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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 />

374<br />

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

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

6.3 TYPOLOGY OF<br />

RESPONSES<br />

Responses can be classified according to: the driver or<br />

threat generating a need for action (e.g., habitat loss,<br />

pesticides), the actors taking the action (from private<br />

individuals to intergovernmental institutions), the type of<br />

action (e.g., policy, financial, etc.) or the scale of impact<br />

(international, regional, etc.). Most sets of responses could<br />

be variously classified according to all these different<br />

classifications, and there is no right way, but there is<br />

usually a way that seems most logical and informative for a<br />

particular subject.<br />

Previous attempts to classify responses relating to<br />

ecosystem services include the Millennium Ecosystem<br />

Assessment (Chopra et al., 2005), the UK National<br />

Ecosystem Assessment (UK NEA; Brown et al., 2014),<br />

and a recent policy analysis carried out by the Food and<br />

Agricultural Organization of the United Nations, which<br />

classified policy responses for pollinators into six themes<br />

(FAO; Rose et al., 2014).<br />

After reviewing these typologies, we decided classifying<br />

by type of action is the most straightforward way to group<br />

BOX 6.1<br />

Types of response<br />

TECHNICAL. These responses are tools and procedures<br />

that people use to manage pollinators or pollination, or land<br />

management approaches that could benefit pollinators.<br />

For example, they include farming or agroforestry practices<br />

such as organic farming and crop rotation (section 6.4.1),<br />

techniques to reduce the impact of pesticide use (6.4.2),<br />

creation or restoration of pollinator habitat (6.4.3) and methods<br />

of bee disease control (6.4.4).<br />

LEGAL. These responses are mandatory rules at international,<br />

national and regional levels (‘hard’ law) and also non-legally<br />

binding treaties, guidelines, standards and codes of practice<br />

developed by law-making institutions (‘soft’ law). For<br />

pollinators and pollination, the responses include habitat or<br />

species protection through conservation designations, and<br />

controlling imports of non-native species, for example.<br />

ECONOMIC. These responses are financial or economic<br />

actions either to either punish bad practices or provide<br />

economic incentives for good practices, related to pollinators.<br />

They include, for example, taxes on pesticides that increment<br />

their costs and reduce the benefits for the farmers (6.4.2),<br />

incentive payments to farmers for pollinator-friendly practices<br />

responses for pollinators and pollination. Classifications<br />

based on actors, scales or threats were less useful, as many<br />

responses involve several actors working together, operate<br />

at several scales or respond to many possible threats.<br />

For our action-based typology, we adapted the Millennium<br />

Ecosystem Assessment model (MEA, 2011), including<br />

their technological, legal, economic and social/behavioural<br />

categories, and modifying their cognitive category to<br />

one that included not only research and indigenous and<br />

traditional knowledge, but also education and awarenessraising<br />

(see definitions in Box). Our definitions were informed<br />

also by the NEA and FAO reports.<br />

The six thematic policy areas identified by the FAO exercise<br />

(Rose et al., 2014) are listed in Table 6.3.1. These were<br />

identified by policymakers and scientists from eleven,<br />

predominantly developing countries, as a set of successful<br />

approaches for decision makers to support. We did not use<br />

them to structure our chapter, because they represent a<br />

mix of policy sectors (e.g., pesticides, nature conservation)<br />

and action types (e.g., economic, social/behavioural and<br />

knowledge). Table 6.3.1 shows where in this chapter<br />

relevant information can be found.<br />

(6.4.1), and markets instruments such as payments for<br />

ecosystem services (6.4.3).<br />

SOCIAL/BEHAVIOURAL: These responses focus on<br />

the informal institutions, governance and decision-making<br />

processes that shape people’s choices. They include<br />

participatory processes to involve communities in decisionmaking<br />

(not the same as involving communities in research<br />

and knowledge gathering), adaptive management of native<br />

habitats, and voluntary codes of practice generated by<br />

community, consumer or industry groups rather than by lawmaking<br />

institutions.<br />

KNOWLEDGE. Knowledge responses include actions that<br />

generate new knowledge and actions that transfer or share<br />

knowledge among groups of actors. They cover scientific<br />

research and monitoring, as well as documenting and sharing<br />

indigenous and local knowledge. They also include education,<br />

outreach, knowledge exchange and collaborative research<br />

activities. These are distinguished from social and behavioural<br />

actions because they focus on the communication or<br />

transfer of knowledge, rather than on decisions, actions and<br />

behaviour.

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