could provide a regional assessment of surface soil moisture content (). Theoretically, SAR backscatter (, dB) detected by orbiting satellite-based sensors (e.g., ERS-2 SAR) is directly related to ; in practice, is also highly influenced by topographic features, vegetation density, and variations in small-scale surface roughness. Thus, it is difficult to convert SAR images directly into maps of regional for heterogeneous terrain. Previous studies have suggested that the accuracy of SAR-based estimates could be improved by combining data from optical sensors (e.g., surface reflectance and temperature) to discriminate the SAR signal response to vegetation.


Research Objectives

1. Investigate the sensitivity of ERS-2 C-band SAR backscatter measurements to soil moisture content in a semi-arid rangeland with sparse vegetation cover; and
2. Test an approach based on both optical (Landsat TM) and radar (ERS-2 SAR) measurements to improve regional estimates of soil moisture content.


Approach

In this project, we designed an experiment to study the link between ERS-2 SAR C-band backscatter to soil moisture, while minimizing the influence of other conditions. That is, we focused our study on flat, uniformly-vegetated sites, and planned to monitor the variations in soil moisture and vegetation cover over time. By choosing flat sites, we avoided the effects of topography; and by monitoring the sites over time (rather than multiple sites over space), we minimized the influence of variations in small-scale roughness conditions. Furthermore, by measuring vegetation density on a monthly basis at each site, we were able to quantify changes in vegetation that might influence SAR .

We requested 10 ERS-2 SAR scenes covering our study site throughout 1997. Dates of these overpasses were selected to correspond closely with the dates of overpasses of the Landsat-5 satellite. Landsat Thematic Mapper (TM) sensor measures surface reflected radiance in six wavelengths (from 0.45 to 2.35 µm) and measures surface temperature in a single spectral waveband covering 10.42 to 11.66 µm. Images from 6 months in 1997 are illustrated to below.

radar backscatter vs glai

This figure is a graphic illustration of the basic approach for the use of SAR/optical synergism for estimation of soil moisture content. The effects of soil roughness were taken into account by taking the difference between the SAR backscatter from a given image and the backscatter from a "dry season" image (). The vegetation influence was corrected by using an empirical relationship between () and green leaf area index (GLAI), where the latter was derived from the optical data. Thus, the soil moisture conditions are related to the length of the vertical arrow in the Figure; where the soil moisture content of B is greatest and A least, with C intermediate.

landsat and sar images


Experimental Site

experimental sites

Three sites were chosen in the Upper San Pedro River Basin (USPB) in southeast Arizona for investigation of the SAR/optical approach for monitoring surface soil moisture content. The sites were characterized by level terrain and uniform vegetation cover (over a 300 x 300 m area), and were named by the dominant vegetation type: Tobosa, Sacaton and Creosote. The Tobosa site is located in a swale which supports a mix of tobosa grass (Hilaria mutica) and creosote (Larrea tridentata) shrubs. The Sacaton site is dominated by big sacaton (Sporobolus wrightii) with some tobosa grass. The Creosote site is on a flat mesa and is characterized by scattered creosote shrubs (Larrea tridentata) with very few grasses or annual forbs.


Resultssoil moisture at experimental sites

Due to fortunate weather conditions, we obtained an excellent range of soil moisture conditions for our study. During the June SAR overpass, the soil moisture conditions at all sites were extremely dry, and the late summer greenup of the vegetation had not yet occurred. Consequently, we designated it as the "dry" scene and subtracted the June SAR backscatter () from the backscatter measured on all other dates to account for the contribution of surface roughness to the SAR signal.

We derived a relation between () and plant area index (PAI) using SAR () values from the March image for the Creosote (C) and Sacaton (S) sites. There was no significant variation in () associated with the measured variation in PAI at the two sites.

radar backscatter vs plant area index

It appeared that the differences in standing brown vegetation biomass at these two sites were accounted for in the roughness correction. Consequently, the values of () should be directly related to soil moisture conditions at the site, with no need for a PAI correction.

  • As expected, the measured C-band SAR backscatter (, dB) was poorly correlated (=0.21) with surface soil moisture content () at the three field sites (labeled C, S and T in the figure on top below). When the data were corrected for differences in surface roughness and standing brown vegetation biomass, there was a good correlation (=0.94) between () and at the three field sites (the figure on the bottom, below).
  • However, an unexpected result was discovered with data from the February SAR scene. That is, the SAR backscatter related to the moderately-wet soil conditions in February was less than that for extremely-dry soil conditions in June (i.e., <0). We suspect that there was an error in the sensor calibration on that date; further investigation will be conducted regarding this anomalous result.

radar backscatter vs soil moisture

Using the relation between () and derived from measurements at the three experimental sites, regional maps of surface volumetric soil moisture were obtained from the January and March SAR images. The maps of these two dates show a good contrast between regional soil moisture conditions:

  • 12 January: Due to recent snowmelt, the soil conditions at all three sites (and throughout the region) were near saturation.
  • 23 March: Due to an exceptionally dry Spring, the regional soil conditions were very dry.

surface soil moisture maps


Concluding Remarks

These preliminary results are encouraging, though not entirely conclusive. Despite the good relation between SAR backscatter () and volumetric soil moisture (), the overall sensitivity of the SAR signal to changes in soil moisture was low. The full set of ten ERS-2 SAR and Landsat TM images will allow further investigation of this SAR/optical approach for mapping regional soil moisture. The inclusion of a larger data set in this analysis will provide greater understanding of and confidence in the final results. Also, the forthcoming scenes will cover a period of increasing green vegetation at all three sites, and allow analysis of the use of optical data to normalize the effects of variations in green vegetation growth on the SAR signal.


Acknowledgements

We would like to acknowledge the valuable help we received from Wanmei Ni, Chandra Holifield, Ross Bryant and others in collecting the multitude of soil and vegetation samples. We also acknowledge financial support from NASA Mission to Planet Earth (MTPE) and the European Space Agency that made this work possible: NASA-S-41396-F, NASA NAGW-2425, NASA-W-18,997 and ESA-AO2.F115.


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