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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 />

6.4.2.1.4 Reduce pesticide use (includes<br />

Integrated Pest Management)<br />

Developing and implementing cropping systems that entail<br />

no or low use of pesticides, such as organic farming (see<br />

section 6.4.1.1.4) may reduce use and thereby exposure<br />

to pesticides. A major effort in conventional farming has<br />

been to decrease pesticide use through the adoption of<br />

integrated pest management (IPM). This entails a number<br />

of complementing pest control strategies with larger<br />

reliance on biological pest control and changed cultivation<br />

practices that decrease the need to use pesticides and<br />

to apply pesticides only when they are needed, i.e., when<br />

other measures are insufficient and pest abundances<br />

have reached the damage threshold (Desneux et al.,<br />

2007; Ekström and Ekbom, 2011; USDA, 2014; http://<br />

www.ipmcenters.org/). The cultivation practices involved<br />

include crop rotation or mixed cropping, and field margin<br />

management, with co-benefits for pollinators discussed<br />

in section 6.4.1.1. Measures have to be balanced against<br />

the risk of attracting pollinators to or near areas treated<br />

with pesticides.<br />

6.4.2.2 Legal responses<br />

6.4.2.2.1 Registration<br />

The requirement to register a pesticide before use is<br />

a primary level and regulatory policy tool that in many<br />

countries has as one aim: to limit use of bee-toxic pesticides<br />

and implement pollinator-safe use of the pesticide. Pesticide<br />

products are normally registered one by one, separately for<br />

specific uses (e.g., seed dressing, by crop) and separately<br />

in each country; but national registration can also be based<br />

on internationally agreed procedures. A comprehensive<br />

global overview of registration procedures and requirements<br />

is not available. It is, however, safe to say that the principle<br />

and strictness in the rules and procedures for a pesticide<br />

registration vary enormously among countries. An indication<br />

of this variation is given by the Environmental Performance<br />

Index (EPI) that is updated annually since 2000 (http://epi.<br />

yale.edu). It gives a country-based overall assessment of<br />

environmental stress on human health and ecosystems<br />

based on agricultural land use and policies, and includes<br />

pesticide use and regulation.<br />

Information about pesticide use is largely lacking and many<br />

countries even lack sales statistics. The EPI therefore<br />

instead scores the regulatory strength at the registration<br />

of pesticides, and tracks plans by national governments<br />

to phase out and ban a number of Persistent Organic<br />

Pollutants (POP), including nine pesticides now obsolete<br />

in agriculture. Ekström and Ekbom (2011) list the scored<br />

capacity to regulate pesticides of 11 coffee-producing<br />

countries in 2008. The scores range from 0 or 1 (e.g.,<br />

Guatemala, Uganda, and Honduras) to around 20 (e.g.,<br />

Brazil, Indonesia, Peru, and Vietnam), which is level with<br />

the scores of countries with internationally recognized strict<br />

registration rules (New Zealand 22, Sweden 22, US 19).<br />

Other indications of the global variation in the regulation of<br />

pesticide use through registration is given by a regional risk<br />

assessment report for West Africa. It shows that pesticide<br />

regulation in West African countries is weak and that 50% of<br />

pesticide applications in Mali, and 8% of marketed pesticide<br />

products in Niger are reported as unregistered and therefore<br />

entirely lack risk assessments for pollinators (Jepson<br />

et al., 2014). Panuwet et al. (2012) report illegal use of<br />

pesticides, and weaknesses in the regulation and monitoring<br />

of pesticides use in Thailand. More strict registration<br />

rules not only include advanced risk assessments (with<br />

ecotoxicological studies) and rules of use (through labelling),<br />

but can also include responsibilities for the pesticide<br />

producer to mitigate risks and monitor use after registration,<br />

and allows for further restrictions of use should negative<br />

impacts on the environment and non-target organisms<br />

be observed (e.g., EC 2009, see especially Articles 6, 36<br />

and 44). New, even more conservative, risk assessment<br />

systems are being developed for the EU and US that include<br />

measures of lethal and sub-lethal effects for several bee<br />

species in addition to the honey bee (EFSA, 2013; Fischer<br />

and Moriarty, 2014).<br />

6.4.2.2.2 Labelling<br />

The label provides instruction for use of the pesticide<br />

and is considered an important tool to limit risk to nontarget<br />

organisms and humans. Labelling is a regulatory<br />

action that is generally part of the pesticide registration.<br />

No comprehensive summary of labelling internationally<br />

is available. A label may or may not include instructions<br />

directly related to protecting pollinators, but many pesticide<br />

labels include clear warnings about the potential risks<br />

to pollinators. In a survey on registration procedures<br />

including 20 OECD countries worldwide, all countries were<br />

found to use label mitigation to reduce risk to pollinators<br />

including approval restrictions (e.g., excluded crops, rate<br />

restrictions), use restrictions (e.g., not to be used during<br />

flowering), and advice for risk-reducing practices (e.g.,<br />

avoid drift). Most countries (~80%) have a mechanism<br />

for enforcing mandatory label mitigation measures and<br />

restrictions, e.g., such that “do not” statements are legally<br />

binding. Few countries have a formal mechanism for<br />

determining the effectiveness of risk mitigation with labelling<br />

(Alix, 2013; http://www.oecd.org/chemicalsafety/riskmitigation-pollinators/),<br />

which is typically based on incident<br />

monitoring systems.<br />

6.4.2.2.3 Compulsory training and education<br />

Many countries require a licence (certification) for a person<br />

to apply certain pesticides; this licence or certification is<br />

385<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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