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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 />

this bee species (e.g., Richards, 1984). Alfalfa (Medicago<br />

sativa) is a Eurasian crop introduced to North America as an<br />

important foodstuff for cattle, but honey bees are often poor<br />

pollinators of alfalfa (Free, 1993). Following a presumably<br />

earlier unintentional introduction of M. rotundata to the east<br />

coast of North America around 1930 from Eurasia, where<br />

it is native, the species had made its way to central and<br />

western USA by the 1950s, where large areas of alfalfa<br />

were grown for seed. Not only is M. rotundata an excellent<br />

pollinator of alfalfa, it also nests gregariously in artificial<br />

domiciles. Targeted research revealed important aspects<br />

of its biology, and a viable industry in alfalfa leafcutter bee<br />

management became established (Stephen 1961, 1962;<br />

Bohart, 1962; see also Pitts-Singer and Cane, 2011).<br />

Official figures on the size of the industry (number of bees<br />

produced) are lacking, but an estimated 800 million alfalfa<br />

leafcutter bees are traded commercially per year and a<br />

further 1,600 million are encouraged in and around alfalfa<br />

fields by bee-friendly farming practices and provision of<br />

nesting medium in the USA (Peterson et al., 1992, Reisen<br />

et al., 2009), with a sizable industry in Canada, too, that<br />

also supplies M. rotundata from largely pathogen-free<br />

areas in Canada to the US market. Land surrounding<br />

alfalfa fields in the USA is also occasionally managed for<br />

the ground-nesting alkali bee Nomia melanderi, which is<br />

also an efficient alfalfa pollinator. Management involves not<br />

only the enhancement of natural nesting sites but also the<br />

actual building of completely artificial nesting sites, called<br />

bee beds (Johansen and Mayer, 1976). The species has not,<br />

though, been commercialised to any extent (Cane, 2008),<br />

and neither has Rhophitoides canus, another groundnesting<br />

solitary bee successfully managed for alfalfa seed<br />

production in eastern Europe (Ptacek, 1989 in Bosch,<br />

2005). Pollination of alfalfa makes a strong case for the<br />

diversification of managed pollinators.<br />

Leafcutter and mason bees are all solitary, and the diversity<br />

of these and other species employed in (semi-)commercial<br />

enterprises remains small. In Japan, the native Osmia<br />

cornifrons has been successfully managed since the 1940s<br />

for improved apple pollination (Yoshida and Maeta, 1988;<br />

Maeta, 1990), where it is traded and used to pollinate 70%<br />

of the apple production area (Maeta, 1990). In Europe, an<br />

estimated one million Osmia bicornis (=rufa) bees are traded<br />

per year for apple and other fruit pollination by 10-20 small<br />

companies, while Osmia cornuta in central and southern<br />

Europe and Osmia lignaria in the US and Canada are being<br />

traded to the same or greater extent for the pollination of<br />

orchard crops (Bosch and Kemp, 2002). In the tropics,<br />

other largely solitary species such as carpenter bees (genus<br />

Xylocopa) have been experimentally managed as potential<br />

pollinators of crops such as passion fruit (Passiflora edulis,<br />

Junqueira et al., 2012; Junqueira et al., 2013), whose flower<br />

morphology does not allow efficient pollination by honey<br />

bees. In Australia, the native blue-banded bee Amegilla<br />

chlorocyanea is as efficient as bumble bees in pollinating<br />

tomatoes grown in glasshouses (Hogendoorn et al., 2006).<br />

This list in not exhaustive.<br />

3.3.6 Other managed pollinators<br />

The commercial management of other insect pollinators has<br />

great potential (Kevan et al., 1990, Howlett, 2012), but is<br />

currently on a much smaller scale than that of honey bees,<br />

bumble bees or solitary bees. Flies were occasionally used<br />

for strawberry pollination in the 20 th Century (Free, 1993).<br />

However, this practice has been largely replaced by Bombus<br />

pollinators, considered more efficient crop pollinators than<br />

flies. Bumble bees need to gather large quantities of pollen<br />

and nectar for their offspring and so are far more consistent<br />

flower visitors than flies (Free, 1993). Blowflies and syrphid<br />

flies can also be important pollinators of crops grown for<br />

seed in cages (to control cross-pollination), e.g. the blowfly<br />

Calliphora vomitori for the pollination of onion grown for<br />

seed (Currah and Ockendon, 1983), and are also available<br />

commercially. As mentioned above, another species of<br />

fly, Lucilia sericata (common green bottle fly), is available<br />

commercially for pollination (section 3.2.3).<br />

3.4 TRENDS IN INTRODUCED<br />

<strong>POLLINATORS</strong> <strong>AND</strong><br />

TRANSMITTED PATHOGENS<br />

3.4.1 Outline of section<br />

This section provides a general overview of trends in<br />

pollinator introductions to novel habitats and its ecological<br />

effects, especially those related with disease transmission.<br />

It discusses the different concepts related to pathogen<br />

transmission and the existing evidence for honey bees,<br />

bumble bees, and leaf cutter bees. The frequency of<br />

introduced species and the prevalence of different infectious<br />

diseases on a worldwide scale is summarised according to<br />

the existing evidence.<br />

3.4.2 Ecological effects of<br />

introduced pollinators<br />

In this section, the term ‘introduced species’ will be used as<br />

synonymous with ‘non-native species’ to denote a species<br />

that lives outside its original distributional range, which<br />

has arrived there by human activity, either deliberate or<br />

accidental, and is able to survive and reproduce in the new<br />

habitat without human assistance. An introduced species<br />

might become an invasive species if it can outcompete<br />

169<br />

3. THE STATUS <strong>AND</strong> TRENDS IN <strong>POLLINATORS</strong><br />

<strong>AND</strong> <strong>POLLINATION</strong>

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