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POLLINATORS POLLINATION AND FOOD PRODUCTION

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THE ASSESSMENT REPORT ON <strong>POLLINATORS</strong>, <strong>POLLINATION</strong> <strong>AND</strong> <strong>FOOD</strong> <strong>PRODUCTION</strong><br />

plants, crops or plant diversity in the crop margins, can have<br />

considerable positive effects on pollinators and pollination<br />

(Garibaldi et al., 2014; Kremen and Miles, 2012; Shackelford<br />

et al., 2013). Traditional land-use systems included<br />

classically low-input low-output systems with high variability<br />

throughout Europe in the form of livestock systems,<br />

arable and permanent crop systems, and mixed systems,<br />

persisted mainly in upland and remote areas (Plieninger et<br />

al., 2006). However, most of these traditionally managed<br />

landscapes have disappeared today due to intensification<br />

or land abandonment (Stoate et al., 2001). Environmentally<br />

friendly management methods, such as organic farming,<br />

diversified farming systems, polyculture farming, crop<br />

rotations, and conservation practices within agricultural<br />

management prescribed under policy instruments such as<br />

agri-environment schemes, are based on such practices<br />

(see more details in Chapter 6; see definitions in the<br />

glossary). Also integrated pest management (IPM), which<br />

combines biological and cultural control with informed<br />

use of chemicals as part of a system approach to provide<br />

targeted and efficient pest management solutions, could<br />

have beneficial effects on pollinators by improving habitat<br />

and minimizing the use of insecticides applied (Gentz et al.,<br />

2010; see also in section 2.3.1).<br />

Several studies suggest that there are positive effects of<br />

diversified farming systems and organic management<br />

relative to conventional monocultures (Kennedy et al.,<br />

BOX 2.2.1<br />

Network concepts<br />

• link: ecological interaction, e.g. trophic or mutualistic<br />

interaction (Bascompte and Jordano, 2007).<br />

• network: a set of nodes (species) connected through links.<br />

In the framework of pollination networks, they are graphical<br />

representations of which plant species interacts with which<br />

pollinator species, and how strong the interactions are.<br />

• link richness: number of realized links in a network.<br />

• connectance: the proportion of possible links that are<br />

realized (Bascompte and Jordano, 2007). Increased<br />

connectance confers higher network stability.<br />

• modularity: Links between nodes are heterogeneously<br />

distributed. In networks, link-dense sections are termed<br />

modules, and species within a module are linked more<br />

BOX 2.2.2<br />

Landscape concepts<br />

tightly together than they are to species in other modules.<br />

The extent to which species interactions are organized into<br />

modules is termed the modularity of the network (Olesen et<br />

al., 2007).<br />

• nestedness: measure that describes interactions in the<br />

network. It represents a pattern of interaction, in which the<br />

set of species with which specialists interact is a subset of<br />

the species with which generalists interact (Bascompte and<br />

Jordano, 2007).<br />

• rewiring: link switching, usually after biotic and/or abiotic<br />

environmental changes that modify the plant-pollinator<br />

community (Hagen et al., 2012).<br />

41<br />

2. DRIVERS OF CHANGE OF <strong>POLLINATORS</strong>,<br />

<strong>POLLINATION</strong> NETWORKS <strong>AND</strong> <strong>POLLINATION</strong><br />

• land cover: observed (bio)physical cover on the Earth’s<br />

surface (Di Gregorio and Jansen, 2005)<br />

• land use: the arrangements, activities and inputs people<br />

undertake in a certain land cover type to produce, change<br />

or maintain it (Di Gregorio and Jansen, 2005).<br />

• habitat: the range of environments suitable for a certain<br />

species (Fischer and Lindenmayer, 2007). This is the range<br />

of locations in which the ecological conditions that allow a<br />

given species to establish and survive exist.<br />

• habitat loss: Loss of habitat for a particular species (Fischer<br />

and Lindenmayer, 2007). In the case of pollinators, this<br />

relates mainly to the loss of nesting and floral resources.<br />

• habitat degradation: gradual deterioration of habitat quality<br />

(Fischer and Lindenmayer, 2007). In these circumstances,<br />

a species can still occur, but may decline, occur at a lower<br />

density, or be unable to breed. For instance, in the case of<br />

pollinators, this can occur when the habitat harbors altered<br />

floral resources, which results in reduced flower numbers<br />

or diminished nutritional value.<br />

• connectivity: measure of connectedness between patches<br />

harboring suitable conditions for a given species. (Fischer<br />

and Lindenmayer, 2007). The opposite of isolation.<br />

• fragmentation: breaking apart of continuous suitable areas<br />

into multiple patches (Fischer and Lindenmayer, 2007).<br />

• landscape: a mosaic of interacting ecosystems; an area<br />

spatially heterogeneous in at least one factor of interest<br />

(Turner, 2005). In the case of pollination and pollinators,<br />

this can be an area heterogeneous in the occurrence of<br />

habitats for different species.<br />

• isolation: measure of separation between existing patches<br />

harboring suitable conditions for a given species (Fischer<br />

and Lindenmayer, 2007). The opposite of connectivity.

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