Drainage of plots
1. Presentation
Characterization of the technique
Description of the technique:
| Martine Despreaux-Robelin | CA 71 | mdespreaux(at)sl.chambagri.fr | St Germain du Bois (71) |
|---|---|---|---|
| Jean-Robert Moronval | LEGTA E de Chambray | jean-robert.moronval(at)educagri.fr | Gouville (27) |
| Pierre mulliez | CA 49 | pierre.mulliez(at)maine-et-loire.chambagri.fr | Angers (49) |
| Estelle Meslin | INRA | estelle.meslin(at)rennes.inra.fr | Rennes (35) |
| Rémy Ballot | INRA | remy.ballot(at)grignon.inra.fr | Grignon (78) |
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Promote water flow in hydromorphic plots by installing deep drains. Draining a plot requires a preliminary soil study and topographic survey to determine the technical implementation details (spacing of drains, collectors...) and identify any potential wetlands.
Details on the technique:
Draining one or more plots represents a significant investment. The effectiveness of the operation must therefore be evaluated beforehand.
Implementation period On established crops
Drainage of a plot is a long-lasting operation.
Spatial scale of implementation Plot
Drainage can be done at the plot scale, or even in a coordinated manner at the watershed scale.
Application of the technique to...
All crops: Sometimes difficult to generalize
On drained plots, precautions must be taken for crops with taproot systems (notably rapeseed) which may pose risks of drain clogging.
All soil types: Easily generalizable
However, drainage is only justified on soils sensitive to hydromorphy. A prior pedological study is essential.
All climatic contexts: Easily generalizable
Regulation
NEGATIVE influence
The Water Law requires declaration of drainage projects from a cumulative drained area of 20 ha since 1993 and subjects project implementation to authorization from 100 ha. These areas are reduced to 0.1 ha for declaration and 1 ha for authorization in wetland zones. Modifications in the minor bed of watercourses may also require declaration or authorization.
Water Law and wetlands
2. Services provided by the technique
3. Effects on the sustainability of the cropping system
"Environmental" criteria
Effect on air quality: Variable
GHG emissions: VARIABLE
Effect on water quality: Variable
N.P.: VARIABLE
Pesticides: DECREASE
Effect on fossil resource consumption: Variable
Fossil energy consumption: VARIABLE
Other: No effect (neutral)
Air: The drainage operation itself involves greenhouse gas emissions due to fuel consumption. But in the long term, fuel consumption and related greenhouse gas emissions can be reduced thanks to more favorable soil working conditions. Moreover, drainage limits nitrous oxide emissions by denitrification.
Water: Drainage can promote nitrogen transfer to water. The risk is particularly high in the first years following drainage, when accumulated organic matter is mineralized. Conversely, drainage would limit the transfer of phosphorus and pesticide residues to water by reducing runoff.
Flood risk: Increase
Drainage accelerates water transfer to watercourses and can thus amplify the risk of flooding following rainfall events.
Fossil energy: The drainage operation itself consumes energy, but in the long term, drainage can limit fuel consumption related to crop establishment by maintaining favorable soil working conditions.
"Agronomic" criteria
Productivity: Increasing
Drainage improves the yield potential of hydromorphic plots by maintaining favorable conditions for crop development.
Soil fertility: Increasing
Drainage of hydromorphic plots has a positive effect on soil nitrogen supply by promoting mineralization. Furthermore, it prevents the accumulation of toxic elements in the soil (ferrous, sulfurous, manganese ions…).
Water stress: Decreasing
Drainage promotes root exploration of the soil and thus better utilization of the available water reserve.
Functional Biodiversity: Variable
Drainage is unfavorable for species dependent on wet environments and anaerobic microorganisms. Conversely, it favors aerobic microorganisms.
"Economic" criteria
Operating costs: Variable
Drainage can reduce the need for fungicide protection and nitrogen fertilization. But the use of inputs and associated operating costs may increase to meet the increased yield potential.
Mechanization costs: Decreasing
Drainage can reduce fuel consumption due to better soil working conditions.
Margin: Increasing
Drainage generally improves system profitability by increasing plot potential.
Other economic criteria: Variable
Fuel consumption: Decrease
The drainage operation itself consumes fuel but can reduce fuel consumption due to better soil working conditions.
Land charges: Increase
Drainage implementation represents a significant cost: on average €1600/ha excluding preliminary studies.
"Social" criteria
Working time: No effect (neutral)
Peak period: Decreasing
Drainage of hydromorphic plots allows better spreading of work, enabling wider intervention windows.
Observation time: No effect (neutral)
4. Organisms favored or disfavored
Favored Bioagressors
| Organism | Impact of the technique | Type | Details |
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Disfavored bioagressors
| Organism | Impact of the technique | Type | Details |
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Favored Auxiliaries
| Organism | Impact of the technique | Type | Details |
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Disfavored Auxiliaries
| Organism | Impact of the technique | Type | Details |
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Favored climatic and physiological accidents
| Organism | Impact of the technique | Details |
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Disfavored climatic and physiological accidents
| Organism | Impact of the technique | Details |
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5. For further information
- Drainage
- -Trouche G.
Les mots de l'agronomie, Website, 2014
- La carotte, practical guide.
- -Villeneuve, F.
CTIFL Edition, Book, 1992
- Drainage and drained soils
- -Mulliez P. (CA 49)
Anjou Cultures n°127, Press article, 2008
- Diseases of lettuce. Identification, knowledge and control.
- -Blancard, D.
INRA Edition, Book, 2003
- Phytophthora diseases worldwide
- -Erwin
The American Phytopathological Society Press ed, Book, 1996
6. Keywords
Bioagressor control method: Cultural control
Mode of action: Mitigation
Type of strategy regarding pesticide use: Redesign