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3. ESTABLISHMENT AND REPRODUCTIVE SUCCESS OF OILSEED RAPE ( BRASSICA

3.3 R ESULTS

3.4.2 Comparison of cultivated and weedy species

confirm that seed production per plant on some ruderal sites may be substantial and can exceed my findings (Dietz-Pfeilstetter et al. 2006, Menzel 2006).

agricultural seeds lost in transport and not for seeds produced under ruderal conditions.

However, my seed viability tests show that seeds collected from ruderal OSR and B. rapa almost show no reduction in seed viability compared to commercial seeds.

The cultivated species displayed high seed viability and low levels of dormancy. In addition, they clearly exhibited greater plant fitness, as the proportion of seedlings which grew into reproducing individuals was also significantly and greatly higher compared with the weedy species, with 41.1 and 83.4% for OSR and B. rapa, compared to 8.7% for B. nigra and 2.9%

for R. raphanistrum. While B. rapa even produced more seeds per plant than the weedy relatives, OSR produced at least equal amounts. In both weedy species most individuals developed poorly, and only few well-developed individuals produced large amounts of seeds.

This L-shaped distribution in seed reproductive output has previously been described for populations of R. raphanistrum (Stanton 1985). Furthermore, interspecific competition within the containers will have favoured fast-developing species. B. rapa was observed to be the first to flower in early May, followed by OSR (mid- to late May). R. raphanistrum and B. nigra flowered considerably later in early June and mid-July, respectively. B. nigra was at a particular disadvantage as the only species with a considerable emergence in spring 2008, while seedlings of all other species emerged almost exclusively in fall 2007. In addition, B. nigra has much smaller seeds and consequently smaller seedlings than the other species, which can be disadvantageous in a competitive environment (Stanton 1985). Larger seedlings are more resistant to environmental hazards, have more reserves and gain better access to resources (Leishman et al. 2000). Thus, the cultivated species may have largely depleted resources such as light and nutrients, resulting in a poor development of B. nigra and R. raphanistrum.

Other studies confirm superior establishment success of OSR over B. nigra in competition with grassland vegetation under field conditions (Walker et al. 2004) and a tendency for higher seed production by B. rapa vs. B. nigra in non-competitive greenhouse experiments (Feldheim & Conner 1996).

3.4.3 Implications for transgene escape

The superior performance of the cultivated species on low-quality ruderal substrates indicates a higher potential weediness for OSR and B. rapa than expected. In spite of low substrate quality and a stressful environment in terms of resource competition, the cultivated species were “weedier” than B. nigra and R. raphanistrum in some aspects which are typically attributed to successful weeds (Ammann et al. 2000): the capacity to germinate and produce

seeds in a wide range of environments, to produce a very large number of seeds under favourable conditions, as well as a rapid growth through the vegetative phase to flowering.

Given that both OSR and B. rapa successfully established on ruderal soils and showed a high reproductive capacity, hybridisation of these species, which is frequent and may lead to transgene introgression in agricultural settings (see 1.2.1), may well occur in feral populations.

While it has been demonstrated that some domestication traits, such as a dwarfing gene (Rose et al. 2009), can reduce fitness, my findings suggest that crop genes in general are not disadvantageous in non-agricultural environments. Studies with crop-wild hybrids mostly show lower fitness for the hybrid than for the wild parent (reviewed in Campbell 2007, Ellstrand 2003 and Hails & Morley 2005), including hybrids of OSR and wild relatives (but see Hauser et al. 2003). However, these studies are mostly restricted to early-generation hybrids whose fitness may be influenced by effects such as outbreeding depression and heterosis (Burke & Arnold 2001, Ellstrand 2003), which may over- or underestimate the probability of crop genes to persist within weed populations (Campbell 2007).

Some studies investigating the consequences of specific domestication traits indeed confirm that crop traits can be beneficial to plant fitness in stressful or non-crop environments, for example large size of seedlings and plants, rapid growth, early flowering and large flowering disk diameter in sunflowers (Baack et al. 2008, Mercer et al. 2007). In contrast, random crop alleles in crop-wild hybrids of OSR and weedy B. rapa only showed a positive effect in the absence of competition (Rose et al. 2009). In several cases, conventional crop genes managed to persist in weeds for several years under natural conditions (genes from OSR persisting in weedy B. rapa (Hansen et al. 2001), or genes from R. sativus persisting in R. raphanistrum (Snow et al. 2001)), giving further indications that crop genes do not generally confer a selective disadvantage (Campbell 2007). More significantly, an invasive hybrid line of R. sativus and R. raphanistrum has completely replaced the wild progenitor in California and apparently led to its local extinction (Hegde et al. 2006).

Similarly, my study indicates that R. raphanistrum and B. nigra could potentially benefit from crop traits conferred by OSR. One has to keep in mind, though, that my results are restricted to first-year successional stages in the absence of vertebrate and slug herbivory where competition by perennial plants was minimal. All three factors can heavily influence long-term survival of feral OSR populations (Crawley et al. 1993). While my results hint at a lower competitive ability of the weedy relatives, further research is needed on resistance to

herbivores or to fungal attack and other mortality factors. Another, possibly more important factor, is long-term survival in the seed bank, which does occur in OSR (Lutman et al. 2003) but at generally lower rates than those observed in weedy relatives (Hails et al. 1997, Lutman et al. 2002). It is an important characteristic of annual weeds and a factor for feral population persistence (Ammann et al. 2000, Cheam 1995, Gressel 2005). For a full assessment of OSR weediness, the benefits and drawbacks of high dormancy levels versus high reproductive output in the first year need to be assessed in the view of long-term establishment success (see 6.1.5).

In conclusion, my findings do not support the common assumption that crop traits would necessarily be disadvantageous in a wild environment, especially under stressful conditions, and that selection against crop alleles would prevent or reduce the introgression of transgenes into wild relatives (Squire et al. 2010, Stewart et al. 2003). My findings imply that ruderal environments may well facilitate uncontrolled spread of transgenes from OSR. Even though it is a cultivated plant, OSR has proven successful under suboptimal soil conditions, displayed the potential for self-sustained population increase and even outperformed weedy relatives.

Despite the fact that feral populations are mostly short-lived, their potential for weediness should thus not be overlooked or minimised, especially if further fitness advantages, such as herbicide resistance, are conferred through a transgene. Apart from the dangers this poses through uncontrolled transgene spread via feral OSR populations, it also raises concern regarding transgene spread via weedy or cultivated relatives, which does not seem to be limited by negative fitness effects of conventional domestication traits. Ruderal sites may thus serve as suitable refuges facilitating transgene escape. Given that an intensive monitoring of these sites is very time-consuming, transgene spread via these sites may go largely unnoticed.

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