Practicing No-Till Farming Techniques (NTFT)

1. Presentation
Characterization of the technique
Description of the technique:
No-till farming techniques (TCSL) involve no longer using tillage between harvest and sowing of the next crop. One can distinguish no-till techniques with deep work (loosening, subsoiling...) and without deep work. Direct seeding is covered in another sheet.
Implementation period
On established crop
Spatial scale of implementation
Plot
Application of the technique to...
All crops:
Sometimes difficult to generalize
The implementation of no-till farming techniques can be delicate for some crops, especially those sensitive to compaction.
All soil types:
Sometimes difficult to generalize
The implementation of no-till farming techniques can be facilitated in soils whose structural activity favors the restoration of porosity (clay soils).
All climatic contexts:
Easily generalizable
Regulation
2. Services provided by the technique
3. Effects on the sustainability of the cropping system
"Environmental" criteria
Effect on air quality:
Decreasing
GHG emissions: VARIABLE
particle emissions: INCREASE
Effect on water quality:
Variable
N.P.: NEUTRAL
pesticides: VARIABLE
turbidity: DECREASE
Effect on fossil resource consumption:
Decreasing
fossil energy consumption: DECREASE
Other:
No effect (neutral)
Air: Adoption of TCSL can lead to an increase in ammonia emissions, particularly for nitrogen solutions, because maintaining residues on the surface increases the contact surface with air. Adoption of TCSL helps limit greenhouse gas emissions related to fuel consumption. It also promotes carbon storage in the soil. Nitrous oxide emissions due to denitrification may be increased due to a longer anoxic state at the end of winter in no-till.
Water: Adoption of TCSL has little impact on nitrogen leaching and phosphorus runoff transfers. The impact on pesticide transfers is variable. TCSL promotes water infiltration: thus, it limits runoff transfers but can favor deep transfers by leaching during the drainage period. The increase in organic matter content promotes retention by the clay-humus complex and biodegradation by soil microorganisms.
Fossil energy: Adoption of TCSL involves substituting tillage with other less energy-consuming soil work operations. However, abandoning tillage may require multiple passes during intercrop periods to manage weeds in less diversified rotations. In this case, the reduction in fuel consumption may be limited or even null.
"Agronomic" criteria
Productivity:
Variable
Depending on the crops, the impact of no-till farming techniques on yield is variable. Abandoning tillage does not cause yield losses on winter cereals, for example, but losses can be recorded for crops sensitive to compaction.
Soil fertility:
No effect (neutral)
Lower soil porosity at the surface in the absence of tillage can lead to mineralization starting later in spring. This may lead to anticipating nitrogen inputs. However, long-term trials tend to show that in the long run, the mineralization difference between tillage and no-till does not justify modifying the total dose applied.
Water stress:
Decreasing
Adoption of practices of no-till farming leads to an increase in surface organic matter and promotes vertical soil porosity; thus, the useful water reserve is favored.
Functional biodiversity:
Increasing
Adoption of TCSL reduces pressure on soil life in general.
Other agronomic criteria:
Variable
Weed pressure : variable
Abandoning tillage no longer allows burying seeds deeply. Combined with cultural practices favoring their germination, it can lead to increased weed pressure when seed banks are large.
Pest pressure : variable
Abandoning tillage can lead to increased rodent pressure. The impact on slugs is variable (pressure sometimes lower in tillage than in no-till).
Disease pressure : variable
Absence of tillage can increase pressure from certain pathogens due to residue non-burial (take-all, fusariosis…). However, reducing the number of passes reduces the risk of inoculum transfer from one plot to another via tools.
"Economic" criteria
Operational costs:
Variable
Adoption of TCSL can lead to increased weed pressure in some cases and imply increased herbicide costs. Maintaining residues on the surface can also favor some pests and diseases (slugs, fusariosis...). Seeding density may also need to be increased to compensate for emergence losses.
Mechanization costs:
Variable
Adoption of no-till farming practices generally reduces mechanization costs by eliminating tillage, an energy-consuming operation. But this reduction can be small or even null if tillage abandonment must be compensated by multiple intercrop passes to control weed pressure. Moreover, TCSL may require acquiring adapted equipment.
Margin:
Variable
The impact of adopting no-till farming practices on margin is variable, depending on the balance between the more or less significant reduction in mechanization costs on one side, and on the other side the increase in operational costs that may result from increased weed and pest pressure, as well as yield decreases recorded on some crops.
Other economic criteria:
Decreasing
Fuel consumption: Decrease
Adoption of TCSL involves substituting tillage with other less energy-consuming soil work operations, resulting in a 15 to 30% reduction in fuel consumption. However, abandoning tillage may require multiple intercrop passes to manage weeds in less diversified rotations. In this case, the reduction in fuel consumption may be limited or even null.
"Social" criteria
Working time:
Decreasing
Adoption of no-till farming practices generally has a neutral impact on overall workload; the reduction in soil work time is offset by more observations. However, better distribution of working time is often highlighted.
Peak period:
Decreasing
Observation time:
Increasing
4. Favored or disadvantaged organisms
Favored bioagressors
Disadvantaged bioagressors
Favored auxiliaries
Disadvantaged auxiliaries
Favored climatic and physiological accidents
Disadvantaged climatic and physiological accidents
5. For further information
- In the wake of no-till
- -Agreste Agreste primeur, n°207,, Press article, 2008 link to article
- Evaluation of environmental impacts of No-Till Farming Techniques (TCSL) in France
- -Labreuche J., Le Souder C., Castillon P., Real B. (Arvalis), Ouvry J.F. (AREAS), Germon J.C. (INRA), De Tourdonnet S. (AgroParisTech) Professional report, 2007 study report
- Environmental impacts of TCSL: positive effects on air quality and greenhouse effect
- -Germon J.C. (INRA), Nicolardot B. (AgroSupDijon), Métay A. (SupAgroMontpelier), Labreuche J. (arvalis) Perspectives agricoles n°347, p40-45, Press article, 2008 link to article
- Environmental impacts of TCSL: integrating TCSL into sustainable production systems, a challenge for agronomists
- -Stengel P. (INRA) Perspectives agricoles n°352, p38-44, Press article, 2009 link to article
- Environmental impacts of no-till farming techniques: no-till techniques concern one-third of French surfaces
- -Labreuche J. (Arvalis) Perspectives agricoles n°342, p38-43, Press article, 2008 paid article
- Environmental impacts of no-till techniques: TSL modify soil quality and biodiversity
- -De Tourdonnet S. (AgroParisTech) Perspectives agricoles n°344, p36-41, Press article, 2008 link to article
- No-till in arable farming and livestock: environmental and economic evaluations.
- -Le Garrec L., Revel A. (INRA) Ingénieries n°38, p21-35, Press article, 2004 link to article
- Getting started without failing in no-till
- -Ouvrard N. Réussir arable farming n°241, p46, Press article, 2010 article
- Storing carbon in French agricultural soils
- -Arrouays D., Balesdent J., Germon J.C., Joyet P.A., Soussana J.F., Stengel P. (INRA) Professional report, 2002 study report
- TCSL in environment: no-till farming reduces erosion within plots
- -Ouvry J.F. (AREAS), Lebissonnais Y. (INRA) Perspectives agricoles n°345, p62-68, Press article, 2008 link to article
- Nitrogen transfer and mineralization: little effect of soil work
- -Le Souder C. (arvalis) Perspectives agricoles n°348, p20-22, Press article, 2008
- Phosphorus transfer: no-till finds its limits
- -Castillon P. (Arvalis) Perspectives agricoles n°348, p24-25, Press article, 2008
- Pesticide transfers: solutions for each major soil type
- -Réal B. (Arvalis) Perspectives agricoles n°348, p20-22, Press article, 2008 article
6. Keywords
Bioagressor control method:
Mode of action:
Type of strategy regarding pesticide use:
Annexes
Est complémentaire des leviers
Favorise les bioagresseurs suivants
- Theophrastus' Abutilon
- Yarrow
- Wind bentgrass
- Creeping bentgrass
- Field lady's mantle
- White amaranth
- Prostrate amaranth
- Prostrate pigweed
- Hybrid amaranth
- Reflective amaranth
- Ragweed
- Tall ammi
- Mayweed
- Field chamomile
- Tall chamomile
- Common chervil
- Thalius' rockcress
- Common mugwort
- Spreading orach
- Clustered oat
- Ludovician sterile oat
- Intermediate barbarée
- Three-lobed beggarticks
- Cornflower
- Sterile brome
- Irregular calepine
- Shepherd's purse
- Hairy bittercress
- Wild carrot
- Clustered cerastium
- Field thistle
- Milk thistle
- White goosefoot
- Wall goosefoot
- Hybrid goosefoot
- Polyspermous goosefoot
- Couch grass (chicken foot)
- Creeping couch grass
- Corn marigold
- Nîmes hawkweed
- Jimsonweed
- Blood digitgrass
- False rocket
- Four-angled willowherb
- Hemlock-leaved storksbill
- Hemlock water-dropwort
- Small spurge
- Petty spurge
- Spurge (wake-up call)
- Common fennel
- Lesser celandine
- Wild oat
- Small-flowered fumitory
- Common fumitory
- Fusariosis
- Fusarioses producing fumonisins
- Trichothecene A fusarioses in maize
- Trichothecene A fusarioses in barley
- Trichothecene B fusarioses with zearalenone in cereal straw
- Trichothecene B fusarioses with zearalenone in maize
- Trichothecene fusarioses in sorghum
- Cleavers
- Cottony galactites
- Round-leaved geranium
- Slender-stemmed geranium
- Dove's-foot geranium
- Dissected geranium
- Soft geranium
- Tuberous vetchling
- Field gromwell
- False viper's bugloss
- Soft brome
- Rigid darnel
- Toad rush
- Field sow-thistle
- Rough sow-thistle
- Curly endive
- Clasping-leaved dead-nettle
- Purple dead-nettle
- Large-fruited hemp-nettle
- Common hawkweed
- Bastard toadflax
- Narrow-leaved toadflax
- Lesser toadflax
- Field bindweed
- Hedge bindweed
- Dioecious catchfly
- Chamomile matricaria
- Scentless chamomile
- Common mallow
- Round-leaved mint
- Annual mercury
- Black nightshade
- Field chickweed
- Field mustard
- Black mustard
- Field forget-me-not
- Branched broomrape
- Dichotomous panicgrass
- Hair panicgrass
- False millet panicgrass
- Cock's-foot panicgrass
- Two-spiked paspalum
- Field peppergrass
- Drave peppergrass
- Annual meadow-grass
- Common meadow-grass
- Argemone poppy
- Corn poppy
- Venus' comb
- Field pansy
- Harvest parsley
- Paradoxical phalaris
- Ten-stamened pokeweed
- False hawkweed picris
- Ribwort plantain
- Greater plantain
- Creeping potentilla
- Giant horsetail
- Horsetails
- Rough charlock
- Charlock
- English ryegrass
- Italian ryegrass
- Field buttercup
- Marsh buttercup
- Creeping buttercup
- Patience-leaved knotweed
- Amphibious knotweed terrestrial form
- Bird's knotweed
- Bindweed knotweed
- Persicaria knotweed
- Mignonette mignonette
- Blunt-leaved dock
- Curly dock
- Small sorrel
- Common groundsel
- Glaucous setaria
- Green setaria
- Whorled setaria
- Field sherardia
- Hedge mustard
- Aleppo sorghum
- Edible nutsedge
- Venus' looking-glass
- Field spurge
- Intermediate chickweed
- Field madder
- Tall tordyle
- Field torilis
- Knotted hedge parsley
- Coltsfoot
- Sumatra fleabane
- Ivy-leaved speedwell
- Persian speedwell
- Field speedwell
- Shining speedwell
- Common vervain
- Rat's-tail fescue
- Field foxtail
Favorise les auxiliaires