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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 />

to a loss of cultural values associated with pollinators.<br />

Native Americans have pursued legal challenges to this<br />

appropriation, but the issues are not resolved and remain<br />

controversial (Johansen, 2007; King, 2013).<br />

5.4.2.8 Pollination governance deficits<br />

The International Risk Governance Council (IRGC, 2009)<br />

has identified governance deficit arising because the<br />

threats to pollination and related risks are not adequately<br />

taken into account in policies and regulations that may<br />

affect pollinators and their services. Their review of the<br />

current regulatory and governance context identified the<br />

main deficit is that most regulations that affect pollinators<br />

and pollination are not specific to pollination (IRGC,<br />

2009). Their report then focuses on five particular aspects<br />

of governance deficits: uncertainty of science; lack of<br />

adequate economic schemes to internalise environmental<br />

costs; absent or inadequate land use policies; inadequate<br />

stakeholder participation and consultation; and difficulty of<br />

medium- to long-term planning. Chapter 6, section 6.2.1.2,<br />

summarises the progress towards reducing these barriers,<br />

and additional responses.<br />

Here we consider impacts that result from the overall deficit<br />

in pollination risk governance, the lack of specificity to<br />

pollination. Governance of pollination extends across many<br />

sectors such as agriculture, trade, nature conservation, and<br />

encompasses the complex roles of, and power relationships<br />

between, for example, civil society, governments, the private<br />

sector, indigenous peoples and local communities from<br />

local to nation-state to global scales (IRGC, 2009). While<br />

governance has many definitions and indicators (Ernstson<br />

et al., 2010), in this context of lack of specificity, the Graham<br />

et al. (2003) definition is useful, as it highlights interactions,<br />

and these pose both risks and opportunities in pollination<br />

governance (0). For example, Ernston et al.’s (2010)<br />

empirical analysis of the governance of pollination and seed<br />

dispersal services in Stockholm highlighted how interactions<br />

lead to key risks including highly contested land use,<br />

numerous, fragmented multi-level administrative units that<br />

trigger under-valuing of pollination services, marginalization<br />

of key actors oriented to protection of pollination, scale mismatches,<br />

networks that cross scales but do not span (e.g.,<br />

cemetery managers do not link with allotment gardeners),<br />

and low levels of flexibility for adaptation.<br />

Analysis of pollination governance within the European<br />

Union identified problems from (horizontal) interplay across<br />

sectors, e.g., contradictory goals between agricultural and<br />

nature conservation that impact on pollination resources,<br />

and from (vertical) interplay between fine-scale cultural<br />

variation in motivations and practices that protect pollination<br />

and the homogenizing effect to EU directives (Ratamäki et<br />

al., 2015). Empirical analysis of the factors affecting farmers’<br />

decisions to adopt pollination-friendly practices in coffee<br />

plantations identified farmers’ perceptions and attitudes,<br />

social-location factors, institutions, certification schemes,<br />

and markets as powerful drivers across local, regional and<br />

larger scales; a conceptual model of these interacting forces<br />

was created to provide the foundation for future research<br />

into interventions that would enhance pollination (Bravo-<br />

Monroy et al., 2015).<br />

5.4.3 Introduction to management<br />

and mitigation options<br />

As noted in the introduction, this chapter addresses<br />

management and mitigation options as appropriate to<br />

different visions, approaches and knowledge systems, of<br />

impacts of the decline of diversity and/or populations of<br />

pollinators. The concept of management and mitigation<br />

options is very similar to Chapter 6 concepts of responses<br />

to risks and opportunities associated with pollinators and<br />

pollination, although perhaps with greater emphasis on<br />

avoiding situations that create a need to “respond”. The<br />

Chapter 6 responses focus on the drivers identified in<br />

Chapter 2 (see Table 6.2.3). Again, many of the people’s<br />

experiences of declines and associated drivers identified<br />

through the assessment for this chapter are the same<br />

as, or similar to, those in Chapter 2, but there are several<br />

differences. Notable differences include the identification in<br />

this chapter of drivers related to loss of access to traditional<br />

lands, and changes to and loss of traditional knowledge,<br />

tenure and governance systems that protect pollination<br />

and pollination governance deficits Table 5-4. Chapter 6<br />

does discuss pollination risk governance deficits, but as a<br />

response rather than a driver.<br />

Table 5-4 also presents the management and mitigation<br />

options considered here in response to these drivers. These<br />

options represent a range of integrated responses that focus<br />

on minimizing impacts in ways that ensure protection of<br />

the many contributions of pollinators as part of supporting<br />

nature’s benefits to people and good quality of life. Chapter<br />

6 also includes material that is relevant to minimizing such<br />

impacts, for example in relation to options such as “diversify<br />

farm systems”. To avoid repetition, we have included crossreferences<br />

to relevant material in this chapter in the Chapter<br />

6 text on responses.<br />

As largely integrated responses, the ten options reviewed<br />

here generally focus on protecting aspects of both nature’s<br />

benefits and good quality of life, and address multiple<br />

drivers. Nevertheless, there are some differences of<br />

emphasis – for example, rights-based approaches respond<br />

directly to the driver of lack of access to traditional lands,<br />

and biocultural conservation explicitly recognizes ecosystem<br />

dynamism and in some cases welcomes invasive species.<br />

Table 5-4 indicates where particular management and<br />

323<br />

5. BIOCULTURAL DIVERSITY, <strong>POLLINATORS</strong> <strong>AND</strong><br />

THEIR SOCIO-CULTURAL VALUES

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