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Transactions of the ASABE | 1983

The Pit Bailing Method for Hydraulic Conductivity Measurement of Isotropic or Anisotropic Soil

Herman Bouwer; R. C. Rice

ABSTRACT WITH the pit bailing technique, a hole is dug (normally with a backhoe) to below the groundwater table. After equilibration, the water level in the pit is rapidly (instantaneously) lowered and the subsequent rise of the water level is measured for calculation of the hydraulic conductivity K around the pit. The pit bailing technique was originally developed for septic tank leach field design. However, the method is also useful for in-situ measurement of K for other purposes. This is particularly true for stony soils, where augerhole and other methods are difficult and often fail. Another advantage of the pit method is that the volume of soil on which K is determined is larger than for the augerhole and piezometer methods. The equation originally given for the pit method was based on the Thiem formula, which limited the method to situations where the pit bottom was at or close to the impermeable layer. The geometry of the flow system for the pit method, however, is similar to that for the piezometer method if the water table coincides with the top of the piezometer cavity. Thus, the equation for the piezometer method can also be used for the pit method. This extends the applicability of the pit method to partially penetrating pits in soils that are underlain by either impermeable or very (inifinitely) permeable material. Geometry factors for the piezometer method presented by Youngs were extrapolated to the case where the static water table coincides with the top of the cavity. The resulting values then can be used for the pit method. The validity of this approach was demonstrated in a large sand tank where the average K-value yielded by pit-bailing tests on holes of various diameters and depths was 31 m/day as compared to an average value of 37 m/day obtained with one-dimensional and seepage meter methods. In anisotropic soils, K in horizontal and vertical direction can be calculated from the K values obtained from two pits with different geometries.


Ground Water Monitoring and Remediation | 2004

Do Pharmaceuticals, Pathogens, and Other Organic Waste Water Compounds Persist When Waste Water Is Used for Recharge?

Gail E. Cordy; Norma L. Duran; Herman Bouwer; R. C. Rice; Edward T. Furlong; Steven D. Zaugg; Michael T. Meyer; Larry B. Barber; Dana W. Kolpin


Archive | 1992

Self-aligning optical transceiver

R. C. Rice


Journal of Water Pollution Control Federation | 1984

Renovation of wastewater at the 23nd avenue rapid infiltration project

Herman Bouwer; R. C. Rice


Journal of Irrigation and Drainage Engineering-asce | 1989

Effect of water depth in groundwater recharge basins on infiltration

Herman Bouwer; R. C. Rice


Archive | 1983

Combination tool chest dolly and leaved workbench

R. C. Rice


Soil Science Society of America Journal | 1964

Simplified Procedure for Calculation of Hydraulic Conductivity with the Double-Tube Method 1

Herman Bouwer; R. C. Rice


Transactions of the American Society of Civil Engineers | 1963

Effect of Velocity on Seepage and its Measurement

Herman Bouwer; L. E. Myers; R. C. Rice


Soil Science Society of America Journal | 1967

Modified Tube Diameters for the Double-Tube Apparatus 1

Herman Bouwer; R. C. Rice


Water Resources Research | 1980

Reply [to “Comment on ‘Delayed aquifer yield as a phenomenon of delayed air entry’ by Herman Bouwer and R. C. Rice”]

Herman Bouwer; R. C. Rice

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Herman Bouwer

United States Department of Agriculture

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Gail E. Cordy

United States Geological Survey

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Larry B. Barber

United States Geological Survey

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Michael T. Meyer

United States Geological Survey

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Norma L. Duran

United States Environmental Protection Agency

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