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 />
210<br />
4. ECONOMIC VALUATION OF POLLINATOR GAINS<br />
<strong>AND</strong> LOSSES<br />
INTRODUCTION <strong>AND</strong><br />
OUTLINE<br />
Pollinators are a key component of global biodiversity,<br />
providing vital ecosystem services to crops and wild plants<br />
(Klein et al., 2007; Potts et al., 2010; for more details, see<br />
Chapters 2 and 3). However, there is evidence of recent<br />
decline in both wild and managed pollinators and parallel<br />
decline in the plants that rely upon them (Potts et al., 2010;<br />
Biesmeijer et al., 2006). Declining pollinators can result in<br />
the loss of pollination services, which can have important<br />
negative ecological and economic impact that could<br />
significantly affect the maintenance of wild plant diversity,<br />
wider ecosystem stability, crop production, food security<br />
and human welfare (Potts et al., 2010).<br />
The importance of animal pollinators in the functioning of<br />
most terrestrial ecosystems has been extensively described<br />
and analysed in a broad range of scientific literature (see<br />
Chapter 3). The importance of pollinators and pollination<br />
services can often be evaluated in economic terms in order<br />
to link decisions made with economic consequences (Daily<br />
et al., 1997; Daily et al., 2000). The economic assessment<br />
of pollinators and pollination services is measured by their<br />
total economic value (TEV; summarized in Figure 4.1).<br />
Economically, the total value of an ecosystem service is<br />
the sum of the utilitarian reasons a society has to maintain<br />
it. This is typically divided into (i) use values, the values of<br />
the benefits that people gain from the functioning of the<br />
ecosystem (e.g., the pollination of crops); and (ii) non-use<br />
values, the values that people attribute to the existence of<br />
an ecosystem service, regardless of its actual use (existence<br />
value, e.g., the existence of pollinators) or the value they<br />
place on the potential to use the ecosystem service in the<br />
future (bequest value e.g., species that could pollinate<br />
crops in the future). Pollinators and pollination have a use<br />
value because the final product of their service can be<br />
used directly by humans, such as with crops or honey (a<br />
consumptive use), as well as the leisure and aesthetics<br />
created by the presence of pollinated wild plants within the<br />
landscape (a non-consumptive use value). Pollination can<br />
also provide indirect use values through supporting the<br />
reproduction and genetic diversity of wild and cultivated<br />
plants that benefit humans. Finally, the use value of<br />
pollinators and pollination also contains an option value<br />
(the value given to preserve a choice option of pollinators<br />
and pollination-dependent products in the future) and the<br />
insurance value (the capacity of pollinator communities to<br />
reduce the current and future risks associated with using<br />
pollination services; Baumgärtner and Strunz, 2014).<br />
However, not all these values are directly related to<br />
markets (only the consumptive uses that are marketed).<br />
Consequently, the impacts of management on pollination<br />
services could be under-estimated when making decisions,<br />
potentially resulting in inefficient or unsustainable use of<br />
resources. Economic valuation provides two forms of<br />
essential information to stakeholders. Firstly, it highlights<br />
the economic contribution of pollinators to the various<br />
benefits provided to the agricultural sector and society.<br />
Thus, it tells the decision maker how much net benefit arises<br />
from different interventions, which in turn allows for the<br />
optimal design of such interventions. Secondly, economic<br />
valuation can assess the impact of variations in pollinator<br />
population on the economic welfare of different groups of<br />
people, such as farmers or consumers. By considering<br />
this information, decision makers, from both the public and<br />
private sectors, are able to make better-informed decisions<br />
about the impacts of proposed investments, public<br />
spending or management changes. This chapter aims to<br />
review the conceptual framework and the various methods<br />
of economic valuation of pollinators and the effective use<br />
of these valuations. There are also other value systems,<br />
including spiritual, cultural and indigenous and local<br />
knowledge values, which can inform decision-making, these<br />
are reviewed in Chapter 5.<br />
In this chapter, pollination services are considered an<br />
ecosystem service, i.e., “the conditions and processes<br />
through which natural ecosystems, and the species that<br />
make them up, sustain and fulfil human life” (Daily, 1997).<br />
The evidence is clear for wild pollinators that are provided by<br />
natural ecosystem as forests or soils, but some ambiguity<br />
remains when considering managed pollinators as they can<br />
be considered as livestock, far from nature. However, they<br />
are used to provide services in agricultural systems that,<br />
while heavily managed, remain a functioning ecosystem<br />
(or agro-ecosystem, see Swinton et al., 2006; Swinton et<br />
al., 2007; Zhang et al., 2007). Thus described, pollination<br />
services from managed pollinators are ecosystem services<br />
offered by the agro-ecosystem. Unlike many well-quantified<br />
ecosystem services, pollination services are provided by<br />
mobile organisms that can move in uneven patterns across<br />
their foraging range, making them more difficult to assess<br />
accurately (Kremen et al., 2007). Furthermore, pollination<br />
services are an intermediate service, a service that is not<br />
beneficial in itself but instead underpins other benefits,<br />
such as crop production and landscape aesthetics, by<br />
helping produce pollinator-dependent crops for human<br />
food and nutrition security, along with the reproduction of<br />
certain plants (Fisher et al., 2009; Mace et al., 2012). The<br />
value of intermediate services is assessed not by looking at<br />
their direct consequence (pollination) but by their impacts<br />
on the final goods that are produced (food, honey, etc.).<br />
These final goods have a market price which gives some<br />
reasonable indication of their use value (note that prices<br />
may under-estimate values). However, pollinators are also<br />
final ecosystem services in themselves because of the value<br />
associated with their existence. Although this complicates<br />
the challenge of accurately valuing pollination services<br />
more substantial, these abstract benefits can still be valued