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International Review of Waste Management Policy - Department of ...

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61.1.2 Cost benefit Analysis<br />

Cost benefit analysis takes a somewhat different approach. In cost benefit analysis,<br />

the underlying philosophy is to translate impacts into a common metric – that <strong>of</strong><br />

money. Economists are <strong>of</strong>ten keen to make the distinction between valuing<br />

somewhat controversial things – for example, life, or landscapes – and valuing<br />

preferences for (or against) them. At one level, therefore, the approach would appear<br />

to have something in its favour relative to LCA in that it enables various different<br />

types <strong>of</strong> impact across different media quite readily aggregated in a common,<br />

monetary, unit. Another positive feature <strong>of</strong> CBA is that it enables cost to be included<br />

in the analysis. LCAs clearly cannot do this without significant modification.<br />

Through the process <strong>of</strong> discounting, time is accounted for in CBA. This takes on<br />

particular significance when comparing different treatment options with significantly<br />

different pr<strong>of</strong>iles relating to emissions over time. This is a consideration that is not<br />

available to LCA practitioners, though many LCA practitioners appreciate the<br />

significance <strong>of</strong> time.<br />

CBAs also tend to be more concerned with impacts than are LCAs. As mentioned<br />

above, LCAs are insensitive to issues <strong>of</strong> pollutant concentration. In order to evaluate<br />

impacts, economists rely upon credible dose-response relationships. This also<br />

requires some understanding <strong>of</strong> how emissions from a given process can be<br />

translated into concentrations to which receptors are exposed. A major plus point,<br />

therefore – the attempt to estimate actual impacts – immediately becomes a<br />

weakness. There are relatively few pollutants for which quality dose-response<br />

relationships exist. For others, the way pollutants follow particular pathways is not<br />

especially well known so even the exposure term is unclear. For some pollutants,<br />

even where exposures are well known, the dose-response relationships are subject to<br />

uncertainty (sometimes radically so, as exemplified by differences in US and EU<br />

perspectives on the threshold at which dioxins present a hazard to human health).<br />

On top <strong>of</strong> all this, even for those pollutants whose fate is relatively well-known (so the<br />

exposure term is relatively well understood), and those for which the dose-response<br />

relationships are tolerably well understood, there remain issues associated with the<br />

valuation process itself. Many outside the economics discipline criticise the approach<br />

to ‘valuing nature / health’ as ethically indefensible, though economists respond that<br />

choices as to how to make best use <strong>of</strong> scarce resources must be made. However,<br />

within the discipline, debate continues on issues such as how to value mortality and<br />

morbidity, what discount rate to use, etc.<br />

61.2 External Costs <strong>of</strong> Residual <strong>Waste</strong> Treatment<br />

The analysis <strong>of</strong> costs and benefits associated with residual waste treatment options is<br />

a subject which has been discussed in a range <strong>of</strong> studies. Many <strong>of</strong> these look not just<br />

934<br />

29/09/09

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