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Collecting real-time soil moisture profiles in the vadose zone C.M. Rose S.C. Armstrong J.L. Walker G.N. Young and J.C. Burton Environmental Research Division Argonne National Laboratory Argonne Illinois USA '"e?-.et;p\.-i..... L-* :kg \ - E '.&/ kz " OM I6 897 The submitted manuscript has been authored by a contractor of the U S Government under contract No W-31-19-ENG-38 Accordingly the U S Government retams a nonexclusiveroyalty-free license to publish or reproduce the published form of thls contribution or allow others to do so. for U S Government purposes ABSTRACT: The savings realized by using cone penetrometer (CPT) technology to supplement site characterizationwork are well documented. Adding soil moisture profiling to CPT testing can further enhance the interpretation of geologic and hydrogeologic conditions at a site. The performance Characteristics of three soil moisture probes ( S M p s ) used with direct-push technology were tested at a site in South Carolina. In the unsaturated zone all three probes predicted volumetric soil moisture within LS moisture units of the laboratory values more than 65% of the time. When the results were outside this range the difference was not large enough to lead to erroneous interpretations of the actual soil moisture trends. Results of testing in a variety of hydrogeologic conditions indicate that when SMPs are used with proper site calibration and controls each probe can predict soil moisture values within the unsaturated zone that closely match laboratory results in real time. 1 INTRODUCTION Soil moisture measurements are currently made on samples retrieved from a bore hole or test pit by using specific ASTM (American Society for Testing and Materials) methods in a geotechnical laboratory. The entire process can take days or even weeks. In addition the soil moisture content measured in the laboratory sometimes underestimates the actual moisture content of the soil because of drying of the sample during handling. Additional sampling is often required after the initial results are received. The purpose of this project was to evaluate in the field three SMPs developed for deployment with a CPT. The SMPs operate by using the soil's dielectric properties to predict the moisture content. A time domain reflectometry probe developed by Sandia National Laboratories and two frequency domain probes developed by Applied Research Associates ( A M ) and Conewel were used in the study. All three SMPs were easy to set up and install and each provided real-time data that were useful for immediate assessment of the subsurface moisture conditions in the vadose zone. Each SMP was to provide soil moisture data within +5 moisture units of the actual soil moisture as defined by using conventional ASTM standardized sample collection and analysis methods (ASTM 1964; Wilson 199). Three separate locations were selected at the U.S. Department of Energy's Savannah River Site in South Carolina to provide geologic and hydrogeologic variability between the evaluations of the SMPs. To provide control continuous soil samples were collected adjacent to each test site with conventional drilling techniques and then sent to a laboratory for geotechnical analysis. The SMPs were used in conjunction with conventional CPT technology that provided tip stress and sleeve friction parameters for further characterization of the subsurface conditions. Multiple soil moisture profiles were obtained around the borehole at each control location. 2 FIELDPROGRAM Three core holes (SBOL SB2 and SB3) were drilled at two different sites (TNX Area and M Area; Figure 1) with a hollow-stem auger. Soil samples were collected at each location with a 7.6-cm (3-in.) Shelby tube. The samples were handled stored and analyzed according to the ASTM procedures defined in Argonne's Test Plan (Argonne 1996a). Law Environmental's soil engineering laboratory analyzed the samples for grain size and volumetric soil moisture content. Data were collected with each of the three SMPs at minimum of two locations by pushing each sensor along the circumference of a circle 2.6-3.9 m (8-12 ft) in diameter around SBO1 SB2 or SB3.

DISCLAIMER This report was prepared as an account of work sponsored by an agency of the United States Government. Neither the United States Government nor any agency thereof nor any of their employees makes any warranty express or implied or assumes any legal liability or responsibility for the accuracy completeness or usefulness of any information apparatus product or process disclosed or represents that its use would not infringe privately owned rights. Reference herein to any specific commercial product process or service by trade name trademark manufacturer or otherwise does not necessarily constitute or imply its endorsement mommendation or favoring by the United States Government or any agency thereof. The views and opinions of authors expressed herein do not nccessarily state or reflect those of the United States Government or any agency thereof.

.. M Area Figure 1. Location of study area. Each S M P was coupled to a 4.4-cm (1.75-in.) electronic CPT that permitted the simultaneous acquisition of soil moisture and geotechnical data (tip stress sleeve friction and pore pressure) for each push. The ARA and Conewel SMPs recorded percent volumetric soil moisture resistivity and conductivity during the pushes. The Sandia S M P recorded percent volumetric soil moisture. For best results each S M P developer (ARA Sandia and Conewel) recommends site-specific calibration. Argonne further recommends that all CPT sensors always be used with site-specific

controls. However no site-specific information was available for the test site prior to the field evaluation Therefore each sensor was calibrated before deployment on the basis of standard laboratory readings (bucket tests) for sand or previous tests performed with the sensor. Each of the three sensors performed similarly in evaluating the volumetric moisture profile at each of the three core locations. Because of limited space the S M P data for only one of the three probes are presented here. The data presented are reasonably representative of all of the probes tested. SB2 SBOl - 583-1- -2-3 DISCUSSION To verify the sensors capabilities to characterize geology three continuous cores were collected from soil borings at two sites (TNX Area and M Area) to provide detailed geologic and soil moisture data. After volumetric soil moisture measurements were completed the Shelby tube was cut open and the core material was characterized. The sediments at the TNX Area and the M Area consist of interbedded fine sands silts and clays with clayey sands and sandy clays dominating the vadose zone (Figure 2). The sediments at the TNX Area were saturated at approximately 1.8-11.2 m (33-34 ft) below ground surface (BGS). Saturated sediments were not encountered at the M Area because of the greater depth of the water table. The lateral variability in the near-surface sediments was more pronounced at TNX Area whereas the M Area showed little lateral variability. Soil moisture probe data were collected by pushing each sensor to a depth of approximately 16.4 m (5 ft) BGS around soil borings SBOl and SB2. Because the water table at TNX began at 11. m (33.5 ft) BGS the probes effectiveness in both saturated and unsaturated conditions could be evaluated. At the M Area Slvip data were collected only in the vadose zone. Figure 3 shows the ratios of sand or silt to clay (as determined by the laboratory) resistivity plots for the CPT push of the ARA sensor and plots of the ARA sensor s volumetric moisture data with the +5 moisture unit error range (based on the laboratory volumetric moisture results) for SBO1 SB2 and SB3. The CPT resistivity measurements were taken to provide supplementary stratigraphic information (see Argonne 1996b for more details). In the vadose zone variability in soil moisture content is controlled primarily by geology. Moisture content is generally greater in soils containing a higher percentage of clay and or organic material. The volumetric moisture content in these clays and organic-rich soils can be > 3392 a value similar to -4 - -5- a sand silty sand clayey sand silty. clayey sand i 1 sandy clay cla ey sand wlt aggregate sand gravel L clay gravelly sand Figure 2. Geologic columns for soil boring locations SBO1 SB2 and SB3. that for saturated soils (Wierenga 1995). Conversely the soil moisture content in sandier soils is generally much lower often < 1%. Below the water table the distinction between the various types of geologic materials becomes uncertain. 4 RESULTS AND COMPARISON OF THE THREE SOIL MOISTURE PROBES The site installation setup and operation of each sensor proved to be quick and simple. All sensor data were collected by using the ASTM standard push rate

-5 - -1-15 - 3-21 : : 5-25 5 : 2-3! -35do- - -45-5 ~...-... O F Wn*- -5-1 -15-2 -25-3 -35-4 -45-5 I 5 1 IS 2 I 25-5 + -45 2 4wo 6 8 11 io -5-1 -1-2a -2-3 -3-4 -4 1 2 3 4 5-5 SaWSilt-Clay Ratio eo loo Resistivity (ohms-m) 2Mx) 4 Mxx) 6 5 1 15 2 25 3 35 4 Volumetric Moisture (%) 6 Figure 3. Ratios of sand or silt to clay resistivity data and volumetric moisture data for soil boring locations SBOl (top) SB2 (middle) and SB3 (bottom). Resistivity data are shown for two pushes. Volumetric moisture data are also shown for two pushes and the acceptable range (+5 moisture units from laboratory values) is indicated by the heavy lines.

of 2 c d s. The data were displayed in numeric form on the screen during the push. Each sensor was operated with software provided by the developer; a simple program was written in the field to merge each file with the CPT tip stress and sleeve friction data files. Plots of the final logs were produced within minutes of each completed push. The variability in volumetric soil moisture with respect to geology might be due in part to surface elevation differences and thickening or thinning of units over small spatial intervals at the site. In addition the laboratory volumetric moisture and grain size analyses were performed on discrete sections (15.2-25.4 cm [6-1 in.]) collected from soil cores whereas CPT sensor readings were collected continuously along the entire borehole. To evaluate the ability of the S M P to reasonably predict volumetric moisture content within the soil profile each.of the S M P profiles was plotted in conjunction with an error line of +5 volumetric moisture units. This margin of error was based on the laboratory soil moisture data. Evaluation of the ARA sensor showed that its volumetric moisture predictions generally agreed with laboratory data given the geologic differences between each sensor location and the control location as well as the geologic variability at each location (Figure 3). In the vadose zone at the TNX Area the S M P data fell well within the range of +5 volumetric moisture units established from the laboratory data. In the saturated zone discrepancies between the values predicted by the sensors and the laboratory data were more common with approximately 2-395 of the predicted data outside the acceptable range of -15 moisture units. Both sets of data follow the same trends predicting higher soil moisture values in the clayey material and lower values in the sandy units in the vadose zone. The data for the percent volumetric moisture collected at SB3 in the M Area (Figure 3) fell almost entirely within the acceptable range (k5moisture units). Evaluation of the Sandia sensor showed that its predicted percent volumetric moisture values generally agreed with the laboratory values for the vadose zone given the potential variability in geology at the TNX Area. However in the saturated zone values greater than 1% volumetric moisture were predicted falling outside the acceptable range 75% of the time. In the upper 9.8 m (3 ft) at the M Area the Sandia SMP predicted a volumetric moisture content slightly lower than the laboratory data2% of the time but the values matched almost perfectly at 9.8-16.4 m (3-5 ft) BGS. Evaluation of the Conewel sensor showed that within the vadose zone this sensor predicted a sediment moisture content lower than the laboratory data 8-37% of the time. For the saturated zone at the TNX Area moisture contents predicted were higher than the laboratory data. The Conewel SMP data fell outside the range of k5 moisture units 45-72% of the time and were in excess of the laboratory data by as much as 3-4%. In comparison to the laboratory data at M Area the Conewel SMP predicted a slightly lower volumetric moisture content 2-3% of the time and a higher moisture content only 3-7% of the time in the upper 13.8 m (42 ft). Below this level the probe predicted volumetric moisture contents below the range of rt5 moisture units. 5 CONCLUSIONS Each S M P profile followed the actual laboratory data trends at all three locations. The geologic units with higher clay contents had higher percent volumetric soil moisture values whereas geologic units in the vadose zone with higher sand contents had predictably lower volumetric soil moisture values. Beneath the water table clay units might not be distinguishable with the limited data provided by these tools. However used in combination with geologic data and the standard CPT measurements the SMP can make a substantial contribution to the geologichydrogeologic framework required for characterization of any site. Additional studies are needed to evaluate further the performance of SMPs in predicting soil moisture in a variety of hydrogeologic conditions. ACKNOWLEDGMENTS This work was supported by the U.S. Department of Energy Assistant Secretary for Environmental Management under contract W-3 1-19-Eng-38. REFERENCES Argonne 1996a. Experimental Test Plan: Soil Moisture Determinations Based on Dielectric Measurements Argonne Illinois: Applied Geosciences and Environmental Management Section Environmental Research Division Argonne National Laboratory. Argonne 1996b. Evaluation Report: Study of Three Soil Moisture Probes with Laboratory Sample Results Argonne Illinois: Applied Geosciences and Environmental Management Section Environmental Research Division Argonne National Laboratory. ASTM 1964. Thin-walled tube sampling of soils (ASTM D 1587) In ASTM Committee D-18 on Soils and Rocks for Engineering Purposes (ed.) Procedures for testing soils: 53-56. Philadelphia: American Society for Testing and Materials.

4 Wierenga P.J. 1995. Water and solute transport and storage. In C.G. Wilson. & C.G.Everett (eds.) Handbook of vadose zone characterization and monitoring:73. Ann Arbor: Lewis Publisher. Wilson L.G. 199. Methods for sampling fluids in the vadose zone. In D.M. Nielsen & A.I. Johnson (eds.) American Society for Testing and Materials ground water and vadose zone monitoring ASTM STP 153: 7-24. Philadelphia: American Society for Testing and Materials.

Report Number (14) @NL /E/? 1 bp-- - lo--- Publ. Date (11) Sponsor Code (1 8) I zr79 [ E qk x F DOE