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Single
ring infiltrometer; in action. |
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Single
ring infiltrometer; finished. |
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Principles:
Known
boundary and pressure conditions are used to determine the unrestricted
3-dimensional infiltration capacity, of a soil confined below the
single, steel ring. The ability for the soil to transmit water (be
permeable) is hence determined through steady state calculations
and, this Saturated Hydraulic Conductivity (Ksat), which is universally
used as an empirical constant to quantify specific, soil-water flow
and infiltration capacity problems. Ksat “is one of the most
important factors playing a role in many agronomic, engineering
and environmental activities” (Herman et al, 2003) and hence,
is a useful term to quantify.
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Methods:
A single
steel ring with dimensions (20cm diameter and 17cm tall) is inserted
2cm into the soil surface.
It
is with 2L of fresh water by sealing with a plastic sheet, pouring
the water over the plastic and pulling the plastic slowly.
The
initial height is measured once all the water is released and time
initiated.
Further
water level (height) measurements are taken at 15-second intervals
for the first few minutes and, after 2 minutes another 15 seconds
is added to the interval period (subject to intensity of infiltration;
figure 2).
This
process is continued until all the water has infiltrated or a steady
state rate is recognisable.
The
single ring infiltrometer was used at all 10 sites within the study
area and at the soil pit.
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Filling ring with water and taking initial measurement. |
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Method
for taking continuous height measurements. |
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Analysis:
Analysis
is completed in the JMP5.1 statistical analysis program.
For
each individual site, the x,y distribution of time against cumulative
infiltration is displayed, so that the point steady state infiltration
can be visually determined.
A line
is then fitted along the steady state portion of the graph. Within
the resulting linear equation, the gradient is equated as the soil-water
flux (q).
Using
q = Ksat.{(C/G.pi.r)+1} the Ksat (mm/h)
of the soil can be determined as all other components are known
or estimated.
q = statistically determined (cm/min)
C
= wetting front potetenial (estimated for clays at 150 cm)
G
= shape factor for infiltration (0.8456)
pi
= 3.1415...
r
= radius of ring (10cm)
An
example is shown in figure 3, with the steady state infiltration
represent by the red, fitted line and nearby equation. The gradient
and hence, q = 0.0025 (cm/sec) which, is then inserted in the above
equation to compute the Ksat, as summarised below in the results
section.
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JMP
5.1 output for analysis of C1, linear equation sited (note the
exclusion of points not in a steady state of infiltration, the red
line represent the steady state function).
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Results
and Discussion:
A comparison
of Ksat values for land use concludes that soil under pasture has
a characteristically higher Ksat value as shown be the distribution
of values and the summarized data, to the right and below, respectively.
Hence,
it is extrapolated that pasture soils have a higher ability to transmit
water within the soil profile. This is due to the interaction of
a number of soil physical and hydrological factors. Soil under pasture
is more stable and less likely to slake and disaggregate and therefore,
not restrict water movement. More so, there is also a greater chance
of plant roots and macro pores promoting infiltration, because of
the pastures greater soil structure.
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Distribution
of Ksat values as a function of 0.land use. |
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The
soil pit Ksats, although, positioned within a vacant pasture were
low primarily due to them being placed on a platform almost 1m within
the soil profile. These sites were either picked back and left rough
(Pit: site A) or smoothed over (Pit: site B) and hence, had low
and differing Ksat results evident in the table below. This introduced
the effect of surface condition as the two methods of leveling the
soil, resulted in varying Ksat values.
Summary
of results for single ring infiltrometer.
Site |
q
(mm/h) |
Ksat
(mm/h) |
| C1 |
1.25 |
13.00 |
| C2 |
1.25 |
13.54 |
| C3 |
1.08 |
9.75 |
| C4 |
0.48 |
4.33 |
| C5 |
3.12 |
28.17 |
| P1 |
64.02 |
577.93 |
| P2 |
2.40 |
21.67 |
| P3 |
5.55 |
50.10 |
| P4 |
2.55 |
23.02 |
| P5 |
18.0 |
162.49 |
| Pit:
site A |
0.13 |
1.14 |
| Pit:
Site B |
0.10 |
0.91 |
The
extreme outlier at P1 is distracting, however could simply be put
to a large crack in the profile or an incorrect experimental practice,
resulting in the rapid infiltration or loss of water.
In
conclusion , single ring infiltrometers in conjunction with Darcian
flow equations are very important in water management issues; in
regards to irrigation, contaminant and solute movement. Flow can
inexpensively be quantified and useful parameters (Ksat and flow
fluxes) can be deduced, which expand the usefulness of single ring
infiltrometers (Wu, 1998).
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Problems:
Single ring infiltrometers measures all dimensions of flow, as represented
below and therefore, has limited applications as vertical flow is
the critical flow concerning agriculturalists and environmentalists.

Infiltration
is influenced by ring size, ring insertion depth and soil type,
therefore the process is site specific and limited accordingly (Wu
and Osten).
Ksat calculations are highly sensitive to sample size, flow geometry,
sample collection procedures and soil physical-hydrological properties
such as clay content and mineralogy and therefore have many areas
for error during calculation. (Herman et al, 2003).
Conceptual 3-D wetting front.
The
falling head technique is limited by 2L volume of water, and therefore
sometimes does not indicate a steady state, which is needed for
subsequent analysis.
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References:
Herman,
S., Mertens, J., Timmerman, A., and Feyen, J. 2003. Comparison of
tension infiltrometer, single-ring pressure infiltrometer and soil
core Ksat estimates on a sandy loam hill slope. Geophysical Research
Abstracts, Vol. 5, 02662, 2003.
Wu, L. 1998.
New method developed to measure the vertical infiltration capacity
of soils using single ring infiltrometers. Soil Water and Irrigation
Management, University of California. http://esce.ucr.edu/soilwater/news.htm#New%20Method
Wu,
L., and Oster, J. Instrument for Plant and Water Management. Department
of Soil and Environmental Sciences, University of California. http://esce.ucr.edu/WU/CETRAIN.html
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