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Inclusion of Consumption of carbon intensive materials in emission - - PowerPoint PPT Presentation

Inclusion of Consumption of carbon intensive materials in emission trading systems An option for carbon pricing post 2020 Roland Ismer/Karsten Neuhoff/Manuel Haussner/Vera Zipperer/ 1 Motivation 2 The mechanism 3 Technical Implementation


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Inclusion of Consumption of carbon intensive materials in emission trading systems An option for carbon pricing post 2020

Roland Ismer/Karsten Neuhoff/Manuel Haussner/Vera Zipperer/…

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1

Motivation

2

The mechanism

3

Technical Implementation

4

Conclusion

Inclusion of Consumption of carbon intensive materials in emission trading systems

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SLIDE 3

1.

Industrial activities with the highest cost increase from carbon pricing

(Assumption: carbon price 20 €/t CO2 and electricity price increase 10 €/MWh)

Inclusion of Consumption of carbon intensive materials in emission trading systems

Industrial emissions dominated by production of carbon intensive materials

Production of cement and steel alone accounts for 38% of European industry emissions:  Important to realize mitigation opportunities of selected carbon intensive materials  Production and use of these materials justifies focused attention

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Three groups of emission reduction opportunities for carbon intensive materials

Inclusion of Consumption of carbon intensive materials in emission trading systems

1.

 Porftfolio of mitigation options to achieve deep decarbonisation (G7) with 80-95% reductions (EU)  Similar picture for other material sectors like steel  To date only progress on Group 1: fuel shifting and some process efficiency  Group 3 largely unexplord (materials efficiency and substitution) and no progess in Group 2 (CCS)

Group 2: Carbon focused process innovation Group 1: Fuel shifting and production efficiency Group 3: Material efficiency and subsitution 0% 20% 40% 60% Biomass (waste) Pre-treated (waste) Energy Efficiency Carbon Capture and Storage Innovative Cement Based Materials Clinker Substitution Substitution/ Efficient Use

  • f Cement

By what percentage can cement sector reduce its emissions

IEA (low demand scneario) Ecofys/WWF UK Committee on Climate Change Cembureau Mineral Products Association WBSD/ECRA Technology Report

Example Cement

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Carbon pricing can in principle create incentives for all mitigation opportunities

1.

Inclusion of Consumption of carbon intensive materials in emission trading systems

Note: Additional need for strategic (public) innovation investment and programs or policies to

  • vercome inertia (outside of scope of this presentation).

Global Full Auction- ing

Emissions reductions through Role of carbon pricing Fuel shifting and production efficiency Carbon focused process innovation Material efficiency and substitution Incentives for improving carbon efficiency of materials production Consistent mechanism including clarity on costs allocation Makes efficient material use / low carbon material competitive Group 1 2 3

 With global converging carbon pricing, all allowances can be auctioned also in materials production.  In such a scheme carbon price creates the full incentive for all Groups of mitigation options.

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Free allocation for carbon leakage protection limits incentives from carbon price

1.

  • 1. Historic

emissions

  • 3. Recent

production and historic intensity dynamic

  • 4. Recent

production and benchmark

Basis of free allowance allocation

  • 2. Historic

production and benchmark

Emissions reductions through Fuel shifting and production efficiency Carbon focused process innovation Group 1 2 Role of carbon pricing Incentives for improving carbon efficiency of materials production Consistent mechanism including clarity on costs allocation Material efficiency and substitution Makes efficient material use / low carbon material competitive 3

Inclusion of Consumption of carbon intensive materials in emission trading systems

No matter how allowances are allocated for leakage protection, significant distortions remain:

  • If based on historic emission (intensities) discourages efficiency improvements
  • > Can be improved with use of benchmarks (2 & 4)
  • If based on historic output, then allocation can deviate significantly from emissions
  • > Can be avoided with use of recent production volumes (3 & 4)
  • >But further limits price pass through for materials efficiency & substitution (3 & 4)
  • If consumers don’t pay carbon, no business case for large scale use of CCS type technologies

Incentive: Full Some Small

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Adding inclusion of consumption can restore the carbon price and incentives

1.

Inclusion of Consumption of carbon intensive materials in emission trading systems

Historic emissions Recent production and historic intensity dynamic Recent production and benchmark

Basis of free allowance allocation

Historic production and benchmark

Emissions reductions through Fuel shifting and production efficiency Carbon focused process innovation Group 1 2 Role of carbon pricing Incentives for improving carbon efficiency of materials production Consistent mechanism including clarity on costs allocation Material efficiency and substitution Makes efficient material use / low carbon material competitive 3

Recent production and benchmark Recent production and benchmark + IoC

 Free allocation based on recent production and benchmark eliminiates price pass through.  Can be corrected with a consumption charge on carbon intensive materials at benchmark rate.  Thus full incentives for Mitigation Opportunities in Group 2 and 3 are restored.

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1

Motivation

2

The mechanism

3

Technical Implementation

4

Conclusion

Inclusion of Consumption of carbon intensive materials in emission trading systems

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The mechanism and its incentives

2.

Inclusion of Consumption of carbon intensive materials in emission trading systems

 Follows model of existing consumption charges (excises) on fuel, tobacco, alcohol etc.  Restores incentive for mitigation opportunities in group 2 and 3.

Process action How IoC strenghtens incentives for mitigation Creation of liability per ton of e.g. steel (benchmark rate times carbon times ton of steel) Group 2: Credible perspective for carbon capture: extra costs allocated to consumers, not (cross-) subsidized Passing on liability Group 3: Increases profitability of materials efficiency and substitution with charge on carbon intensive materials Liability suspended Release for consumption: Suspended liability becomes due Companies can inform consumers about level of charge to enhance awareness Information on embedded carbon engages consumers

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No double charging (illustrative example cement)

2.

With global carbon price, cost

  • f acquiring

allowances added to product price.

Product price

Consumption charge added to product price Production cost Cost of emission allowances Production cost Free allocation compensates allowance cost Production cost

Inclusion of Consumption of carbon intensive materials in emission trading systems

 Level playing field maintained, as charge applies to all steel (irrespective of origin).  Consumption charge volume equivalent to revenue if allowances are auctioned to industry.  Consumers face same cost as in world of global carbon price and full auctioning. Free allowance allocation at benchmark per (recent) output reduces cost and product price. Consumption charge at benchmark restores product price as if

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The case of import and export

2.

Inclusion of Consumption of carbon intensive materials in emission trading systems

 No differentiation how and where product was produced  No effect on competitiveness of the European steel sector because imports are charged as well

Foreign territory

Process action Creation of liability per ton of e.g. steel (benchmark rate times carbon times ton of steel) Passing on liability Liability suspended Release for consumption: Suspended liability becomes due Companies can inform consumers about level of charge to enhance awareness Process action Acquittal of liability upon export Creation of liability upon import

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The effect of combining benchmark based allocation with IoC

Inclusion of Consumption of carbon intensive materials in emission trading systems

  • Ensures full carbon price incentive for all groups of mitigation options.
  • Clarity on allocation at full benchmark level because no need to trade off with

incentive in value chain  Enhances long-term investment framework

  • No competitive disadvantage for companies because all competitors (also close

substitutes) are treated the same.

  • With free allocation at full benchmark level robust leakage protection also for

high carbon prices and therefore long-term clarity for decarbonisation.

2.

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1

Motivation

2

The mechanism

3

Technical Implementation

4

Conclusion

Inclusion of Consumption of carbon intensive materials in emission trading systems

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Administrative Implementation: Domestic case

3.

Inclusion of Consumption of carbon intensive materials in emission trading systems

 Reporting to existing national authorities, e.g. BAFA (DE), Environment Agency (UK)

Process action Quarterly reporting to national authority: Creation of liability per ton of e.g. steel (benchmark rate times carbon times ton of steel) Liability held + Liability created

  • Liability passed with

products Passing on liability Liability held + liability received

  • Liability acquitted

(lodging of declaration) Liability suspended Release for consumption: Suspended liability becomes due Companies can inform consumers about level

  • f charge to enhance

awareness

Domestic territory

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Administrative Implementation: International case

3.

Inclusion of Consumption of carbon intensive materials in emission trading systems

Foreign territory

Process action Quarterly reporting to national authority: Creation of liability per ton of e.g. steel (benchmark rate times carbon times ton of steel) Liability held + Liability created

  • Liability passed with

products Passing on liability Liability held + liability received

  • Liability acquitted

(lodging of declaration) Liability suspended Release for consumption: Suspended liability becomes due Companies can inform consumers about level

  • f charge to enhance

awareness

Domestic territory

Process action Reporting to customs authorities: Acquittal of liability upon export Weight of carbon intensive product contained in product by customs declaration Creation of liability upon import

 Reporting on imports and exports embedded in customs procedure

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De-minimis approach – only selected products and firms are covered

Inclusion of Consumption of carbon intensive materials in emission trading systems

Domestically:

  • Mandatory for all producers of cement and steel sector (plus close

substitutes)

  • Producers of subsequent products can self-select to participate so that

liability passed on them is suspended: no need to pay charge up-front and

  • ption to waive charge for exports.

Internationally:

  • Trade categories defined in which consumption charge is relevant (e.g.

price increase relevant for choices of intermediary and final consumption choices)

  • For products in these trade categories, importers need to report and incur

liability for weight of carbon intensive materials in product

3.

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International aspects

Inclusion of Consumption of carbon intensive materials in emission trading systems

3.

On good side of WTO Law

  • charge imposed on all steel, cement etc. consumed within the

territory irrespective of their origin

  • charge does not distinguish between production methods

(independent of specific carbon footprint) No discrimination against like imported products Incentive for low-carbon materials and efficient material use in all products served to domestic consumers

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EU Law aspects

Inclusion of Consumption of carbon intensive materials in emission trading systems

3.

IoC as integral part of EU ETS for the following reasons:

  • Environmental objective: Restoring incentives for mitigation options of

group 2 and 3 of EU ETS that are lost with free allocation as leakage protection.

  • Revenues used to substitute auction revenues to fund climate action.
  • Revenues collected partially used to acquire allowances at the auction

platforms for net carbon imports.

  • Technical points: charge calculated according to the benchmark used for

free allocation and charge based on recent months average carbon price.  IoC qualifies as environmental regulation and can be implemented as part of EU ETS Directive, thus public acceptance in MS and qualified majority voting in Council.

Source: Ismer and Haussner, Inclusion of Consumption into the EU ETS: The Legal Basis under European Union Law, RECIEL, forthcoming.

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Administrative costs

3.

Inclusion of Consumption of carbon intensive materials in emission trading systems

Low operating costs of typical consumption charges like

  • Excise duties
  • VAT

Reasons to anticipate that the inclusion of consumption will have similar low operating costs:

  • Design of the scheme follows the mechanism of excise
  • Verification and compliance simplified because of fewer fraud

incentives: charge constitute limited fraction of product price and is never reimbursed (unlike VAT).

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1

Motivation

2

The mechanism

3

Technical Implementation

4

Conclusion

Inclusion of Consumption of carbon intensive materials in emission trading systems

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Conclusion

Inclusion of Consumption of carbon intensive materials in emission trading systems

 2050 Emissions reduction objectives can only be achieved with portfolio of mitigation options  Benchmark based allocation plus IoC activates carbon price throughout the value chain as it reinstalls incentives for mitigation options in all three groups  Consumption charges on the good side of WTO law  Low administrative costs as design similar to other consumption charges (excise and vat)

4.

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Thank you for your attention!

DIW Berlin — Deutsches Institut für Wirtschaftsforschung e.V. Mohrenstraße 58, 10117 Berlin www.diw.de

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Monetary effects

Inclusion of Consumption of carbon intensive materials in emission trading systems

Effect on consumers

  • Incremental costs of consumption charge represents only small cost increase to

consumers in final product price

 IoC provides funds for financing climate action without imposing a significant burden on final consumers and without damaging European Competitiveness

4.

Relative price changes for the 9 groups

  • f manufactured goods in the CREEA

MRIO model, scope: EU28, reference year: 2007. Source: Pauliluk et al.

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Imports

Source: Pauliuk et al, 2015.

Imports into and exports from the EU28 in 2012, cumulative, sorted by relative liability

  • r price change (EUR/EUR) (plot with cutoff at 0.01EUR/EUR)

Exports

De-minimis approach – Imports and Exports to be covered

Inclusion of Consumption of carbon intensive materials in emission trading systems

  • 4.

Mirror pictures