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

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A<br />

Richness S<br />

B<br />

Shannon H’<br />

C<br />

Distances to centroids<br />

50<br />

40<br />

30<br />

20<br />

10<br />

0<br />

3<br />

2<br />

1<br />

0<br />

0.8<br />

0.7<br />

0.6<br />

0.5<br />

0.4<br />

0.3<br />

B<br />

B<br />

B<br />

a)<br />

Wheat<br />

after<br />

annuals<br />

P = 0.0041<br />

P = 0.0033<br />

P < 0.0001<br />

b)<br />

Lucerne<br />

1 year<br />

c)<br />

Lucerne<br />

2–6<br />

years<br />

Groups of fields<br />

d)<br />

Wheat<br />

after<br />

lucerne<br />

Fig. 2 Weed species diversity measures for four groups of fields<br />

(see Table 1). (A) species richness (B) Shannon diversity in<strong>de</strong>x,<br />

(C) Bray–Curtis distance to group centroids (beta-diversity). Broad<br />

lines are medians, black dots are means, boxes show the interquartile<br />

range and whiskers extend to the last data point <strong>with</strong>in<br />

1.5 times the inter-quartile range, open circles are further outliers.<br />

P-values of ANOVA (A, B) and permutation tests (C) are given.<br />

Groups not sharing the same letter are significantly different<br />

at a = 0.05.<br />

perennials Taraxacum spp. and Rumex spp. have<br />

already been reported (Ominski et al., 1999; Albrecht,<br />

2005; Hiltbrunner et al., 2008; Ulber et al., 2009). Our<br />

surveys suggest that other perennial species ⁄ genera react<br />

A<br />

A<br />

A<br />

Ó 2010 INRA<br />

Journal Compilation Ó 2010 European Weed Research Society Weed Research 50, 331–340<br />

B<br />

B<br />

A<br />

B<br />

B<br />

A<br />

Arable weeds and perennial lucerne 337<br />

similarly (Reseda spp., Malva spp., Picris spp., Crepis<br />

spp., Silene latifolia Poir., Falcaria vulgaris Bernh.,<br />

Table 3), leading to a strong response of the whole<br />

functional group (Fig. 3). Perennial species likely profited<br />

from the absence of soil tillage. In this way, weed<br />

growth conditions in pluriannual lucerne may be similar<br />

to no-till systems (e.g. Zanin et al., 1997). Some perennials<br />

might also be more tolerant to prolonged competition.<br />

Conversely, most annual weeds are probably best<br />

adapted to annual <strong>crop</strong>s and survive the yearly soil<br />

tillage as seeds in the soil. Soil tillage may even promote<br />

recruitment of annual weeds, while it may be inhibited<br />

un<strong>de</strong>r <strong>de</strong>nse canopies of perennial <strong>crop</strong>s (Huarte &<br />

Arnold, 2003). Annual <strong>crop</strong>s would therefore correspond<br />

to very early successional stages favouring<br />

r-selected species <strong>with</strong> shorter life cycles and generative<br />

reproduction (therophytes), whereas established lucerne<br />

would correspond to later successional stages favouring<br />

slower growing and longer living biennial and perennial<br />

(K-selected) species (hemicryptophytes and geophytes).<br />

Cirsium arvense (L.) Scop. was the most important<br />

exception (Table 3), <strong>de</strong>spite its perennial life cycle.<br />

Negative impacts of forage <strong>crop</strong>s on C. arvense have<br />

repeatedly been observed (e.g., Ominski et al., 1999) and<br />

might be linked to the repeated mowings exhausting the<br />

carbohydrate reserves nee<strong>de</strong>d for regrowth (Graglia<br />

et al., 2006).<br />

While the a priori division of broad-leaved species<br />

into six functional groups according to life cycle and<br />

morphology has proven to be quite successful in our<br />

study, we have no explanation for the heterogeneous<br />

reactions of the different grass species. Grasses may<br />

show a better regrowth after cutting than broad-leaved<br />

species, but cutting may strongly reduce seed production,<br />

especially of tall grasses. In previous studies, some<br />

grass species including Apera spica-venti (L.) P.Beauv.,<br />

Avena fatua L. and Setaria faberi F.Herm. were<br />

suppressed by forage <strong>crop</strong>s (Schoofs & Entz, 2000;<br />

Albrecht, 2005), while others including Elymus repens<br />

(L.) Gould and Poa sp. increased (An<strong>de</strong>rsson &<br />

Milberg, 1996; Clay & Aguilar, 1998; Teasdale et al.,<br />

2004; Albrecht, 2005). In our study, the FG of perennial<br />

grasses was slightly increased in lucerne, which may be<br />

compared <strong>with</strong> the positive reaction of perennial broadleaved<br />

species (see above). In contrast, the FG of annual<br />

grasses showed no significant differences. Looking at<br />

each individual species might be more informative.<br />

Species favoured by lucerne inclu<strong>de</strong>d both perennial and<br />

annual grasses (Poa trivialis L. and Bromus spp.) and<br />

some species that are sometimes inclu<strong>de</strong>d in the sown<br />

mixtures (Lolium spp. and Festuca spp., An<strong>de</strong>rsson &<br />

Milberg, 1996), while other annual and perennial grasses<br />

showed no differences or were suppressed (Alopecurus<br />

myosuroi<strong>de</strong>s Hudson., A. fatua, P. annua and E. repens).

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