Soil erosion potential is increased if the soil has no or very little
vegetative cover of plants and/or crop residues. Plant and residue cov-
er protects the soil from raindrop impact and splash, tends to slow
down the movement of surface runoff and allows excess surface water
to infiltrate.
Wind erosion less common, but again takes place after vegetation
has been lost and when soil particles are loosened. Early signs of wind
erosion include deposition of sand particles around plants and micro-
ripples on the surface of exposed areas. The final extreme is the clas-
sic sand desert dune structures. The lack of windbreaks (trees, shrubs,
residue, etc.) allows the wind to put soil
particles into motion for
greater distances thus increasing the abrasion and soil erosion. Knolls
are usually exposed and suffer the most.
Sheet erosion is the most common form of erosion. Unprotected
soil particles are loosened by trampling, through wind erosion and by
the impact of rainfall. The soil particles are then transported by rain-
water surface flow to the river and stream systems. Sheet erosion is
characterized by a general lowering of the soil level, leaving raised
pedestals where the root mass of the remaining vegetation protects it.
Sheet erosion is soil movement from raindrop splash resulting in the
breakdown of soil surface structure and surface runoff; it occurs rather
uniformly over the slope and may go unnoticed
until most of the pro-
ductive topsoil has been lost.
Rill erosion results when surface runoff concentrates forming small
yet well-defined channels. These channels are called rills when they
are small enough to not interfere with field machinery operations. The
same eroded channels are known as gullies when they become a nui-
sance factor in normal tillage.
Gully erosion is the most obvious and dramatic demonstration of
erosion, although in most areas actually less significant in terms of to-
tal land degradation. Gully erosion rarely occurs without sheet ero-
sion. It can also be triggered by erosion along livestock tracks, foot-
paths and road edges. The process can start with "rills" and end up
with gullies that are tens of meters deep.
There are farms that are loosing large quantities of topsoil and sub-
soil each year due to fully erosion. Surface runoff, causing gull forma-
tion or the enlarging of existing gullies, is usually the result of im-
proper outlet design for local surface and subsurface drainage systems.
159
The soil
instability of fully banks, usually associated with seepage of
ground water, leads to sloughing and slumping of bank slopes. Such
failures usually occur during spring months when the soil water condi-
tions are most conductive to the problem. Poor construction, or inade-
quate maintenance, of surface drainage systems, uncontrolled live-
stock access, and cropping too close to both stream banks has led to
bank erosion problems.
The effects of soil erosion are complex. Some of the impacts may
appear to be reversible by suitable soil conservation programmes and
improving cultivation practices, whereas there are other types of deg-
radation which are irreversible. The latter
type includes land lost by
gulling, or cases of severe sheet erosion where the soil cover has been
removed to a great extent. In cases where degradation is reversible it
is generally difficult to assess the actual extent and impact of land de-
gradation as farmers do convert their land to less demanding uses or
increase the level of inputs. Methodologies for prediction of soil ero-
sion have been developed since the early thirties.
Many farmers have already made significant progress in dealing
with soil erosion problems on their farms. However, because of con-
tinued advances in soil management and crop production technology
that have maintained or increased yields in spite of soil erosion, others
have not been aware of the increasing problem on farmland. Aware-
ness usually occurs only when property is damaged and productive ar-
eas of soil are lost.
Certain conservation measures can reduce
soil erosion by both wa-
ter and wind. Tillage and cropping practices, as well as land manage-
ment practices, directly affect the overall soil erosion problem and so-
lutions on a farm. When crop rotation or changing tillage practices are
not enough to control erosion on a field a combination of approaches
or more extreme measures might be necessary. For example, contour
plowing, strip cropping, or terracing may be considered.
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