3 Erosion and Sediment Transport - 3.3 Measurement and calculation of soil loss Flashcards
Measurement and Calculation of Soil Loss at glance
We have insufficient field data and the required monitoring networks do not currently exist.
The assessment of erosion at large scale is only feasible by using mathematical models.
Models need field data for calibration/validation!
Erosion is a process, but the eroded material is usually called “soil loss”.
Active and Passive Variables Influencing Erosion
Climate (natural/active)
– precipitation, snow, temperature, wind, climate change
Soil (natural/passive)
– particle size, structure, aggregate stability, susceptibility to crusting, hydraulic conductivity, field capacity etc.
Topography (natural/passive)
– slope steepness, slope length, slope form, exposition
Vegetation (natural/passive)
– phenological phase, density, species, root depth
Land management (anthropogenic) – land cover, tillage, crop rotation, terrace construction, irrigation, erosion protection measures
Experimental Parcel for Erosion Measurement
See pict on slide 29
Models for the Calculation of Soil Loss - Deterministic Models
Single event
Physical process model
Loss and deposition
Transferrable to other investigation areas
Models for the Calculation of Soil Loss - Empirical Models
Long-time mean
Statistical analysis from plot experiments
Only soil loss
Not transferrable without recalibration
Erosion Models
Most models attempt to combine: – soil erodibility & landscape – land use – driving forces (active variables) – erosion protection measures
Models:
– Universal Soil Loss Equation (USLE)
– Revised Universal Soil Loss Equation (RUSLE V1, V2)
– Water Erosion Prediction Project (WEPP)
– Erosion 2D/3D (deterministic model)
– KINEROS2
– SWAT (example for hydrological models, which often incorporate empirical soil loss models like USLE/RUSLE)
Universal Soil Loss Equation USLE
A = R.K.Ls.C.P [ton/ha.yr]
A: Average annual erosion rate (sheet and rill erosion only)
R: Rainfall factor (runoff erosivity index) [MJ mm / ha h]
K: Soil erodibility factor [(t h) / (MJ mm)] -> how easily can soil aggregate be broken by rain drops
L, S: Topographic factors [-]: slope length and slope steepness
C: Crop management factor [-] -> ratio of soil loss compared to fallow (bare, exposed) soil
P: Erosion control practice factor [-]
USLE – RUSLE
USLE computes unit plot erosion by R*K
Unit plot attributes: 9% slope, 72.6 feet long, cultivated fallow.
The factors LSCP are normalized (value 1 for unit plot conditions) .
LSCP adjust unit plot erosion to account for differences to field conditions of the actual site.
USLE computes long-term mean annual values of soil loss. This does not adequately represent erosion processes, neither is this a suitable temporal resolution for todays hydrological models.
The revised RUSLE2 works with daily resolution and combines deterministic equations with the unit plot concept of the USLE.
Estimation of Sediment Yield
The Universal Soil Loss Equation does not compute sediment intake into rivers. A large fraction of the lost material is deposited in the valleys.
Reservoir Survey Method: determine quantity of deposited sediment per year.
Consequences of Soil Erosion and Sediment Transport
Land surface
– Removal/redistribution of soil, formation of unwanted structures
– Loss of arable land and valuable topsoil, decline in productivity
– Reduction of soil functional capacity
– Damage of infrastructure (pumps, buildings, traffic)
Aquatic systems
– Diffuse pollution by contaminants and nutrients
– Changing river beds, silting of lakes, river courses, reservoirs, docks, …
– Destruction of habitats
– Eutrophication
Note: Soil erosion is a natural process occurring over geological timescales. Where the natural rate has been significantly increased by human activity, accelerated soil erosion becomes a process of degradation and thus a threat to soil.
Soil Erosion Risk Assessment
See diagram on slide 36
Pan-European Soil Erosion Risk Assessment (PESERA)
PD Dr.
Quick glance at the map on slide 37