SALSA Poster:

MONITORING TEMPORAL SOIL MOISTURE VARIABILITY WITH DEPTH USING CALIBRATED IN-SITU SENSORS, Hymer et al.

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MONITORING TEMPORAL SOIL MOISTURE VARIABILITY WITH DEPTH USING CALIBRATED IN-SITU SENSORS

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Daniel C. Hymer (1), M. S. Moran (2) and T. O. Keefer (2)

1 University of Arizona, Department of Soil, Water and Environmental Science

2 USDA-ARS, Tucson, AZ

email: dhymer@tucson.ars.ag.gov


ABSTRACT

Soil moisture is a critical component of many regional and global climate studies. Unfortunately, long-term, spatially distributed soil moisture data sets are rare because conventional soil moisture instrumentation is point based and procedurally intensive. Electrical Resistance Sensors (ERS), however, are capable of collecting nearly continuous data using data-loggers with little maintenance and virtually no supervision. In this experiment, hourly ERS and intermittent Time Domain Reflectometer (TDR) measurements taken concurrently in 1990 and 1991 were used to develop a soil moisture data set for sensors located in the Walnut Gulch Experimental Watershed. Ultimately, these calibrations yielded a 16 month, hourly data set for sensors buried in six different trenches across the Lucky Hills subwatershed at 5, 15 and 30 cm depths. These data were then used to validate the one-dimensional Simultaneous Heat and Water (SHAW) model which simulates heat and water movement through plant cover, snow, residue and soil. Robust spatial and temporal characteristics of these data should provide important insights into rangeland management issues.


BACKGROUND

Soil moisture is a basic link between the hydrologic cycle and the energy budget of land surfaces. Therefore, soil moisture data sets are useful in many disciplines including agriculture, forest ecology, civil engineering, water resources, meteorology and soil science. In semiarid rangelands, soil moisture is a major control of evapotranspiration and a significant factor in runoff generation. Consequently, soil moisture is one primary component of many hydrologic models.

Unfortunately, long term soil moisture data sets are rare because conventional soil moisture measurement techniques (e.g., gravimetric and Time- Domain- Reflectometry) have historically been procedurally and labor intensive. Electrical Resistance Sensors, however, are capable of collecting nearly continuous data with little maintenance using data-loggers. Like most soil moisture instruments, ERS require a calibration to convert a measured signal to a volumetric water content. In this experiment, we calibrated a network of in situ ERS sensors in the Walnut Gulch Experimental Watershed to create a long term, temporally continuous soil moisture data set.


walnut gulch experimental watershed


RESEARCH OBJECTIVES

research objectives


lucky hills subwatershedMETHODS AND RESULTS

Eighteen pairs of ERS and TDR probes were installed horizontally into trench faces under three bare and three shrub covered surfaces in the Lucky Hills subwatershed at 5, 15 and 30 cm depths. Data loggers recorded hourly ERS values and Agricultural Research Service scientists collected TDR samples at varying time intervals. ERS readings were stored as a series of resistances (ohms) while TDR values were recorded as Volumetric Water Content () values (m3m-3).


ers/tdr calibrationERS and TDR measurements taken at identical times between August of 1990 and December of 1991 were extracted for individual trenches and depths. Calibration parameters for each ERS sensor were derived using the expression TDR = a ERSb, where a and b are calibrated parameters. Data presented in Figure 1 show a representative calibration curve with matched TDR and ERS values (R2= 0.88).

Parameters a and b were optimized with non-linear curve fitting techniques from a statistical software package. Once acceptable parameters were calculated for each sensor, the calibration expression was applied to the entire hourly ERS data set to produce 16 month, hourly . Coefficient of determination (R2) values for all 18 sensors ranged from 0.33 to 0.88. Statistical tests were also completed for the "b" parameter to ensure that a significant calibration relationship was established.


SHAW MODEL

The Simultaneous Heat and Water (SHAW) model is a detailed process model which simulates heat and water movement through a plant-residue-soil system. A vertical, one dimensional profile extending from the vegetation canopy to a specified depth within the soil is represented in this model. At various points in this vertical profile, nodes represent various canopy and soil layers. For each of these nodes, interrelated water, water vapor, heat and solute fluxes can be calculated. As demonstrated in a 1990 experiment in Walnut Gulch, the SHAW model was capable of simulating multi-species plant canopies; variable heat and water fluxes at grass and shrub dominated sites were simulated well (SHAW Model, Gerald Flerchinger, 1996).

In this experiment, we tested the ability of the SHAW model to simulate the calibrated ERS sensors at 5, 15 and 30 cm depths under bare and shrub covered surfaces between 1990 and 1991 (DOY 229-210). Preliminary results of this analysis are given in Table 2.

shaw model and ERS data

Mean SHAW model and observed ERS values are shown with their respective R2 values. Figure 2 shows the SHAW model simulations and ERS estimates of at 5 and 15 cm depths.

shaw model simulations 1

shaw model simulations 2

shaw model simulations 3

graph legend


CONCLUSIONS

These findings indicate that an in-situ calibration of ERS sensors that integrated high frequency ERS data with reliable TDR data worked well. An hourly soil moisture data set for a 16 month period was composed for 6 replicate sites at 3 different depths. This simple calibration procedure also demonstrates the utility of the ERS sensor for future soil moisture studies. Overall, the SHAW model provided a reasonable simulation of the calibrated ERS sensors. Future studies may focus on the calibration of the model to the ERS data sets.


ACKNOWLEDGMENTS

The authors would like to acknowledge Leslie Bach, Saud Amer, Bill Kustas, Gerald Flerchinger, the Water Conservation Laboratory (Phoenix, AZ) and the Tombstone field office staff for their efforts. This research was funded, in part, by an EOS grant (NASA NAGW-2425), a grant from the Landsat Science Team (NASA S-41396-F) and the Monsoon '90 project (IDP-88-086). Carl Unkrich, Scott Miller and Gary Richardson deserve thanks for their patience.


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