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...

Wild bees are important contributors to the pollination ecosystem service, but they are especially vulnerable to agricultural intensification which causes the loss and fragmentation of natural habitats. We monitored bumblebee populations (Bombus spp.) in 14 grassland patches incorporated into the agricultural habitat mosaic in the Mezőföld region, Hungary. We asked how bumblebee populations were affected by local vegetation quality and the presence of various landscape elements, including fields in agri-environmental schemes, at various spatial scales. A stratified analysis revealed that vegetation quality, especially the lack of weeds, was the most important local factor that positively affected both bumblebee abundance and species number. We found no significant landscape scale effects between 50-250 m. Between 500-1000 m grassland area in the landscape had consistently significant positive effect on species richness. At the 2 km scale the extent of arable fields had a negative impact on both abundance and richness. A higher percentage area of arable fields in the landscape participating in agri-environmental schemes had no positive effect on bumblebee abundance or species richness. Considering all local and landscape effects and their possible interactions, model selection and variance partitioning revealed that local factors were the most important determinants of bumblebee richness and abundance. Local and landscape factors had high shared variance but did not interact with each other. The present study indicated that small scale landscape composition had the lowest importance, but larger scale landscape composition was significant, most likely because bumblebees can forage far from their nests. If we are able to provide good quality grassland patches incorporated into the agricultural habitat mosaic, then we can build on the strong spill over propensity of bumblebees and can expect their contribution to the pollination of various crops.Key words: Bombus, pollination, landscape complexity, grassland, agri-environmental scheme INTRODUCTIONFrom the second part of the 20th century, the intensification of agricultural production became higher than ever before. The intensive agricultural * This paper is dedicated to Prof. László Papp, in honor of his 70th birthday and his outstanding contribution to the fields of dipteran taxonomy and ecology.Acta Zool. Acad. Sci. Hung. 62, 2016 388 SÁROSPATAKI, M., BAKOS, R., HORVÁTH, A., NEIDERT, D., HORVÁTH, V. et al. management resulted in general biodiversity decline in Europe (de Heer et al. 2005), leading to a decrease in the level of ecosystem services including pollination (Murray et al. 2009). The landscape change and fragmentation of habitats through agricultural intensification created structurally poor landscapes (Tilman et al. 2001), and these affected the diversity and abundance of pollinators, especially wild bees (Biesmeijer et al. 2006, Goulson et al. 2010, Kremen et al. 2002, Potts et al. 2010.Pollination is an important ecosystem service, provided prima...