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Hydraulic Conductivity Measurement
Hydraulic conductivity (K) defines the rate of movement of water through a porous medium such as a soil or aquifer. It is the constant of proportionality in Darcy’s Law and as such is defined as the flow volume per unit cross-sectional area of porous medium under the influence of a unit hydraulic gradient. This translates to SI units of m3/m2/day or m/d, but other measurement units are commonly used (Table 1)
| Description | metres/day (m/d) | metres/second (m/s) | millimetres/day (mm/d) | millimetres/hour (mm/hr) |
|---|---|---|---|---|
| Extremely slow | 0.000001 | 1.5741x10-11 | 0.001 | 0.000041667 |
| Very Slow | 0.0001 | 1.5741x10-9 | 0.1 | 0.0041667 |
| Slow | 0.01 | 1.5741x10-7 | 10 | 0.41667 |
| Moderate | 1 | 1.5741x10-5 | 1000 | 41.667 |
| Fast | 10 | 1.5741x10-4 | 10000 | 416.667 |
| Very Fast | 100 | 1.5741x10-3 | 100000 | 4166.667 |
Measurement of hydraulic conductivity is problematic, considering the parameter can differ over several orders of magnitude across the spectrum of sediments and rock types, as indicated in Table 2. The parameter can also vary markedly in space, even with apparently minor changes in sediment characteristics. Hydraulic conductivity is influenced by the properties of the fluid being transmitted (such as viscosity) as well as the porous medium. Hydraulic conductivity is also scale dependent, so that measurements taken at the core sample level may not be directly extrapolated to the aquifer scale. It is also direction dependent, so that hydraulic conductivity can be markedly different in the vertical from the horizontal. Hydraulic conductivity cannot be directly measured but inferred from field, laboratory or modelled data.
| Rock Type | Grain size (mm) | Hydraulic Conductivity K (m/d) |
|---|---|---|
| Clay | 0.0005-0.002 | 10-8-10-2 |
| Silt | 0.002-0.06 | 10-2 - 1 |
| Fine Sand | 0.06 -0.25 | 1-5 |
| Medium Sand | 0.25-0.50 | 5-20 |
| Coarse Sand | 0.50-2 | 20-100 |
| Gravel | 2-64 | 100-1000 |
| Shale | small | 5x10-8 - 5x10-6 |
| Sandstone | medium | 10-3-1 |
| Limestone | variable | 10-5-1 |
| Basalt | small | 0.0003-3 |
| Granite | large | 0.0003-0.03 |
| Slate | small | 10-8-10-5 |
| Schist | medium | 10-7-10-4 |
Different approaches have been taken to estimate hydraulic conductivity, including:
Using seepage meters which directly measure the flux (Q) at the interface between the surface water feature and the aquifer. The basic method is to isolate part of the sediment-water interface with a chamber open at the base (with surface area A) and measure the change in water volume contained in a bag attached to the chamber over a measured time period. When combined with head gradient measurements (dh/dl) between the sediment bed and the surface water body from minipiezometers (Lee & Cherry, 1978), the vertical hydraulic conductivity can be derived from Darcy’s Law:
(Equation 1)
- Infiltration Tests, where infiltrometers (also known as permeameters) are used to measure the rate that water can infiltrate downwards through the sediment/soil profile which is a function of vertical hydraulic conductivity. Two basic methods can be employed. In falling-head tests water is added to reach a target level in the infiltrometer, after which the subsequent decline in water level is recorded as infiltration occurs. In constant-head tests, the target level is maintained during the test duration by adding increments of water of known volume. These tests are commonly used for unsaturated soils, but can also be carried out in calm, shallow water bodies (McMahon et al, 1995; Duwelius 1996; Lindgren & Landon, 2000; Rosenberry 2000). Various instruments are available that are based on measuring infiltration, including well, disc and ring (double and single) permeameters (ANCID, 2000). Similar tests using constant-head or falling-head configurations can be undertaken in the laboratory on core samples taken from the field site.
- Pump Tests, involving pumping groundwater from the piezometer and monitoring the pumping rate, as well as the groundwater level in the piezometer or in nearby piezometers. The pump test (also called aquifer test) indicates how the aquifer responds to groundwater withdrawals, with the data used to estimate aquifer characteristics such as hydraulic conductivity. A wide variety of formulas are available for the analysis of pump test data, based on differences in aquifer type and geometry, boundary conditions, and underlying assumptions. Slug Tests are particular tests where the rate of groundwater recovery is measured after a small volume (slug) of water is suddenly displaced (Duwelius 1996; Cey et al, 1998; Springer et al; 1999).
Grainsize analysis, involving determining the distribution of grainsizes within the sediment using standard sieves. Empirical relationships are used to estimate hydraulic conductivity from standard grainsize parameters (Vukovic & Soro, 1992). The grainsize diameter at which 10% of the sediment is finer (d10) is applied in a commonly used empirical formula, initially developed by Hazen (1893):
(Equation 2)
where AH is a dimension coefficient (= 1.0 for m/d), C is an empirical constant (=860) and T is a temperature correction factor (=1 at 10° C). Another empirical relationship developed by Alayamani & Sen (1993) uses the slope and intercept (I0) of the grainsize distribution curve between d10and the median grainsize (d50):
(Equation 3)
References
- Alayamani MS, Sen Z, 1993. Determination of hydraulic conductivity from complete grain-size distribution curves. Ground Water 31 (4) 551-555.
- ANCID, 2000. Open channel seepage and control. Vol 1.1 Literature review of channel seepage identification and measurement. Australian National Committee on Irrigation and Drainage. Prepared by Sinclair Knight Merz.
- Brassington R, 1988. Field Hydrogeology. Geological Society of London Handbook Series. Open University Press.
- Cey EE, Rudolph DL, Parkin GW and Aravena R, 1998. Quantifying groundwater discharge to a small perennial stream in southern Ontario, Canada. Journal of Hydrology 210:21-37.
- Duwelius RF, 1996. Hydraulic conductivity of the streambed, East Branch Grand Calumet River, Northern Lake County, Indiana. US Geological Survey Water-Resources Investigations Report 96-4218.
- Hazen A, 1893. Some physical properties of sands and gravels. Massachusetts State Board of Health, 24
th Annual Report. - Lee DR and Cherry JA, 1978. A field exercise on groundwater flow using seepage meters and mini-piezometers. Journal of Geological Education 27:6-10.
- Lindgren RJ, Landon MK, 2000. Effects of ground-water withdrawals on the Rock River and associated valley aquifer, Eastern Rock County, Minnesota. US Geological Survey Water-Resources Investigation Report 99-4157.
- McMahon PB, Tindall JA, Collins JA, Hull KJ, Nuttle JR, 1995. Hydrologic and geochemical effects on oxygen uptake in bottom sediments of an effluent-dominated river. Water Resources Research 31(10) 2561-2569.
- Rosenberry DO, 2000. Unsaturated-zone wedge beneath a large natural lake. Water Resources Research 36(12) 3401-3409.
- Springer AE, Petroutson WD, Semmens BA; 1999. Spatial and temporal variability of hydraulic conductivity in active reattachment bars of the Colorado River, Grand Canyon. Ground Water 37(3) 338-344.
- Vukovic M, Soro A, 1992. Determination of hydraulic conductivity of porous media from grain-size composition. Water Resources Publications, Littleton, Colorado