Introduction
Infiltration is the process by which water on the ground surface enters the soil. Infiltration rate in soil science is a measure of the rate at which soil is able to absorb rainfall or irrigation. It is measured in inches per hour or millimeters per hour. The rate decreases as the soil becomes saturated. If the precipitation rate exceeds the infiltration rate, runoff will usually occur unless there is some physical barrier. It is related to the saturated hydraulic conductivity of the near-surface soil. The rate of infiltration can be measured using an infiltrometer.
Infiltration is governed by two forces: gravity and capillary action. While smaller pores offer greater resistance to gravity, very small pores pull water through capillary action in addition to and even against the force of gravity.
The rate of infiltration is determined by soil characteristics including ease of entry, storage capacity, and transmission rate through the soil. The soil texture and structure, vegetation types and cover, water content of the soil, soil temperature, and rainfall intensity all play a role in controlling infiltration rate and capacity. For example, coarse-grained sandy soils have large spaces between each grain and allow water to infiltrate quickly. Vegetation creates more porous soils by both protecting the soil from pounding rainfall, which can close natural gaps between soil particles, and loosening soil through root action. This is why forested areas have the highest infiltration rates of any vegetative types.
The top layer of leaf litter that is not decomposed protects the soil from the pounding action of rain; without this the soil can become far less permeable. In chaparral vegetated areas, the hydrophobic oils in the succulent leaves can be spread over the soil surface with fire, creating large areas of hydrophobic soil. Other conditions that can lower infiltration rates or block them include dry plant litter that resists re-wetting, or frost. If soil is saturated at the time of an intense freezing period, the soil can become a concrete frost on which almost no infiltration would occur. Over an entire watershed, there are likely to be gaps in the concrete frost or hygroscopic soil where water can infiltrate.
Once water has infiltrated the soil it remains in the soil, percolates down to the ground water table, or becomes part of the subsurface runoff process.
The process of infiltration can continue only if there is room available for additional water at the soil surface. The available volume for additional water in the soil depends on the porosity of the soil and the rate at which previously infiltrated water can move away from the surface through the soil. The maximum rate that water can enter a soil in a given condition is the infiltration capacity. If the arrival of the water at the soil surface is less than the infiltration capacity, is sometimes analyzed using hydrology transport models,mathematical models that consider infiltration, runoff and channel flow to predict river flow rates and stream water quality.
5.1.2 Infiltration characteristics
The infiltration capacity is the maximum rate at which water can be absorbed by a given soil per unit area under given conditions.
The infiltration capacity is the maximum rate at which water can be absorbed by a given soil per unit area under given conditions.
Infiltration regime i(t) depends on the supply
regime (irrigation, rain), but also on soil properties. The cumulative
infiltration I(t),
is the total amount of water infiltrated during a given period.
where:
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I(t)
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the cumulative infiltration during the
t period (mm)
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i(t)
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the infiltration regime during the t
period (mm/h)
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Hydraulic conductivity at
saturation ks,
is an essential parameter of infiltration. It represents the limiting value of
infiltration if the soil is saturated and homogenous. Percolation is the
vertical water flow in soils (porous unsaturated environment) on the
groundwater layer under the influence of gravity. This process follows
infiltration and has a major influence on the underground layer water supply.
Net rain is the amount of
rain that falls to the ground surface during a shower. The clear rain is
deduced from the total rain, diminished by the intercepted fraction of
vegetation and that which is stored in ground depressions. The difference
between the infiltrated rain and the drained rain on the ground surface is
called production function.
5.1.3 Factors which influence infiltration
The main factors that
influence the infiltration are:
- the
soil type (texture, structure, hydrodynamic characteristics). The soil
characteristics influence capillary forces and adsorption;
- the
soil coverage. Vegetation has positive influence on infiltration by
increasing the time of water penetration in soil;
- the
topography and morphology of slopes;
- the
flow supply (rain intensity, irrigation flow);
- the
initial condition of soil humidity. Soil humidity is an important factor
of infiltration regime. The infiltration regime evolves differently in
time for dry or wet soils;
- soil
compaction due to rain drop impact and other effects. The use of hard
agricultural equipment can have consequences on the surface layer of soil.
Figure 5.2 The
infiltration regime depending on time for different types of soil [Musy,2001]
5.2
Models Used to Estimate Infiltration Rates
Infiltration processes can be
estimated by means of different models:
- models
based on empirical relations involving 2, 3 or 4 parameters;
- physically
based models
Infiltration
Capacity
A soil under given condition has an upper limit on
its absorbing capacity. The infiltration capacity of a soil under given
condition is defined as the maximum rate at which it is capable of absorbing
water and is denoted by f. The actual
infiltration observed in a given soil fa
, will be equal to or less than its infiltration capacity f
depending on whether or not the rate of source supply is more or less
than the infiltration capacity. Specifically if i denotes the rate of rainfall, then
fa = f ,
i
f
and fa = i , if i
f
The information regarding the infiltration rates is required in
the estimation of surface runoff and groundwater recharge. Unfortunately f
is not a constant but varies within the duration of storm as well as
seasonally. The factors affecting the infiltration capacity are now discussed.
FACTORS
AFFECTING INFILTRATION CAPACITY
The variations in the infiltration capacity are
large. The infiltration capacity is influenced by many factors. Some factor
contribute to special variation while the others to temporal variation.
Depth of Surface Detention and Thickness of
Saturated layer. Infiltration takes place due to combined influences of gravity
and capillary forces. The infiltration of water through a soil surface may be
visualized as a flow through a large number of tiny pipes as in Figure below.
As the infiltration continues, the wet front will be
travelling downwards. At any instant of time the resistance to flow is proportional
to the thickness of the saturated layer up to wet front L. while the driving
head is proportional to (L + d), d being the depth of detention. At the beginning
of the process when L is either less than d or of comparable magnitude with d,
the resistance to flow is rather less and hence water enters rapidly. This is
one of the reasons why f is large at the beginning of the process.
When the thickness of saturated layer L becomes large and hence d becomes
negligible compared to L any increase in L produces same effect both on
resistance and driving head and so f remains constant. This suggest that the
infiltration capacity should decrease with time in a continuous rain and become
a constant, fc, ultimately
as shown figure below.
Soil
Moisture. If a soil is completel dry at the beginning of
rain here is a strong capillary attraction for moisture in the subsurface
layers that acts in the same direction as gravity and gives high initial value
of infiltration. As water percolates down, the surface layers become
semi-saturated and the capillary forces diminish and hence f also reduces. If the soil is moist to begin with, the
infiltration starts with lesser capacity compared to that of a dry soil. These
two trends are shown in figure above. Another aspect of soil moisture is that
when the soil is subjected to wetting, very wet soil particles called colloids wil swell slightly and reduce
the size of voids. This is another reason why f reduces with time.
Compaction.
The clay-surfaced soils are compacted even by the impact of rain drops which
reduce f. This effect is negligible
on sandy soils. Compaction not only reduces the porosity but also the pore
sizes. When the compaction is artificial due to man-made effect the initial
infiltration capacity is very low and it is further reduced during the storm.
Overgrazed pastures, playgrounds, and areas subjected to heavy vehicular
traffic will have less infiltration capacity. Clay soils when exposed dry to
the storm, apart from being compacted by the rain drop impact may become highly
impermeable because of the in wash of fine particles along with rain water into
the pores. This factor also reduces f
during the storm. High infiltration capacities produced by ploughing and cultivation,
burrowing animals and insects, and decay of vegetable matter such as root are
often reduced very rapidly by compaction due to rain.
Surface
Cover Conditions. The nature of surface cover has also
an important influence on the infiltration. The presence of a dense cover of
vegetation on the surface increase f.
The vegetative cover retards the movement of overland flow and causes high
depths of detention. It reduces the effect of rain drop compaction. It also
provides a layer of decaying organic matter which promotes the activity of
burrowing insects and animals. Transpiration by vegetation tends to keep the
soil moisture at low levels. All these factors tend to increase f.
Temperature.
The effect of temperature on filtration is explained through viscosity. The
flow through soil pores is by and large laminar for which the resistance is
direct proportional to viscosity. At high
temperatures since viscosity of water is low, high infiltration
capacities are expected. In winter months when low temperature prevails, the
infiltration capacity is also low. This is one of the factors responsible for
seasonal variations in f.
Other.
The other factors which may marginally affect the infiltration capacity include
the entrapped air in the pores, the quality of water, freezing, etc. The
presence of entrapped air increases the resistance to flow and therefore
reduces infiltration. The quality water, particularly its turbidity in terms of
clay and colloids it contains, and the salts it contains such as fertilizer residues
from alkaline soils or other sources, may have diminishing influence on
infiltration capacity.
MEASUREMENT
OF INFILTRATION
Infiltration
rates are required in many hydrologic problems such as runoff estimation, soil
moisture budgeting and in irrigation. There are two general approaches to the
determination of infiltration rate. One of these approaches analyses the
observed rainfall hyetograph and runoff hydrograph from a small plot or a
natural watershed to estimate the infiltration rates. The other method uses the
infiltrometers as shown the figure below.
The infiltrometer always gives the infiltration
capacity rate and the information from such infiltrometer tests at various
locations in the basin may give a satisfactory estimate of the average
infiltration capacity rate for the entire basin as a whole. In the hydrograph
analysis, method the actual infiltration rate curve is obtained. However, the
derived estimate of infiltration is as accurate as the precision of the
measurement of rainfall and runoff from the basin.
PHI
INDEX
Infiltration indexes generally assume that
infiltration occurs at some constant or average rate throughout a storm.
Consequently, initial rates are underestimated and final rates are overstated
if an entire storm sequence with little antecedent moisture is considered. The
best application is to large storms on wet soils or storms where infiltration
rates may be assumed to be relatively uniform.
The most common index is termed the phi (
) index for which the total volume of the
storm period loss is estimated and distributed uniformly across the storm
pattern. Then the volume of precipitation above the index line is equivalent to
the runoff (figure below). A variation is the W index, which excludes surface
storage and retention. Initial abstractions are often deducted from the early
storm period to exclude initial depression storage and wetting.
To
determine the
index for a given storm, the amount of
observed runoff is determined from the hydrograph, and the difference between
this quantity and the total gauged precipitation is then calculated. The volume
of loss (including the effects of interception, depression storage, and
infiltration) is distributed uniformly across the storm pattern as shown in
that figure.
Use of the
index for determining the amount of direct
runoff from a given storm pattern is essentially the reverse of this procedure.
Unfortunately, the
index determined from a single storm is not
generally applicable to other storms, and unless it is correlated with basin
parameters other than runoff, it is of little value.
Where, P = total rainfall / precipitation
(cm)
R
= Total runoff (cm)
te
= time of rainfall
Example :
A storm with 10cm rainfall produced a direct runoff of 5.8 cm.
Table below show the time distribution of the storm, estimate the
index.
Time
(hour)
|
1
|
2
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3
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4
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5
|
6
|
7
|
8
|
Rainfall
(cm/h)
|
0.4
|
0.9
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1.5
|
2.3
|
1.8
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1.6
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1.0
|
0.5
|
Solution :
Total rainfall, P =
0.4(1) + 0.9(1) + 1.5(1) + 2.3(1)
+ 1.8(1) + 1.6(1) + 1.0(1) + 0.5(1)
= 10 cm
Total runoff, R = 5.8 cm
Then ,
But this value of
makes the rainfall of the first hour and eight
hour ineffective as their magnitude is less than 0.525 cm/h. The value of te
is need to modified.
Then assume te is 6 hours.
Total rainfall, P = 10 – 0.4 – 0.5 = 9.1 cm
Then ,
This value of
is
satisfactory and by calculating the rainfall excess.
Time
(hour)
|
1
|
2
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3
|
4
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5
|
6
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7
|
8
|
Rainfall
(cm/h)
|
0
|
0.35
|
0.95
|
1.75
|
1.25
|
1.05
|
0.45
|
0
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Total
rainfall excess = 5.8 cm = total runoff
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