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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 />

be it difficult to identify which land owners could receive a<br />

payment for supporting them.<br />

In France, an agri-environment scheme under the European<br />

Common Agricultural Policy (i.e., dispositif apiculture<br />

API: http://www.eure.gouv.fr/layout/set/print/Politiquespubliques/Agriculture/Mesures-Agro-Environnementales)<br />

pays beekeepers to place hives in areas of high biodiversity.<br />

Its stated aim is to enhance the pollination provided by<br />

honey bees, although the effect of this on pollination has not<br />

been measured.<br />

6.4.3.4 Social and behavioural responses<br />

Responses based on influencing social attitudes have<br />

occurred in many places around the world. A number of<br />

initiatives related to pollinator conservation have garnered<br />

significant public support, including citizen science data<br />

collection and on-ground actions (see section 6.4.6.3.4).<br />

However, there have not been systematic studies of their<br />

effectiveness, so that while we have identified some of<br />

the strategies for how nature conservation strategies<br />

for pollination could benefit from social and behavioural<br />

responses (Table 6.4.3), there is little to report regarding<br />

assessment of the effectiveness of these strategies.<br />

Social action also requires an appreciation of the threats to<br />

pollinators, which might be lacking in many communities.<br />

For example, people in the Cook Islands proved to be open<br />

to the idea that hunting restrictions might be necessary<br />

to protect fruit bats, but only after they were made aware<br />

that hunting was a significant threat to these pollinators<br />

(Cousins and Compton, 2005). In Europe surveys revealed a<br />

positive attitude towards the planting of wildflower strips for<br />

pollinator conservation among both farmers and the general<br />

public (Jacot et al., 2007), indicating that some communities<br />

are inclined to support active ecological restoration options.<br />

TABLE 6.4.3<br />

Summary of evidence for responses relating to nature conservation<br />

395<br />

Response Main drivers Type of response Status Scientific evidence<br />

Manage or restore native habitat<br />

patches to support pollinators<br />

Increase connectivity of habitat<br />

patches<br />

Manage invasive species (plants,<br />

pests, predators or pollinators)<br />

that diminish pollinators or<br />

pollinator habitat<br />

Targeted conservation of<br />

specific pollinator species or<br />

groups of species (includes ex<br />

situ conservation of threatened<br />

species, includes species of<br />

special cultural value)<br />

Targeted conservation of<br />

pollinators associated with<br />

specific plant species threatened<br />

by pollination deficit<br />

Establish protected areas or<br />

improve the quality of existing<br />

ones (including protected areas<br />

of cultural value)<br />

Payment for ecosystem services<br />

Maintain sacred and other<br />

culturally protected areas that<br />

support pollinators<br />

Increase taxonomic expertise<br />

on pollinator groups (formal<br />

education/training) and<br />

technology to support discovery<br />

and identification<br />

Land use and its changes<br />

(2.1)<br />

Changes in land cover<br />

and spatial configuration<br />

(2.1.2)<br />

Technical<br />

6.4.3.1.1.<br />

Technical<br />

6.4.3.1.2.<br />

Invasive species Technical<br />

6.4.3.1.4.<br />

Multiple, interacting<br />

threats<br />

Multiple, interacting<br />

threats<br />

Land use and its changes<br />

(2.1)<br />

Land use and its changes<br />

(2.1)<br />

Land use and its changes<br />

(2.1)<br />

All<br />

Technical<br />

6.4.3.1.5.<br />

Technical<br />

6.4.3.1.5.<br />

Established<br />

Tested<br />

Tested<br />

Tested<br />

Tested<br />

Increases diversity and abundance of<br />

pollinating insects<br />

WELL ESTABLISHED<br />

Some evidence that habitat<br />

connections help pollinator movement<br />

and gene flow<br />

ESTABLISHED BUT INCOMPLETE<br />

Case study evidence of some benefits<br />

to pollinator species, but eradication is<br />

difficult to achieve<br />

ESTABLISHED BUT INCOMPLETE<br />

Examples exist for a limited range of<br />

taxa<br />

ESTABLISHED BUT INCOMPLETE<br />

One European example known, for<br />

dittany<br />

(Dictamnus albus)<br />

INCONCLUSIVE<br />

Legal 6.4.3.2.2 Established Protected areas host species diversity,<br />

but it is difficult to determine the impact<br />

of legislation in achieving protection<br />

WELL ESTABLISHED<br />

Economic 6.4.3.3. Tested Ecosystems services payments have<br />

been established for other services<br />

(watershed protection, carbon<br />

sequestration) but no examples for<br />

pollination<br />

ESTABLISHED BUT INCOMPLETE<br />

Social/behavioural<br />

6.4.3.2.2<br />

Knowledge<br />

6.4.3.5.<br />

Established<br />

Tested<br />

Protected areas host species diversity,<br />

but few case studies<br />

ESTABLISHED BUT INCOMPLETE<br />

(see also 5.4.2.4)<br />

Significant training has been achieved<br />

in a number of countries<br />

WELL ESTABLISHED<br />

6. RESPONSES TO RISKS <strong>AND</strong> OPPORTUNITIES ASSOCIATED<br />

WITH <strong>POLLINATORS</strong> <strong>AND</strong> <strong>POLLINATION</strong>

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