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Soil erosion
The wearing away of the land surface by running water, wind, ice, or other geological agents, including such processes as gravitational creep and landslide.
Loss of soil through the action of water, wind, or gravity.
Identified by World Bank (1989) as the Philippines’ worst environmental problem.
ON-SITE IMPACTS OF SOIL EROSION
Reduction in soil depth
Structure deterioration (Reduction in water infiltration and increase of water runoff)
Nutrient loss
Decline in soil fertility
Loss of production
Decline in soil biota
OFF-SITE IMPACTS OF SOIL EROSION
Flooding (Sfeir-Younis and Dragun 1993)
Sedimentation of the irrigation system (PCARRD 1991b) and water reservoir (Cruz, W. et al 1988b)
Reduced hydroelectric output, reduction of productive life of hydroelectric dams
Destruction of coral reefs (Kummer 1992a; PCARRD 1991b; World Bank 1989)
Geological erosion
Accelerated erosion
GENERAL TYPES OF SOIL EROSION (2)
GEOLOGICAL EROSION
Wearing away of the earth’s surface by water or other natural agents under natural environmental conditions of climate, vegetation, and so on, undisturbed by man.
ACCELERATED EROSION
Erosion much more rapid than normal, natural, geological erosion; primarily a result of the activities of humans or, in some cases, of animals. This is often 10 to 1,000 times as destructive as geological erosion, especially on sloping lands in regions of high rainfall.
DETACHMENT OF SOIL PARTICLES FROM THE SOIL MASS
TRANSPORT/ENTRAINMENT OF THE DETACHED PARTICLES DOWNHILL BY FLOATING, ROLLING, DRAGGING, AND SPLASHING
DEPOSITION OF THE TRANSPORTED PARTICLES AT SOME PLACE LOWER IN ELEVATION
Process of soil erosion: (3)
≈6-8 inches
The most versatile part of the soil
An inch of soil requires thousands of years to develop but can easily be lost overnight
DETACHMENT OF SOIL PARTICLES FROM THE SOIL MASS
Rainfall – most important detachment agent
Detachment-limited erosion – eroding agents have the capacity to transport more material than is supplied by detachment
TRANSPORT/ENTRAINMENT OF THE DETACHED PARTICLES DOWNHILL BY FLOATING, ROLLING, DRAGGING, AND SPLASHING
Transport-limited erosion – more material is supplied than can be transported
DEPOSITION OF THE TRANSPORTED PARTICLES AT SOME PLACE LOWER IN ELEVATION
Occurs when sufficient energy is no longer available to transport the particles.
It detaches soil.
It destroys granulation.
Its splash, under certain conditions, causes an appreciable transportation of soil.
RAINDROP IMPACT EXERTS THREE IMPORTANT EFFECTS:
Influence of raindrops
When raindrops impact on a wet soil surface, they detach soil particles and send them flying in all directions.
A very heavy rain may splash as much as 225 Mg/ha of soil.
Some of the particles splash as much as 0.7 m vertically and 2 m horizontally.
Influence of raindrops
IMPACT OF RAINDROPS AT 30KM/H.
PARTICLES ARE SEPARATED DUE TO BEATING OF RAINDROPS.
SURFACE SOIL PORES FILLED WITH SOIL PARTICLES, REDUCING INFILTRATION.
SURFACE FLOW BEGINS DUE TO LACK OF INFILTRATION.
Sheet erosion
Rill erosion
Gully erosion
SPECIFIC KINDS OF SOIL EROSION (BY WATER) (3)
Sheet erosion
The removal of a fairly uniform layer of soil from the land surface by runoff water.
Rill erosion
Numerous small channels of only several centimeters in depth are formed.
Occurs mainly on recently cultivated soils.
Gully erosion
Water accumulates in narrow channels and, over short periods, removes the soil from this narrow area to considerable depths, ranging from 0.3-0.6 m to as much as 23-30 m.
Erosivity
Erodibility
Slope
Plant cover
Human activities
FACTORS INFLUENCING SOIL EROSION (5)
Erosivity
FOR RAINFALL, IT IS A FUNCTION OF:
➥ Intensity
➥ Duration
➥ Mass of raindrop
➥ Diameter of raindrop
➥ Velocity of raindrop
Erodibility
Large particles are resistant to transport because of the greater force required to entrain/transport them
➥ Fine particles are resistant to detachment because of their cohesiveness
↝ Silts and fine sands – least resistant particles
↝ Soils with 40-60% silt content are the most susceptible
Slope
Function of slope length and slope steepness (angle/gradient)
Slope length – the distance from the point of flow to the point of runoff
For short slopes, the rate increase in soil loss rises rapidly, but for long slopes, the rate of increase is very small. There is a limit to the length of a slope that will influence soil loss
As slope steepness increases, soil loss rate also rises at an increasing rate.
When soil slope exceeds a critical steepness, rill erosion begins, which causes total soil loss to increase rapidly.
Plant cover
The greatest deterrent to soil erosion is cover.
The major role of vegetation in reducing erosion is in the interception of the raindrops so that their kinetic energy is dissipated rather than imparted to the soil.
Under certain conditions, a plant cover can exacerbate erosion. Raindrops intercepted by the canopy may coalesce on the leaves to form larger drops which are more erosive
Overall, forests are the most efficient (usually with dense ground litter), but a dense growth of grass maybe almost as efficient.
Human activities
Reduction of vegetation cover
↝ Tillage (for crop production)
↝ Burning
↝ Overgrazing
↝ Mining
↝ Logging
↝ Road construction
A = 0.224.R.K.L.S.C.P
The most widely used tool to estimate erosion is the Universal Soil Loss Equation (USLE)
A
ESTIMATED ANNUAL SOIL LOSS PER UNIT AREA (T/HA/YR)
R
THE RAINFALL EROSIVITY FACTOR
K
THE SOIL ERODIBILITY FACTOR
L
THE SLOPE LENGTH FACTOR
S
THE SLOPE GRADIENT FACTOR
C
THE CROPPING MANAGEMENT FACTOR
P
THE EROSION CONTROL PRACTICE FACTOR
USLE
Developed at the USDA National Runoff and Soil Loss Data Center at Purdue University in a national effort led by Walter H. Wischmeier and Dwight D. Smith.
Hailed as one of the most significant developments in soil and water conservation in the 20th century
Limitations of USLE
It does not explicitly represent hydrologic and erosion processes, i.e. runoff. There is considerable interdependence between variables.
Only predicts the amount of soil loss that results from sheet or rill erosion on a single slope and does not account for additional soil losses that might occur from gully, wind or tillage erosion.
SOIL PROPERTIES THAT TEND TO RESULT IN HIGH K VALUES:
High contents of silt and very find sand
Expansive types of clay minerals
A tendency to form surface crusts
Presence of impervious soil layers
Blocky, platy, or massive structure
SOIL PROPERTIES THAT TEND TO MAKE THE SOIL MORE RESISTANT TO EROSION (LOWER K VALUES):
High SOM content
Non-expansive types of clay
Strong granular structure
USLE factors
A simple method to predict K was presented by Wischmeier et al. which includes the particle size of the soil, organic matter content, soil structure and profile permeability.
The soil erodibility factor K can be approximated from a nomograph if this information is known.
CONTROL OF SOIL EROSION
MAINTENANCE OF SOIL FERTILITY AND PRODUCTIVITY
AVOIDANCE OF SOIL TOXICITIES
SOIL CONSERVATION (3)
SOIL EROSION CONTROL MEASURES OBJECTIVES
Dissipation of raindrop impact
Increase infiltration rates
Reduction of surface runoff velocities
Reduction of soil erodibility by enhancing soil properties that resist erosive forces
Surface covers
The single most effective measure in reducing erosion is to provide a protective cover to the soil surface
Dissipates energy of raindrops thus eliminating the splash effect
Impedes water flow
Increase infiltration
Reduce runoff
Minimize erosion
Surface covers
Help reduce evaporation
Help reduce soil temperature
Help reduce weed growth
Enhance soil fertility
Suppress weed growth
Cover crops
Temporary vegetative cover of fast growing annuals
Grown primarily to protect bare soil
Ground cover
Perennials or regenerating annuals specifically established to protect soil from erosive agents.
Mulching
Practice of spreading plant residues/other organic materials on the ground between crop rows or round tree trunks to protect the bare soil.
e.g. Day-og (Cordillera forest dwellers)
Grasses and other plant debris are spread over the area intended for planting, similar to mulching.
Geotextiles
Use of coconets to protect the slopes.
Physical barriers
Land treatments or physical structures constructed along the contour of the land at defined intervals, to intercept and/or divert runoff.
Includes bench terracing, contour rockwalls, contour bunds and pole barriers or contour fence.
Bench terracing
Slope is converted into series of level to nearly level steps running across the slope supported by steep risers with horizontal cultivated area on the step.
e.g. Banaue rice terraces
Landscape scale agroforestry farming system. Consists of:
Payoh (rice terraces)
Pinugo (forest) system
Contour rockwalls
Fence-like structures made up of the rocks and/or stones piled along the contour of sloping lands.
e.g. Tuping (Nueva Vizcaya, Cebu, Siguijor)
Rockwalls reinforced with ipil-ipil, which is regularly trimmed
Trimmings fed to goat and goat manure used as fertilizer for corn
Contour bounds
Embankments (riser/humps) of stones, grasses, or compacted soil (or combination) which are constructed along the contour to slow down surface runoff and trap eroded soil
e.g. Fanya juu in Eastern Africa
The main purpose is to prevent water and soil loss and to make conditions more suitable for plants to grow.
Pole barriers / contour fences
Ipil-ipil stems bundled into rows across the slope and staked to form low barriers.
e.g. Balabag system in Naalad, Naga, Cebu ➥ A 4-5 year tree-crop rotation
4-5 years of corn-tobacco cropping and ipil- ipil fallow
Contour hedgerows
Hedges of leguminous trees or shrubs, or grasses grown on the contour at a defined interval.
Crops are cultivated on the alleys or spaces between hedgerows.
Regularly pruned to prevent shading the intercrops
e.g. Sloping Agricultural Land Technology (SALT)
Natural vegetative strips
Naturally occurring vegetation like grasses and herbs are left in narrow strips to serve as barriers.
e.g. NVS in Claveria, Misamis Oriental
Alleys are planted with corn.
Contour composting
Banks or barriers trashes and/or earth are constructed across the slope of the land to check surface runoff and soil erosion.
e.g. Gen-gen (Ikalahans- Southern Cordillera, Caraballo, Sierra Madre)
Diversion canals
Natural/artificial drainage channel along the steepest slope, in the valley or along the boundaries of the upland farm used to accommodate runoff.
Contour canals
Holes dug intermittently along water channels to:
↝ Intercept water flow and catch the soil particles
↝ Slow down runoff water
↝ Increase infiltration
Grassed waterways
Channel constructed across the slope to catch upslope runoff and divert it safely to a nearby gully, waterway/river.
Check dams
Obstruction walls across the bottom of a gully which reduce the velocity of the runoff and prevent the deepening or widening of the gullies.
Soil traps
Small canals dug along the contour line to:
↝ Allow water to pass through
↝ Trap soil sediments
Zero tillage
The practice of sowing crops directly into the residue of the previous crop without cultivation.
Weeds are usually controlled using herbicides.
Minimum tillage
The practice of sowing crops on lightly cultivated soil.
Weeds are usually controlled using herbicides.
Weeds are retained.
Contour plowing
The practice of plowing, harrowing, and furrowing along the contour of the land.
Multi-storey agroforestry system
Multi-layered canopy
Velocity of rainfall is reduced
e.g. coconut-based farming systems
Cover crops
Mulching
Ground cover
Geotextiles
Surface covers (4)
Bench terracing
Contour rockwalls
Contour bounds
Pole barrier / contour fences
Physical barriers (4)
Contour hedgerows
Natural vegetative strips
Contour composting
Vegetative barriers (3)
Diversion canals
Contour canals
Grassed waterways
Check dams
Soil traps
Canals and soil traps
Minimum tillage
Zero tillage
Contour plowing
Cultural methods (3)