Joel M. Hubbell
United States Department of Energy
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Vadose Zone Journal | 2002
J. B. Sisson; Glendon W. Gee; Joel M. Hubbell; W. L. Bratton; J. C. Ritter; Anderson L. Ward; Todd G. Caldwell
Soil water pressures, measured over space and time, are needed to predict the direction of water flow and chemical transport in the vadose zone. Advanced tensiometers (ATs), which utilize a water-filled porous cup connected directly to a pressure transducer, can be installed at almost any location and depth using standard drilling techniques such as auger drilling, but these methods can significantly disturb the site. For sites where minimal disturbance is desired, alternate approaches for tensiometer placement have been sought. To test installation techniques and performance longevity, advanced tensiometers were placed into the ground at a test site near Richland, WA using two different installation methods, auger drilling and a drive-cone push technique. The tensiometers were subsequently monitored for nearly 2 yr without refilling or recalibration. The data indicated that tensiometers placed by the auger technique took several months to equilibrate, while the cone push units came to equilibrium within 24 h following their installation. Soil water pressures always remained above -90 cm pressure head (-90 mbar) at depths >90 cm. At the greatest depth (730 cm), positive then negative pressures were observed as the water table was lowered and the soil drained. The results suggest that for our test conditions (coarse sandy soil, no vegetation), soil water pressures stay well within the tensiometer range and unit gradient conditions persist, indicating a draining profile. Advanced tensiometers, placed either by auger or cone penetrometer, provide a robust and reliable method for long-term monitoring of soil water pressure profiles.
Vadose Zone Journal | 2004
Deborah L. McElroy; Joel M. Hubbell
Conceptual flow models provide a framework for predictive modeling of contaminant transport. This study tests the assumptions of steady-state flow and a unit hydraulic gradient in a 177-m-thick vadose zone beneath a mixed waste site, using a network of advanced tensiometers. The conceptual flow model at the waste site, located on the Idaho National Engineering Laboratory (INEEL), describes moisture movement through a geologically complex site comprising basalt flows intercalated with sedimentary interbeds. The presence of sedimentary interbeds is expected to dampen and store much of the episodic recharge, resulting in near steady-state conditions and unit gradient flow. Thirty advanced tensiometers in 18 wells provided field water potential data at depths ranging from 6.7 to 73.5 m below land surface (bls), beneath and adjacent to the waste site. Measured water potentials from February 2000 through August 2002 ranged from near saturation (−30 cm of water) to about −400 cm of water. Above 17 m, the observed long-term drying trends were presumed to be a response to the cumulative effect of lower than average annual precipitation for the last 3 yr (2000–2002). Below 17 m, steady-state conditions were observed at more than one-half of the monitored locations. However, long-term drying and wetting trends were also observed at 9 of the 25 monitored locations below 17 m, in contrast to the steady-state flow assumptions in the conceptual model. Long-term water potential changes ranged from about 20 to 200 cm of water. It is hypothesized that these drying trends are related to areas of focused infiltration, such as drainage ditches, and are a response to decreased runoff from three years of less than average precipitation. A unit gradient was indicated by aligning dispersed monitoring locations along a presumed vertical profile.
Vadose Zone Journal | 2004
Joel M. Hubbell; Michael J. Nicholl; James B. Sisson; D. L. McElroy
near-surface environment. Also, many of the complicating effects found in the near-surface environment will Approaches for estimating liquid flux in the shallow (0–2 m) vadose be damped or eliminated with increasing depth. For zone are hindered by the high degree of spatial and temporal variability present near the land surface. It is hypothesized that high-frequency these reasons, flux measurement at depth would appear variations in flux will be damped with depth. This study was conducted to be an attractive alternative at such sites. However, to estimate deep liquid flux using the Darcian approach at a waste borehole instruments for direct measurement of deep disposal site in south-central Idaho that is underlain by a complex flux do not exist at this time. Environmental tracers sequence of unsaturated basalt flows intercalated with thin sedimen(e.g., Scanlon et al., 1997; Phillips, 2001) may be used tary layers. Flux is estimated by combining in situ water potential to provide information on average historical flux at measurements from sedimentary interbeds located at depths of 34 some sites, but this approach is not conducive to moniand 73 m below land surface (bls) with laboratory estimates for the toring activities. Conversely, Darcian approaches will unsaturated hydraulic conductivity. Tensiometer data at seven locahave a more widespread applicability and are amenable tions indicated nearly constant conditions for 30 mo, while nine of to monitoring. the other 10 sites showed small gradual trends. Assumption of a unit hydraulic gradient led to flux estimates ranging from 0.2 to 10 000 cm Darcian approaches are founded on an assumption of yr 1. Estimates in the 34-m interbed ranged across four orders of one-dimensional vertical flow. One then needs sufficient magnitude while flux estimates for the 73-m interbed ranged three information on either the in situ moisture content or orders of magnitude. While the tensiometer data appear to reflect in water potential to calculate flux from laboratory-derived situ conditions and are a sensitive indicator of hydrologic conditions in unsaturated hydraulic conductivity. Previous applicathe deep vadose zone, the laboratory-developed hydraulic properties tions of this approach have used tensiometers (Stephens introduce a high degree of uncertainty, potentially affecting predicand Knowlton, 1986), thermocouple psychrometers tions by orders of magnitude. There is a need to develop techniques (Andraski, 1997), or heat dissipation sensors (Montazer for assessing flux rates for the range of applicable field conditions to et al., 1986) to measure water potential gradients along improve the confidence in deep flux estimates. boreholes at depths of 2, 5, and 200 m, respectively. Tensiometric data have a distinct advantage in that it is a direct measure of water potential, whereas the other F the transport of waterborne contamitwo methods are calibration-dependent, indirect meanants through the vadose zone requires estimates sures. Available techniques for in situ measurement of for liquid flux between the land surface and the water moisture content are not only calibration dependent, table. While there is an extensive body of literature but also physically difficult to install at depths beyond regarding the estimation of flux at shallow depths, the a few meters. deeper vadose zone has received much less attention. Conventional tensiometers require a continuous waInstruments used for direct measurement of flux in the ter column that extends from the measurement point near-surface environment (0–2 m) include pan lysimeto the sensor location at or near the land surface. The ters (e.g., Jordan, 1968), tension lysimeters (Byre et al., vaporization of water in the water column limits the 1999), and vadose zone flux meters (Wagenet, 1986; depth of emplacement to about 8 m and has precluded Gee et al., 2002). There are also Darcian approaches in the use of tensiometer data for Darcian estimates of which shallow measurements of moisture content or flux below that depth. This problem was recently overwater potential ( ) are combined with laboratory develcome by development of the advanced tensiometer oped relations for the unsaturated hydraulic conductiv(Hubbell and Sisson, 1998), which has been successfully ity to estimate flux (Stephens and Knowlton, 1986). deployed to make direct measurements of water potenHowever, the utility of all such measurements is limited tial at depths up to 145 m. The advanced tensiometer has by the inherent spatial and temporal variability of flux two parts, a permanently installed porous cup assembly in the shallow vadose zone (Wagenet, 1986). with casing that extends to land surface and a removable At sites with thick vadose zones, flux estimates obelectronic pressure transducer assembly for installation tained at depth may be more representative of mass from land surface. Positioning the sensor close to the transfer to the water table than those obtained from the measurement point (porous cup) eliminates the need for a water column extending to land surface, thus reJ.M. Hubbell, J.B. Sisson (ret.), and D.L. McElroy, Idaho National moving the restriction on depth of emplacement. Engineering and Environmental Laboratory, Geosciences Research Here, we present a first attempt to estimate flux at Department, P.O. Box 1625, MS 2107, Idaho Falls ID 83415; M.J. Nicholl, Geosciences Dep., Univ. of Nevada, Las Vegas, NV 89122. depth using long-term monitoring data obtained from Received 10 July 2003. Special Section: Uncertainty in Vadose Zone the deployment of advanced tensiometers. Instruments Flow and Transport Properties. *Corresponding author (jmh@ inel.gov). Abbreviations: bls, below land surface; ESRP, Eastern Snake River Plain; INEEL, Idaho National Engineering and Environmental LaboPublished in Vadose Zone Journal 3:560–569 (2004). Soil Science Society of America ratory; RWMC, Radioactive Waste Management Complex; SDA, Subsurface Disposal Area. 677 S. Segoe Rd., Madison, WI 53711 USA
Archive | 2003
Glendon W. Gee; Anderson L. Ward; James B. Sisson; Joel M. Hubbell; David A. Myers; Harold A. Sydnor
Hydrologic characterization of the vadose zone (from soil surface to the underlying water table) is needed to assess contaminant migration from buried wastes. The Pacific Northwest National Laboratory, under contract with the U. S. Department of Energys EM-50 (Subsurface Contamination Focus Area), and in collaboration with CH2MHILL Hanford Group, the Idaho National Engineering and Environmental Laboratory (INEEL), and Duratek Federal Services (DFS), deployed a suite of vadose-zone instruments at the Hanford Site near Richland, Washington. Several new instruments were tested.
Vadose Zone Journal | 2004
Joel M. Hubbell; James B. Sisson; Michael J. Nicholl; R. G. Taylor
Barometric pressure fluctuations may influence measured water levels in wells where thick vadose zones or low permeability materials overlie unconfined aquifers. Here, we present a well completion method designed to reduce the effects of barometric pressure fluctuations on measured water levels. This well configuration, called the isobaric well, seals the interior of the well from atmospheric pressure, and vents the reference side of the water level pressure transducer to the gas phase pressure above the water table. We tested the isobaric design on a well completed about 180 m below land surface in the Eastern Snake River Plain aquifer at the Idaho National Engineering and Environmental Laboratory. Water level data collected during 14 mo show more than an order of magnitude decrease in diurnal fluctuations when the well was operated in the isobaric mode. Decreasing the noise level allowed clear definition of water level trends that would otherwise have been at least partially obscured by barometric fluctuations. This well configuration allows direct monitoring of water level changes, without the need to rely on postprocessing to mitigate barometric influences.
Archive | 1997
Joel M. Hubbell; Earl D. Mattson; James B. Sisson
Archive | 1995
James B. Sisson; Thomas K. Honeycutt; Joel M. Hubbell
Archive | 2004
Don T. Clark; Richard L. Jones; Terry D. Turner; Joel M. Hubbell; James B. Sisson
Archive | 2001
Joel M. Hubbell; James B. Sisson
Archive | 1996
Joel M. Hubbell; Allan Wylie