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Assessment of the traffic induced soil compaction risk

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Assessment of the traffic induced soil

compaction risk

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Introduction

Compaction affects many physical, chemical and biological properties and processes in the soil and may result in:

- environmental problems (e.g. erosion, flooding, nutrient and pesticide leaching to groundwater)

- agronomic problems (decreased root growth and plant development, with an associated reduction in crop yield)

Root distortion due to soil compaction Sugar beet harvesting

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Pedotransfert function showed that Belgium is one of the European countries most affected by the soil compaction.

However, C. Rosière et al. (2010) showed that pedotransfert fonction can not accurately estimate

compaction susceptibility.

Introduction

 Need to make more

measurements and use physical models.

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The aim of the research project is to measure the compaction at the field scale and to extrapolate the results thanks to physical models and simulations.

Objective of the study

Local measurement

Map of soils susceptibility to compaction Pedotransfert functions

Models and simulations

Two treatments are compared : reduced tillage and conventional tillage with ploughing.

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Materials and Methods

Measurements at the scale of the field

Models

- Soilflex

- The FEM with pseudo elastic model - Sisol, (effect of tillage on soil structure) - Oedometer tests

- Resistance to cone penetration

- Pore size distribution (with mercury porosimeter)

- Permeability - Bulk density

- Proctor compaction test …

Exemple of an oedometer test

Stress (kPa) Str ain (% ) Resistance to penetration

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Materials and Methods

The experiment field is located in Gentinnes in a silt loam soil.

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Materials and Methods

The experiment field is located in Gentinnes in a silt loam soil.

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Materials and Methods

Plot of reduced tillage, and plot of conventional tillage with ploughing were selected close together in order to compare the results in the same conditions.

The location of the 2 repetitions were selected according to soil textural property in order to test the

compaction with two different textures.

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Materials and Methods

Plot of reduced tillage, and plot of conventional tillage with ploughing were selected close together in order to compare the results in the same conditions.

The location of the 2 repetitions were selected according to soil textural property in order to test the

compaction with two different textures.

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Soil sample locations were

selected according to the

path of the wheels

Materials and Methods

Samples were taken at 20

and 40 cm depth

Sample Sugar beet

path of the wheels

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Preliminary results

reduced tillage conventional tillage

Soil pit showed that plot with reduced tillage has a massive

structure compared to plot with conventional tillage

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Conventionnal tillage Reduced tillage

Preliminary results

The drop test confirmed that the soil with reduced tillage

contains larger aggregates

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Preliminary results

Do these differences

influence the behavior

of soils in response to

traffic ?

Conventionnal tillage Reduced tillage

The drop test confirmed that the soil with reduced tillage

contains larger aggregates

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Modelling : The SoilFlex model

1) Stress on the surface of soil 2) Stress propagation through soil 3) Soil deformation

Analytical approach as used in SoiFlex was shown not to be inferior to finite element models with regard to the accuracy.

The weak point is the concentration factor as it is not a directly measurable soil parameter.

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Finite Element Method is a numerical technique for finding approximate solutions of partial differential equations as well as integral equations.

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Discretisation: mesh used to model the soil medium Mathematical model

Exemple of simulation

Modelling : the Finite Element Method

Strain Young’s modulus

Poisson's ratio

FEM were developed for isotropic linear elastic media characterised by E and µ.

Agricultural soil requires specific numerical methods because of the non-linear relationship between strain and displacement.

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Modelling: the Sisol model

Optimisation of tillage practices requires the evaluation of the long-term effects of cropping on changes in the soil structure.

 The SISOL model estimate the quantity and location of ∆ clods

After sugar beet sowing

After sugar beet harvesting

After ploughing

Clods with no

eye-visible porosity (Compacted zones)

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After sugar beet sowing

After sugar beet harvesting

After ploughing

We will modify SISOL and try to estimate the bulk

density

Modelling: the Sisol model

Optimisation of tillage practices requires the evaluation of the long-term effects of cropping on changes in the soil structure.

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Conclusion

The numerous measurements focused on the same plot should

allow a proper assessment of the compaction mechanism and risk.

The use of models should allow extrapolation of results and

evaluation of different cultural practices.

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J.N. LOUVET, J. VERSWIJVEL, K. ABROUGUI, C. ROSIERE, C. ROISIN, M.F. DESTAIN

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Mercury Intrusion porosimetry

Sample

Mercury Therefore, at any pressure, the pores into which mercury

has intruded have diameters greater than

D = -4ϒcosθ/P

D: pore diameters

Mercury does not wet substances and will no penetrate pores by capillary action. Entry into pore spaces requires applying pressure in inverse proportion to opening size.

ϒ: mercury surface tension θ: mercury contact angle P: applied pressure

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Diameter (µm) 100 1 0.01 In tr us ion V ol ume (c c/ g)

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