Environmental Engineering Reference
In-Depth Information
Element
Headline (category)
Examples of indidual indicators
Ozone depleting substances
Greenhouse gases
Impacts on air
Acid gases
pH
water use
Impacts on water
eutrophication inputs
biological functionality
chemical functionality
Impacts on soil
physical functionality
Environmental
biodiversity / conservation
Impacts on ecology
functionality
productivity
landscape impacts
built environment
Intrusiveness
flood risks
material
energy
Resource use
waste disposal
Fig. 20.8 Example indicator hierarchy for the environmental element of sustainable development
then individual indicator assessments may need to be made, but presumably only
within those headline categories for which consensus could not be reached.
Double counting is a potentially serious issue that gives undue weight to an issue
if it is represented by more than one criterion. However, in attempting to avoid
double counting, there is a danger of oversimplification, and that key issues that
resonate with stakeholders are lost (Mitchell 2005 ), as discussed in Section 20.2.1.3 .
Grouping indicators under headlines balances the need to avoid double counting
with the need to avoid over-simplification.
The importance of this kind of structured approach to considering indicators
reflects the functionality of project based decision making, where reaching con-
sensus between different stakeholders for a particular site. Sustainability appraisal
is specific to the circumstances of a particular site or project. It depends on the spe-
cific environmental, economic and social context of the site being considered, and
also the people and organisations involved. The reason for carrying out sustainabil-
ity appraisal will be related to gaining some form of agreement from planning or
regulatory authorities or a local community, or some form of reassurance from a
corporate point of view that the site owner can defend their decision as sustainable,
or some combination of similar reasons. Many factors important in sustainability
are likely to be viewed subjectively by different stakeholders, for example impact of
a project on a historic built environment. Hence, the only real decision will be that
the different stakeholders involved agree that for a particular criterion the most sus-
tainable approach is “x” . Therefore, from a pragmatic point of view, sustainability
appraisal only needs to go as far as is necessary to reach this consensus, and the
 
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