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Diversifying crop rotations with temporary grasslands - Université de ...

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dans <strong>de</strong>s conditions <strong>de</strong> compétition contrastées (présence ou absence <strong>de</strong> luzerne) et avec<br />

ou sans fauche précoce (dispositif factoriel 2x2). La production <strong>de</strong> biomasse par plante a été<br />

affectée par la fauche et par la compétition, et la combinaison <strong>de</strong>s <strong>de</strong>ux traitements a montré<br />

un effet purement additif pour la plupart <strong>de</strong>s espèces (ni affaiblissement, ni renforcement<br />

disproportionnée <strong>de</strong>s effets). Ces connaissances peuvent être utilisées pour concevoir <strong>de</strong>s<br />

systèmes <strong>de</strong> culture conciliant productivité et durabilité.<br />

Mots-clés : Croissance post-fauche, Compétition, Prairies temporaires, Gestion Intégrée.<br />

INTRODUCTION<br />

Plant fitness may be reduced by physical disturbances <strong>de</strong>stroying parts of the plant’s<br />

biomass, competition for resources by neighbouring plants, and different stresses as <strong>de</strong>fined<br />

by Grime (1974). Therefore, plant population dynamics and communities may be structured<br />

by these three processes. Physical disturbances may have various origins such as abiotic<br />

factors (fire, frost, drought, inundation), biotic factors (herbivory, parasitism, grazing) or<br />

human factors such as agricultural management (harvesting, mowing, soil tillage). In arable<br />

fields, competition is the most important interaction between the cultivated <strong>crop</strong>s and the<br />

spontaneously growing weeds (Zimdahl, 2004): <strong>crop</strong> yield may be reduced by competitive<br />

weeds and weed growth may be limited by competitive <strong>crop</strong>s. On the other hand,<br />

disturbances created by different kinds of field operations will affect the plants and are used<br />

to suppress weeds.<br />

Habitats are frequently distinguished by a dichotomy opposing competition and<br />

disturbance: Competition is lower in frequently disturbed habitats and higher in undisturbed<br />

habitats (Grime, 1974). However, both processes may also act in quick succession during the<br />

same vegetation period, for example in perennial forage <strong>crop</strong>s (lucernes, clovers, grasses)<br />

sometimes called ‘<strong>temporary</strong> <strong>grasslands</strong>’. In contrast to the classical annual <strong>crop</strong>s that<br />

prece<strong>de</strong> and follow them in long <strong>crop</strong> <strong>rotations</strong>, perennial <strong>crop</strong>s remain in the field for about<br />

2-6 years. Forage <strong>crop</strong>s are mown 1-5 times per year for hay production creating<br />

disturbances. After each cutting, they show quick regrowth leading to high levels of<br />

competition during the whole vegetation period (except directly after mowing).<br />

Perennial forage <strong>crop</strong>s may have strong impacts on weed abundances and<br />

community composition, as suggested by a survey of farmers (Entz et al., 1995), field<br />

observations (Ominski et al., 1999), field experiments (Schoofs and Entz, 2000;<br />

Heggenstaller and Liebman, 2006) and seed bank studies (Clay and Aguilar, 1998; Sjursen,<br />

2001; Bellin<strong>de</strong>r et al., 2004; Teasdale et al., 2004; Albrecht, 2005). Most of these studies<br />

report reduced abundances of several problematic weed species after the cultivation of<br />

perennial <strong>crop</strong>s, which would be beneficial for the following <strong>crop</strong>s, while other species may<br />

profit from this <strong>crop</strong> type. Nevertheless, little is known about the mechanisms causing these<br />

effects.<br />

Various factors may govern the plant’s ability to survive and grow after cuttings or<br />

other physical disturbances <strong>de</strong>stroying large parts of the aboveground biomass. These<br />

inclu<strong>de</strong> i) the amount of green surface remaining after the disturbance for photosynthesis, ii)<br />

the presence of intact buds (apical meristems) nee<strong>de</strong>d for resprouting and iii) the quantity of<br />

C and N resources that can be remobilized for regrowth (reviewed in Meiss et al., 2008).<br />

These three factors may be affected by different un<strong>de</strong>rlying variables such as (a) the<br />

species functional group (annuals vs. perennials, grasses vs. broadleaved species,…) and<br />

(b) the plant size (biomass), (c) morphology and (d) age (phenological stage) as well as (e)<br />

cutting height, (f) date and (g) frequency (see references in Meiss et al., 2008). Nevertheless,<br />

the plant regrowth capacity may also <strong>de</strong>pend on general growth conditions (temperature,<br />

pH,…) and availability of growth resources (light, water, nutrients) <strong>de</strong>pending on (ii) other<br />

farming operations, (ii) edaphic and climatic variables (soil type, nutrients, precipitation,<br />

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