Decarbonisation of residual waste infrastructure: report

Second report and supporting documents from the Independent Review of the Role of Incineration in the Waste Hierarchy in Scotland (Stop, Sort, Burn, Bury?), on decarbonisation of residual waste infrastructure in Scotland.


5 Eunomia Report Results

This section summarises the results from the Eunomia report[71]. These results are also integrated into the discussions above.

5.1 Eunomia Report Results – Overall

The Eunomia report provides a substantial amount of information on how the modelled pathways would affect decarbonisation of incineration in Scotland in each of the three scenarios. This is summarised in Figure 4.

Figure 4: Carbon emissions associated with the baseline and the pathways for each scenario by direct emissions and carbon credits
Graph of carbon emissions associated with the baseline and the pathways for each scenario, split by direct emissions and carbon credits. The figure shows that the advanced sorting pathway results in the largest reduction in direct emissions, although most of the impact of advanced sorting is from recycling credits. The introduction of CCUS results in a reduction of emissions, largely through carbon credits.

There are four types of impact on emissions that emerge from this work:

1. Direct emissions from the incinerator (teal)

2. ‘Recycling credits’ – emissions avoided by using recycled materials rather than virgin ones (orange)

3. ‘Energy credits’ – emissions avoided by displacing other forms of energy generation (heat and/or electricity) (dark pink)

4. ‘Biogenic carbon capture credits’ – the allowance for burning biogenic waste and then capturing the short-cycle GHGs that are then emitted (yellow)

As discussed in Section 3.2.1, none of these currently score as waste sector emissions and only the first type is generally reported (under energy). However, when considering the resource and waste management system as a whole, and when seeking to reach a net zero and more circular economy, they are clearly relevant to enable policy makers to take fully-informed decisions. This is made even more clear by Figure 5, which shows the emissions associated with the production of materials that eventually become the waste that has to be treated, alongside the waste treatment impacts. When such impacts are included, all the scenarios for all the pathways have a net contribution to climate change. End-of-life benefits arising from techniques like CCUS therefore need to be seen in the wider waste and resources systems context.

Figure 5: Carbon emissions associated with the baseline and the pathways for each scenario including material production emissions
A bar chart showing carbon emissions associated with the baseline and the pathways for each scenario including material production emissions. The chart shows that pathway 4, advanced sorting, heat recovery and CCUS, and pathway 3, advanced sorting and CCUS result in similar emissions, but are the lowest emissions pathways. Pathway 2, Advanced Sorting and Heat Recovery and Pathway 1, Advanced Sorting, are similar and the third and forth lowest emissions, respectively.

In all three scenarios and all pathways, the modelling makes an allowance for energy credits. For the baseline and Pathways 1 and 3 this is from electricity generation (29-61ktCO2e) and for Pathways 2 and 4 both electricity and heat (56-72ktCO2e).

5.2 Eunomia Report Results – Advanced Sorting

Removing most of the recyclable plastic from incinerator feedstock via advanced sorting has a substantial and immediate impact on direct emissions as summarised in Table 2. There are also significant (355-463ktCO2e) recycling credits across the three scenarios from advanced sorting.

Table 2: Modelled direct emissions impact for advanced sorting
2035 Scenario Modelled Direct Emissions ktCO2e
Baseline + AS Reduction
BAU 747 329 418 56%
BES-F 741 328 413 56%
BES-P 496 252 244 49%

This strongly supports the argument that implementation of advanced sorting, along with other measures to avoid plastic waste being incinerated (such as waste prevention and better source segregation as set out in Section 4.3) is a vital decarbonisation solution for incineration. In addition, unlike the other options examined, this is applicable to all current and potential incineration facilities, irrespective of location or technology.

5.3 Eunomia Report Results – CCUS

The Eunomia work also indicates that the application of CCUS could deliver substantial carbon savings by capturing fossil GHG emissions (Table 3), based on the optimistic deployment assumptions used.

Table 3: Modelled direct emissions impact for CCUS
2035 Scenario Modelled Direct Emissions ktCO2e
Baseline + AS + CCUS Reduction
BAU 747 329 106 641 86%
BES-F 741 328 110 631 85%
BES-P* 496 252 90 406 82%

*The savings in scenario BES-P are lower because this scenario assumes less plastic is in the residual waste due to upstream policies.

In addition to the recycling credits described above, CCUS could also deliver biogenic carbon capture credits. These are also potentially significant (417-482ktCO2e), though again accounting for them is not currently straightforward.

However, as Section 4.7 sets out, the barriers to deployment of CCUS are considerable, so these reductions are a best case scenario by 2035 that depends on a number of things falling into place. These results underpin the Review’s position that CCUS should continue to be pursued because of its significant potential, but it cannot be relied upon to decarbonise incineration quickly enough to meet Scotland’s ambitions.

5.4 Eunomia Report Results – Heat Networks

Using excess heat from incinerators for other users has a relatively small impact (and once more is not strictly attributed to the waste sector). This supports and confirms the Review’s position that the deployment of heat networks is unlikely to be a major element in incinerator decarbonisation, though it can still play a useful role in improving the overall efficiency of the facilities that are connected in this way.

Contact

Email: zero_waste_inbox@gov.scot

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