Abstract:1. Pollination is an important ecosystem service as many agricultural crops such as fruit trees are pollinated by insects. Agricultural intensification, however, is one of the main drivers resulting in a serious decline of pollinator populations worldwide. 2. In this study pollinator communities were examined in twelve apple orchards surrounded by either homogeneous or heterogeneous landscape in Hungary. Pollinators (honey bees, wild bees, hoverflies) were surveyed in the flowering period of apple trees. Landscape heterogeneity was characterized in circles of 300, 500 and 1000 m radius around each orchard using Shannon's diversity and Shannon's evenness indices. 3. We found that pollination success of apple was significantly related to the species richness of wild bees, regardless the dominance of honey bees. 4. Diversity of the surrounding landscape matrix had a marginal positive effect on the species richness of hoverflies at 300m, positive effect on the species richness of wild bees at 500m radius circle, while evenness of the surrounding landscape enhanced the abundance of wild bees at 500m radius circle. Flower resources in the groundcover within the orchards supported honey bees. 5. Therefore maintenance of semi-natural habitats within 500m around apple orchards is highly recommended to enhance wild pollinator communities and apple production. Apple is one of the most important insect pollinated crops in the European Union, accounting 51 for 16% of the EU's total economic gains attributed to insect (particularly bee) pollination 52 (Leonhardt et al., 2013). Most apple varieties are cross-pollinated and insect pollination not 53 only affects the quantity of apple production, but can also have marked impacts on the quality 54 of the fruits, influencing size, shape and their market price (Garratt et al., 2014a). The most 55 common insect pollinator of apple is the honey bee (Apis mellifera); however, it is not the bees (Bosch & Blas, 1994). Hoverflies (Syrphidae) have also been observed with pollen loads 63 containing a high proportion of compatible fruit pollen (Kendall, 1973). Agricultural and Forest Entomology 64In the temperate zone, pollinator insects are under threat from a number of limiting 65 factors, such as climate change (Rader et al., 2013), human disturbance (Goulson et al., 66 2008), agricultural intensification (Kearns et al., 1998; Steffan-Dewenter et al., 2005; 67 Fitzpatrick et al., 2006; Memmott et al., 2007), and landscape fragmentation (Aizen & 68 Feisinger, 2003; Diekötter & Crist, 2013), which leads to less effective pollination and 69 reduces agricultural production (Floyd, 1992; Garibaldi et al., 2011a Garibaldi et al., , 2013 (Kremen et al., 2002; Brittain et al., 2013). Maintaining diverse communities, 94Apple is the most important fruit tree in Hungary, as it provides 60 % of the total 95Hungarian fruit production, and currently amounts to 400-600 thousand tons annually on We constructed generalized linear mixed models (GLMM) for each response variab...
To better manage invasive populations, it is vital to understand the environmental drivers underlying spatial variation in demographic performance of invasive individuals and populations. The invasive common ragweed, Ambrosia artemisiifolia, has severe adverse effects on agriculture and human health, due to its vast production of seeds and allergenic pollen. Here, we identify the scale and nature of environmental factors driving individual performance of A. artemisiifolia, and assess their relative importance. We studied 39 populations across the European continent, covering different climatic and habitat conditions. We found that plant size is the most important determinant in variation of per-capita seed and pollen production. Using plant volume as a measure of individual performance, we found that the local environment (i.e. the site) is far more influential for plant volume (explaining 25% of all spatial Published in "Biological Invasions doi: 10.1007/s10530-017-1640-9, 2018" which should be cited to refer to this work. variation) than geographic position (regional level; 8%) or the neighbouring vegetation (at the plot level; 4%). An overall model including environmental factors at all scales performed better (27%), including the weather (bigger plants in warm and wet conditions), soil type (smaller plants on soils with more sand), and highlighting the negative effects of altitude, neighbouring vegetation and bare soil. Pollen and seed densities varied more than 200-fold between sites, with highest estimates in Croatia, Romania and Hungary. Pollen densities were highest on arable fields, while highest seed densities were found along infrastructure, both significantly higher than on ruderal sites. We discuss implications of these findings for the spatial scale of management interventions against A. artemisiifolia.
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