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Connecting Global Priorities Biodiversity and Human Health

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intersectoral collaboration on biodiversity–health<br />

linkages.<br />

4. Towards the development of<br />

common metrics <strong>and</strong> approaches<br />

The integration of biodiversity <strong>and</strong> human<br />

health can be facilitated by the use of common<br />

metrics <strong>and</strong> frameworks. Conventional measures<br />

of health are often too limited in focus to<br />

adequately encompass the multiple health<br />

benefits from biodiversity (Corvalan et al. 2005).<br />

Notwithst<strong>and</strong>ing the broad WHO definition of<br />

health described in Chapter 2 of this volume,<br />

traditional measures of health, such as disability<br />

adjusted life years (DALYs) <strong>and</strong> burden of disease,<br />

tend to have a more narrow focus on morbidity,<br />

mortality, <strong>and</strong> disability, <strong>and</strong> fail to capture the<br />

full breadth of the complex linkages between<br />

biodiversity <strong>and</strong> health, including social <strong>and</strong><br />

determinants <strong>and</strong> cultural underpinnings (E.g.<br />

Talbot <strong>and</strong> Verrinder 2009; see also the chapters<br />

on mental health <strong>and</strong> traditional medicine in this<br />

volume). A more holistic approach is necessary.<br />

Examples of such tools on the human health<br />

side include environmental hazard or risk factor<br />

analyses, tools aimed at the identification (<strong>and</strong><br />

reduction) of health disparities <strong>and</strong> inequities,<br />

identifying environmental <strong>and</strong> socio-economic<br />

determinants of disease, <strong>and</strong> conducting<br />

health impact assessments. Complementary<br />

conservation approaches include l<strong>and</strong>scape<br />

<strong>and</strong> seascape change modelling, vulnerability<br />

<strong>and</strong> adaptation assessments, integrated health<br />

<strong>and</strong> environmental assessments <strong>and</strong> ecosystem<br />

service analyses. Valuation approaches, when<br />

being used in conjunction with, or being based<br />

on, tools <strong>and</strong> methods that further contribute to<br />

our underst<strong>and</strong>ing of ecosystem functioning <strong>and</strong><br />

human health linkages, can also be useful tools<br />

for the assessment of benefits <strong>and</strong> trade-offs of<br />

different policy scenarios. Examples of such tools<br />

on the human health side include environmental<br />

hazard or risk factor analyses, tools aimed at the<br />

identification (<strong>and</strong> reduction) of health disparities<br />

<strong>and</strong> inequities, identifying environmental<br />

<strong>and</strong> socio-economic determinants of disease,<br />

<strong>and</strong> conducting health impact assessments.<br />

Complementary conservation approaches include<br />

l<strong>and</strong>scape <strong>and</strong> seascape change modelling,<br />

vulnerability <strong>and</strong> adaptation assessments,<br />

integrated health <strong>and</strong> environmental assessments<br />

<strong>and</strong> ecosystem service analyses. Valuation<br />

approaches, when being used in conjunction with,<br />

or being based on, tools <strong>and</strong> methods that further<br />

contribute to our underst<strong>and</strong>ing of ecosystem<br />

functioning <strong>and</strong> human health linkages, can also<br />

be useful tools for the assessment of benefits <strong>and</strong><br />

trade-offs of different policy scenarios.<br />

Measuring the health effects of ecosystem change<br />

by considering established “exposure” threshold<br />

values can help to highlight biodiversity-healthdevelopment<br />

linkages. Mechanisms linking<br />

ecosystem change to health effects are varied.<br />

For many sub-fields, exposure thresholds or<br />

st<strong>and</strong>ards have been scientifically established that<br />

serve as trigger points for taking action to avoid<br />

or minimize disease or disability. For example,<br />

air quality st<strong>and</strong>ards exist for particle pollution,<br />

WHO has established minimum quantities of per<br />

capita water required to meet basic needs, <strong>and</strong><br />

thresholds for food security define the quantity of<br />

food required to meet individual daily nutritional<br />

needs. Measuring the health effects of ecosystem<br />

change relative to established threshold values<br />

highlights how such change constitutes exposure –<br />

an important principle linking cause <strong>and</strong> disease<br />

or other health effects – <strong>and</strong> encourages action if<br />

thresholds are exceeded.<br />

Given the complexity <strong>and</strong> heterogeneity<br />

of the tools available to assess health <strong>and</strong><br />

biodiversity linkages, complementary crosssectoral<br />

approaches require the development of<br />

a common evidence base across the health <strong>and</strong><br />

conservation sectors. These can extend from the<br />

development of st<strong>and</strong>ardized measures in the<br />

integration of systematic assessment processes<br />

(including environmental impact assessments,<br />

strategic environmental assessments, health<br />

impact assessments <strong>and</strong> risk or strategic<br />

assessments), to more systematic reviews of<br />

research findings, st<strong>and</strong>ardized data collection<br />

forms <strong>and</strong> computerized modelling programs,<br />

<strong>and</strong> the systemic consideration of multiple health<br />

impacts in policy evaluation <strong>and</strong> assessment. The<br />

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

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