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Connecting Global Priorities Biodiversity and Human Health

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SIMONE D. MCCOURTIE / WORLD BANK PHOTO COLLECTION / FLICKR<br />

is required to underst<strong>and</strong> the routes of exposure<br />

of wild populations to APIs, <strong>and</strong> how these might<br />

change under different scenarios of future climate<br />

<strong>and</strong> population changes (Boxall et al. 2008; Kim<br />

et al. 2010; Redshaw et al. 2013).<br />

To date, much of the research into the<br />

environmental occurrence, fate <strong>and</strong> effects of<br />

APIs has been focused on high-income countries,<br />

<strong>and</strong> more research effort is needed to underst<strong>and</strong><br />

the situation in least-developed countries, <strong>and</strong> to<br />

devise solutions to related environmental risks<br />

(Kookana et al. 2014). Risk assessments also<br />

need to be strengthened to better account for the<br />

sublethal effects of APIs on wildlife populations<br />

(e.g. in situations of low dose but long exposure),<br />

particularly those that may have knock-on effects<br />

on predator–prey relationships <strong>and</strong> wider food<br />

chain impacts. The potential risks of synergistic<br />

or additive impacts – through combinations of<br />

APIs in the environment, or co-occurrence with<br />

other pollutants (e.g. the added impacts of EE2<br />

in populations also exposed to other endocrinedisrupting<br />

compounds) – also need to be better<br />

understood (Backhaus 2014).<br />

One of the most pressing concerns involves<br />

the manner in which antibiotic, antifungal<br />

<strong>and</strong> antiparasitic APIs in the environment may<br />

present selection pressures for drug resistance<br />

in pathogenic organisms. The increasing threat<br />

of antibiotic resistance, including the emergence<br />

<strong>and</strong> rapid spread of multidrug resistance, means<br />

that there is a dem<strong>and</strong> for novel drug responses<br />

as well as for a greater underst<strong>and</strong>ing of how the<br />

use, abuse or overuse, <strong>and</strong> disposal of existing<br />

antimicrobials might promote the emergence<br />

<strong>and</strong> spread of drug resistance. Related to this is<br />

the need for further research on how other forms<br />

of pollution may enhance selection pressure<br />

for the development of antibiotic resistance in<br />

environmental microbes (Baker-Austin et al. 2006;<br />

Finley et al. 2013), <strong>and</strong> on how drug-resistant<br />

pathogens may be spread by wildlife.<br />

Additional work is also required to prioritize<br />

APIs for more detailed risk assessment. For<br />

example, which types of drugs are likely to enter<br />

the environment in ecologically significant<br />

quantities? It is estimated that over 4000 different<br />

pharmaceutical compounds are currently in<br />

178 <strong>Connecting</strong> <strong>Global</strong> <strong>Priorities</strong>: <strong>Biodiversity</strong> <strong>and</strong> <strong>Human</strong> <strong>Health</strong>

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