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Paysages virtuels et analyse de scénarios pour évaluer les impacts ...

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Cropping system factor levels<br />

Two levels of cropping systems were compared: “intensive” and “mo<strong>de</strong>rate”. They differ mainly by winter<br />

landcover and nutrient management. The “intensive” and “mo<strong>de</strong>rate” levels correspond respectively to the<br />

practices observed during the 1995-1997 and 2001-2003 periods on the Frémeur catchment. In the time span<br />

b<strong>et</strong>ween these two periods, significant efforts were done by farmers to reduce soil N inputs. For each period,<br />

farm-type, and landcover class, a typology of CMP was established based on the origin of the fertilizers<br />

involved (mineral, organic) and the spread amounts (Durand <strong>et</strong> al., 2006). Each landcover class (for a given<br />

period and farm-type) was usually characterized by three CMP modalities (up to eight for maize) and their<br />

relative proportions were used as probabilities to combine landcover and CMPs in or<strong>de</strong>r to produce the data<br />

entries for TNT2. Consi<strong>de</strong>ring fertilization, the “mo<strong>de</strong>rate” level differs mainly from the “intensive” level by<br />

a reduction of spread mineral and organic N along with a diminution of the grazed surface and excr<strong>et</strong>a inputs<br />

to grazed grasslands. Organic P inputs were estimated by the soil P mo<strong>de</strong>l presented previously. Mineral P<br />

inputs for the intensive cropping system were estimated a survey done in 2003 (Payrau<strong>de</strong>au <strong>et</strong> al., 2006)<br />

from mineral P loads by farm-type and landcover class. For the mo<strong>de</strong>rate level, mineral P inputs were<br />

systematically omitted.<br />

The agricultural landcover dynamics were simulated at the field scale in two steps:<br />

– Stochastree (Sorel <strong>et</strong> al., submitted; see also chapter III of this thesis), a mo<strong>de</strong>l based on stochastic<br />

<strong>de</strong>cision trees was used to simulate summer crop transitions by consi<strong>de</strong>ring temporal (crop rotation)<br />

and spatial driving factors (farm-type crop area objectives, spatial distribution of crops around the<br />

farmsteads, and sensitivity of crops to soil waterlogging). Stochastree was trained on the 1993-1998<br />

period and the simulation started on year 2000, which was the most exhaustively surveyed year;<br />

– winter landcover was simulated with a s<strong>et</strong> of d<strong>et</strong>erministic and stochastic expert ru<strong>les</strong>, which<br />

involved previous and subsequent summer landcover, <strong>de</strong>rived from the Frémeur catchment survey<br />

(Salmon-Monviola <strong>et</strong> al., submitted). Allocating winter landcover mainly consisted in managing the<br />

harvested maize fields. In the “intensive” level, the fields were left as bare soils generally, whereas in<br />

the “mo<strong>de</strong>rate” level, they were used to grow catch crops like Italian ray-grass or mustard, which<br />

traps N and are then buried by a plowing before the next summer crop sowing (Baggs <strong>et</strong> al., 2000).<br />

The observed and simulated areas of each crop were compared by a Wilcoxon test (p

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