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Chapter 3 Measuring biophysical quantities and the use of ... - TEEB

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<strong>Chapter</strong> 3: <strong>Measuring</strong> <strong>biophysical</strong> <strong>quantities</strong> <strong>and</strong> <strong>the</strong> <strong>use</strong> <strong>of</strong> indicatorsIn addition to <strong>the</strong>se general characteristics, indicators <strong>and</strong> measures need to have anappropriate temporal <strong>and</strong> geographical coverage, <strong>and</strong> ideally be spatially explicit.The importance <strong>of</strong> being spatially explicit has been emphasised in <strong>TEEB</strong> byBalmford et al. (2008). The production, flow <strong>and</strong> <strong>use</strong> <strong>of</strong> <strong>the</strong> benefits <strong>of</strong> biodiversity<strong>and</strong> ecosystems varies spatially, as do <strong>the</strong> impacts <strong>of</strong> policy interventions. Makingavailable data <strong>and</strong> information spatially explicit helps make assumptions explicit,<strong>and</strong> also identifies needs for fur<strong>the</strong>r information. The production <strong>and</strong> <strong>use</strong> <strong>of</strong> <strong>the</strong>benefits <strong>of</strong> ecosystems <strong>and</strong> biodiversity <strong>of</strong>ten take place in different geographicalareas, so a spatially explicit approach is essential to fully evaluate <strong>the</strong> importance <strong>of</strong>ecosystem services <strong>and</strong> <strong>the</strong> impacts <strong>of</strong> related policy actions.2 Existing measures <strong>and</strong> indicatorsBiodiversity, ecosystem <strong>and</strong> ecosystem service indicators <strong>and</strong> measures haveproliferated over <strong>the</strong> past several years, largely in response to <strong>the</strong> setting <strong>of</strong> <strong>the</strong> CBDBiodiversity 2010 Target <strong>and</strong> <strong>the</strong> Millennium Ecosystem Assessment <strong>and</strong> its subglobalactivities. An exhaustive review <strong>of</strong> all <strong>the</strong>se indicators <strong>and</strong> measures is notintended here (see Mace <strong>and</strong> Baillie 2007; Layke 2009 for in depth reviews <strong>of</strong>indicator groups); ra<strong>the</strong>r this section highlights what types <strong>of</strong> indicators <strong>and</strong>measures are available <strong>and</strong> reviews <strong>the</strong>ir relative strengths <strong>and</strong> weaknesses in aneffort to guide <strong>the</strong> selection <strong>and</strong> development <strong>of</strong> appropriate indicators <strong>and</strong> measuresthat can be <strong>use</strong>d to assess <strong>and</strong> predict <strong>the</strong> economic consequences <strong>of</strong> biodiversity<strong>and</strong> ecosystem change.Biodiversity <strong>and</strong> <strong>the</strong> ecosystems that it structures are notoriously complex entities tomeasure <strong>and</strong> assess, <strong>and</strong> this can be undertaken in a variety <strong>of</strong> different ways. TheMA (2005a) <strong>and</strong> Balmford et al. (2008) highlighted that biodiversity indicators areavailable for assessing all <strong>the</strong> different levels <strong>of</strong> <strong>the</strong> biodiversity hierarchy (genes,species, ecosystems), as well as measuring several attributes at <strong>the</strong>se levels, namelydiversity, quantity <strong>and</strong> condition. These three categories <strong>of</strong> attributes are <strong>use</strong>d tostructure this review <strong>and</strong> Table 1. A fourth category <strong>of</strong> indicators is one thatmeasures pressures exerted on <strong>the</strong> environment. This chapter also includes anadditional category focussed on ecosystem service measures <strong>and</strong> indicators, in9

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