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sectoral economic costs and benefits of ghg mitigation - IPCC

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Energy Intensive Industries<br />

Costs <strong>and</strong> Benefits <strong>of</strong> Mitigation in Energy Intensive<br />

Industries<br />

Gina Roos<br />

Summary<br />

As individuals, energy intensive industries have two basic options for mitigating greenhouse gas<br />

emissions: energy efficiency improvements <strong>and</strong> fuel switching. Further synergies could be<br />

obtained from an integrated system approach, but this falls more within the realm <strong>of</strong> the bulk<br />

energy suppliers. There are <strong>costs</strong> <strong>and</strong> <strong>benefits</strong> associated with each <strong>of</strong> the basic options. The<br />

direct <strong>costs</strong> associated with energy efficiency improvements include the cost <strong>of</strong> new technologies<br />

(with a higher depreciation cost on current assets) <strong>and</strong> associated training requirements. Direct<br />

<strong>benefits</strong> center around reduced energy <strong>costs</strong> <strong>and</strong> associated local impacts.<br />

Secondary <strong>costs</strong> <strong>and</strong> <strong>benefits</strong> associated with improvements in energy efficiency are more<br />

dependent on circumstance i.e. whether local supporting industries can adapt or even take<br />

advantage <strong>of</strong> the changes in market dem<strong>and</strong>. The secondary <strong>costs</strong> <strong>and</strong> <strong>benefits</strong> could be<br />

substantial but they <strong>of</strong>ten do not accrue to the industry itself <strong>and</strong> so they need to be considered<br />

from a national perspective.<br />

While the direct <strong>costs</strong> associated with fuel switching will also include technology <strong>and</strong> training<br />

<strong>costs</strong>, there may also be a substantial cost incurred to establish appropriate infrastructure. The<br />

direct <strong>benefits</strong> associated with fuel switching depend on the relative price <strong>and</strong> quality <strong>of</strong> the new<br />

type <strong>of</strong> energy input. With a change in energy markets (as dem<strong>and</strong> for less carbon intensive fuels<br />

increases) it is possible that the price <strong>of</strong> alternative fuels will increase.<br />

The pr<strong>of</strong>ile <strong>of</strong> energy intensive industries differs substantially among developing countries. Less<br />

developed countries tend to have a small industrial base which is specific to the resource base<br />

<strong>and</strong> which generally makes use <strong>of</strong> a dedicated source <strong>of</strong> energy. In this case, a threat to the<br />

energy source could be a threat to the industry itself. More developed countries tend to have a<br />

larger industrial base which utilises a greater diversity <strong>of</strong> resources <strong>and</strong> may have access to more<br />

diverse energy sources as well.<br />

Generally, the cost <strong>of</strong> <strong>mitigation</strong> options will depend on the return on investment period,<br />

proximity to alternative energy sources, <strong>costs</strong> <strong>and</strong> quality <strong>of</strong> alternative energy sources, whether<br />

local synergies are possible <strong>and</strong> whether the mix <strong>of</strong> local <strong>and</strong> foreign inputs is sustainable over<br />

time.<br />

This presentation will present a South African perspective <strong>and</strong> then extend the discussion to<br />

consider implications for the range <strong>of</strong> developing countries, in order to highlight how specific<br />

<strong>costs</strong> can be to local circumstance.<br />

Background<br />

Emissions Inventory<br />

Shackleton et al., (1996) estimated South Africa’s carbon dioxide (CO 2 ) emissions in 1992 at<br />

between 236 <strong>and</strong> 399 million tons per annum. These figures are supported by preliminary results<br />

<strong>of</strong> the South African Emissions Inventory for 1990 (van der Merwe <strong>and</strong> Scholes, 1999), where it<br />

was estimated that approximately 374 million tons <strong>of</strong> CO 2 equivalents were emitted. Carbon<br />

dioxide emissions contributed 81.5%, methane (CH 4 ) emissions 12.5% <strong>and</strong> nitrous oxide (N 2 O)<br />

230

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