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Comparative distribution of forest plant communities of Tara NP according to their CCnp and CCpp (communities are listed in Table 1).

Comparative distribution of forest plant communities of Tara NP according to their CCnp and CCpp (communities are listed in Table 1).

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The apiflora of 34 forest and meadow plant communities in Tara National Park was studied with the aim of assessing their melliferous potential and their contribution to bee pasture during the vegetation period. The melliferous plants were analyzed individually from the aspect of their flowering phenology, abundance, and the intensity of nectar and...

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... Cavities of at least 15 L are required to store the quantity of honey required to overwinter in temperate regions (Seeley 1985) so it is possible that the wild colonies in this study experienced higher mortality than usual. In addition, the study area consisted of forest dominated by beech (Fagus sylvatica), which is wind pollinated and does not produce nectar (Jarić et al. 2013) so it is possible that colony survival was also limited by floral resources (Rutschmann et al. 2023). ...
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Wild-living honey bee (Apis mellifera) colonies naturally nest in old cavity-bearing trees throughout their range, but this important nesting habitat is in global decline. Here we determine the use of ancient, veteran and other listed trees as nest sites by wild-living honey bee colonies in Britain and investigate the effect of tree size, genus and management on occupancy. Over 1,000 trees of special interest (TSIs) were surveyed in southeast England using the Ancient Tree Inventory (ATI) of the Woodland Trust, a charity that protects and promotes trees in Britain. 2% of all TSIs and 4.4% of TSIs with cavities were occupied by wild-living honey bee colonies (n = 21). Occupancy positively correlated with tree diameter, which is surprising given that the overall sample already had a large mean diameter of 1.3 m. Wild-living colonies occupied sweet chestnut (Castanea sativa) more frequently than expected (7% versus 2% overall), probably due to their large mean diameter (1.6 m) and proportion of trees with cavities (73%). Heights of occupied tree cavities (including non-ATI trees) ranged from 0 to 18.2 m with a median of 6.8 m, entrance size ranged from 2.2 to 322 cm² with a median of 33.8 cm² and entrance orientation was not significantly different from random.
... The loss of bee colonies and rising food prices due to global climate change have drawn attention to future approaches and theories that support beekeeping in today's world [1][2][3][4][5]. In this sense, forest ecosystems have become important for beekeeping, as they are a constant source of pollen and nectar for both wild and domesticated honeybees [6][7][8][9][10][11][12]. In terms of forest cover, Türkiye has about 23 million hectares of forest land and a quarter of the annual honey production is obtained from these areas [13]. ...
... The flowering periods of honey plants were first determined from the Flora of Turkey [27][28][29]. The relevant literature was then examined and all information was combined with the field observations [9,[35][36][37][38][39][40][41][42][43][44][45][46][47][48]. During the field observations, at least two plant specimens were collected for both identification and examination of the presence of the nectaria in the lower periphery of the ovaries. ...
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... Entrance height , whereas a cavity of at least 15L is required to store the quantity of honey required to overwinter in temperate regions (Seeley, 1985) so it is possible that the wild colonies in this study experienced higher mortality than usual. In addition, the study area consisted of forest dominated by beech (Fagus sylvatica), which is wind pollinated and does not produce nectar (Jarić et al., 2013) so it is possible that colony survival was also limited by oral resources. ...
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... Un inventaire des plantes basé sur la méthode des quadras a été réalisé pour chaque type d'élément paysager présent (tableau 5). Un coefficient appelé « coefficient coenotic d'intérêt apicole » (CCm) est calculé selon la méthodologie établie par Bagella et al. (2013) et Jarić et al. (2013). Appliqué à chaque élément paysager il indique l'intérêt apicole théorique des éléments paysagers en tenant compte de plusieurs variables telles que le niveau de production individuelle en nectar (inp) et en pollen (ipp) des plantes, leur abondance (ou recouvrement) au sein des éléments paysagers et le rapport entre le nombre de plantes d'intérêt apicole et la richesse floristique de chaque élément paysager. ...
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In the years 2007-2009 the differentiation of flora on the area of balks of different length was assessed. The studies of flora were carried out in the area of 7772 ha of Ińsko Lakeland in Poland. For the detailed studies 72 balks were chosen, formed from roadsides and divided into two groups according to the length. Topographic maps in the scale 1:10 000 were used for the assessment of earlier functions of the studied objects. It was shown that in the areas of an arable surface characteristic of average farms as regards their size in the European Union, the size of arable land and the length of balks related with it had an influence on phytodiversity. Despite the fact that the number of phytocoenoses was larger on shorter balks, their specific poverty did not affect biodiversity significantly. The presence of a large number of melliferous species influenced not only phytodiversity of balks, but it also resulted in the improvement of nutritive conditions, among others, for bees. A larger number of plant species on long balks, including also melliferous and therapeutic species, proves correct management of the production space in a long time period.
... The ecosystem potential to produce honey is evaluated far less often, though some indirect indicators used to map pollination potential (like floral resources) could be adapted for that purpose quite readily. Jarić and co-authors (2013) proposed a formula by which the melliferous potential of plant communities could be estimated, applying this subsequently in assessing selected forest and meadow ecosystems in Serbia (Jarić et al., 2013;Macukanović-Jocić and Jarić, 2016). However, their calculations of honey potential did not account for honeydew as an underpinning raw material, and for the impact of different environmental conditions in determining how varied actual production of nectar and pollen by individuals of the same plant species might be (Demianowicz et al., 1960;Szklanowska, 1973). ...
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The estimation of the value of nature in terms of benefits derived by humans is becoming increasingly popular in environmental assessments and spatial planning worldwide. In line with this approach, the value of any ecosystem can be determined on the basis of its potential (capacity), or the actual amount of goods and services delivered (flow). The aim of this work was to develop indicators of the potential of ecosystems to deliver services related specifically to bees, i.e. to pollination and honey production. A new operational definition of ecosystem potential dedicated to the evaluation of bee-related services was introduced and applied. Two ratio scales were constructed, showing the potential abundance of nesting wild bees (indicating pollination) and the availability of honey substrates (indicating honey production). The expert assessment carried out was closely linked to real regional data. Specific values were assigned to 29 types of ecosystem relevant to bees and identified in the lowland rural landscape of Central Europe. The original scales for the indicators were then classified into the 0–10 ecosystem capacity scale. A specific study area in north-eastern Poland (815 km²) was chosen to show a possible spatial pattern for ecosystem potential in relation to the two bee-related services.