The Waste Sector Under the Effort Sharing Decision

Similar documents
Impact of municipal waste management on climate change. Paweł Głuszyński

The 2030 Effort Sharing Regulation

COMMISSION STAFF WORKING DOCUMENT. The early warning report for Malta. Accompanying the document

COMMISSION STAFF WORKING DOCUMENT EXECUTIVE SUMMARY OF THE IMPACT ASSESSMENT. Accompanying the document

Why is UNFCCC COP21 so significant?

14060/1/14 REV 1 AM/am 1 DG E 1A

EUROCITIES response to the circular economy package. February 2016

ISWA White Paper on Waste and Climate Change

REPORT FROM THE COMMISSION TO THE EUROPEAN PARLIAMENT, THE COUNCIL, THE EUROPEAN ECONOMIC AND SOCIAL COMMITTEE AND THE COMMITTEE OF THE REGIONS

25th commission meeting, 16 October 2014 WORKING DOCUMENT. Commission for the Environment, Climate Change and Energy

Circular Economy Closing the loop An EU Action Plan for the Circular Economy

Council conclusions on the EU action plan for the circular economy

WASTE-TO-ENERGY IN EUROPE WHERE ARE WE AND WHERE ARE WE GOING?

MSW management in Europe

Results from the Swedish Environmental Protection Agency analysis of the ESR-proposal

Waste Management and Recycling:

An Imperial College London report commissioned by Veolia. Authors: Zafeiridou M., Kirkman R., Kyle C., McNeil S. and Voulvoulis N.

A8-0031/ AMENDMENTS by the Committee on the Environment, Public Health and Food Safety

WP 3.3: Policy Roadmap for large-scale biogas implementation in Latvia

BENELUX TALANOA DECLARATION

european suppliers OF Waste-tO-eNergy technology everything you always WaNteD to KNOW about Waste-tO-eNergy

Proposal for a REGULATION OF THE EUROPEAN PARLIAMENT AND OF THE COUNCIL

RECYCLING vs. REUSE ENVIRONMENTAL BENEFITS OF RE-CYCLING VERSUS RE-USE CORRUGATED BOARD PACKAGING AS ILLUSTRATION

The transition to a circular economy therefore requires fundamental changes across the entire economy based on the following interdependent pillars:

Municipal waste management in Slovenia

Climate Action Network-International submission to the AWG-LCA 1. mitigation actions. 21 February 2011

Planning for success in the future zero carbon economy: How to build strong National Energy and Climate Plans.

Specific requests for a policy transition to promote investment in low-carbon technologies

POSITION June Circular Economy Proposal for a Directive amending Directive 2008/98/EC on Waste. Parliamentary Draft Report of Simona Bonafè, MEP

DGE 1 EUROPEAN UNION. Brussels, 27 April 2018 (OR. en) 2015/0274 (COD) PE-CONS 10/18 ENV 127 CODEC 251

The Role of Waste-to-Energy in Sustainable Waste Management

Waste management options and climate change - the case of biowaste

APPLY COVER HERE FROM ILLUSTRATOR FILE

Input from GasNaturally to the Talanoa Dialogue

Input from GasNaturally to the Talanoa Dialogue

DRAFT OPINION. EN United in diversity EN. European Parliament 2015/0272(COD) of the Committee on Industry, Research and Energy

Briefing January 2019 Resources and Waste Strategy for England: Government Policy paper

Poland s Third National Communication under the United Nations Framework Convention on Climate Change, 2001

EBA position on biomass sustainability under the Renewable Energy Directive

ROADMAP. A. Context and problem definition

State of the Nation Report

Joint position paper

COMMUNICATION FROM THE COMMISSION TO THE EUROPEAN PARLIAMENT, THE COUNCIL, THE EUROPEAN ECONOMIC AND SOCIAL COMMITTEE AND THE COMMITTEE OF THE REGIONS

Building blocks for a robust Sustainable Development Mechanism. Carbon Market Watch Policy Brief May 2017

REPORT FROM THE COMMISSION TO THE EUROPEAN PARLIAMENT, THE COUNCIL, THE EUROPEAN ECONOMIC AND SOCIAL COMMITTEE AND THE COMMITTEE OF THE REGIONS

Annual WFAS summary data tables are also available to download in Excel format on SEPA's web site.

Keeping global warming to 1.5 C Challenges and opportunities for the UK

COMMISSION STAFF WORKING DOCUMENT EXECUTIVE SUMMARY OF THE IMPACT ASSESSMENT. Accompanying the documents

THE STORY OF CONTARINA

The new Directive and EU policy and strategies for the management of biowaste

Advanced Waste Management and climate protection - Experiences in Germany Workshop Waste and Climate Change New Delhi

IRELAND S CEMENT INDUSTRY AND ALTERNATIVE FUELS

6515/18 AM/am 1 DG E 1A

Zero Waste Circular Economy A Systemic Game-Changer to Climate Change

Blue Manifesto for Europe s seas. Priorities and urgent actions for the European Commission

Report for the European Commission DG Environment under Framework Contract N o ENV.C.2/FRA/2011/0020

REPORT FROM THE COMMISSION TO THE EUROPEAN PARLIAMENT, THE COUNCIL, THE EUROPEAN ECONOMIC AND SOCIAL COMMITTEE AND THE COMMITTEE OF THE REGIONS

Cascading Use: A Systematic Approach to Biomass beyond the Energy Sector

The Polish National Waste Management Plan 2014

CONTAINER GLASS PRODUCTION UNDER THE EU-ETS REFORM POST-2020:

Paris Summit on climate change: Municipalities and regions as catalysts for success

Strategies of Circular Economy in the Netherlands

Waste-to-Energy: Energising your waste

The Circular Economy a Powerful Force for Climate Mitigation. Transformative innovation for prosperous and low-carbon industry

Valorisation of organic household waste & greenery cuttings

RECYCLING IS NOT ENOUGH

The purpose of this study

COMPROMISE AMENDMENTS 1-14

Waste opportunties: Past and Future Climate Benefits from Better Municipal Waste Management in Europe

Manual of European Environmental Policy

Executive Brief for NAMA Consultation Workshop

Report on Projections of GHG Emissions up to 2020

Eurometaux Position on the review of the European waste management legislation

DRAFT OPINION. EN United in diversity EN. European Parliament 2016/0230(COD) of the Committee on Development

Greenhouse Gas Emissions from Municipal Waste Management : The Situation in Greece

Current developments in European Waste-to-Energy

DRAFT REPORT. EN United in diversity EN. European Parliament 2017/2009(INI) on EU action for sustainability (2017/2009(INI))

Published by: UNDP Kosovo This study was initiated by UNDP Kosovo and UNDP Bratislava Regional Center.

12901/18 JV/bsl 1 TREE.1.B

Biomethane development and the decarbonisation strategy in Italy

URBAN EMPATHY Working Package 3. RESULT INFORMATION FILE Phase 1. Description of the result to be capitalized in URBAN EMPATHY

Key data supporting climate policy in Europe

Waste management in Austria Waste legislation in Austria. Seite

Second Opinion on KommuneKredit s Green Bond Framework

12747/12 ADD 3 KZV/mp 1 DG E 1B

COMMISSION STAFF WORKING DOCUMENT EXECUTIVE SUMMARY OF THE IMPACT ASSESSMENT ON INDIRECT LAND-USE CHANGE RELATED TO BIOFUELS AND BIOLIQUIDS

EU legislation on biogas sustainability. Andreas Pilzecker European Commission, DG Energy - Renewable Energy and CCS

ACT Alliance COP22 Position Paper

Green 2050 Vision for Gloucestershire - Stroud District Green Party

, Municipal waste management in Slovakia

The Green Vision. Scenario for Europe. How to achieve net-zero CO 2. emissions by 2050

Response of Climate Alliance to the European Commission stock taking document Towards a new energy strategy for Europe

REPORT FROM THE COMMISSION TO THE EUROPEAN PARLIAMENT AND THE COUNCIL. The state of the European carbon market in (Text with EEA relevance)

EU outlook on biogas and biomethane: market and legislative developments

Questions and Answers on the Commission's proposal for effort sharing

Implementation of EU waste legislation. Karolina Fras European Commission DG Environment

THE COVENANT OF MAYORS FOR CLIMATE AND ENERGY

zero waste principles

FACILITATIVE SHARING OF VIEWS MALAYSIA 15 MAY 2017

Transcription:

The Waste Sector Under the Effort Sharing Decision Zero Waste Europe Policy Briefing - May 2016 Executive Summary Waste is generally considered to be a sector with a small greenhouse gas (GHG) emission contribution to climate change, following the understanding that the emissions from waste are only those related to waste disposal in landfills and incinerators. However, this assumption is misguided and incorrect, as the waste sector involves a much larger range of activities and a much larger portion of GHG emissions that as such unfortunately go unaccounted. In fact, the waste sector contribution to GHG emission reduction has enormous potential when support is given to the higher tiers of the Waste Hierarchy -including reduction, reuse, recycling, composting, biogas generation, sustainable consumption and production, and it can be a game-changer to the development of a low-carbon economy. The waste sector is a large and untapped sector with a significant potential for cost effective mitigation. Looking at the potential contribution of the waste sector to a low-carbon economy, recent research 1 calculated the climate contribution from the optimal implementation of the Circular Economy Package waste targets (2014 version). Assuming the implementation of a 70% recycling, 30% of food waste reduction, and an 80% recycling of packaging waste, the EU would save 190 million/tones CO 2 -eq/year, which would be the equivalent to the total annual emissions of the Netherlands. The Effort Sharing Decision 2030 framework has the potential to further reduce emissions in the waste sector, and this is an opportunity that should not be missed. In order to deliver effective GHG emission reductions, the new 2030 framework should follow some key recommendations both for the overall framework and in particular for the waste sector: 1 Eunomia (2015), The Potential Contribution of the Waste Sector to a Low-Carbon-Economy, (https:// www.zerowasteeurope.eu/downloads/the-potential-contribution-of-waste-management-to-a-low-carbon-econ omy/)

1. Be aligned with the Circular Economy Package and the Waste Hierarchy, ensure support for the most environmental and cost-effective options for reducing emissions in the waste sector. This will lead to significant GHG emission reductions and reinforce the synergies between European climate, energy and waste legislation. 2. Increase ambition in line with the Paris Agreement, with a long-term goal to limit temperature increase to well below 2 C, and pursue efforts for limiting it to 1.5 C. This will require the development of a solid set of guidelines and robust governance to ensure the effective implementation of sectoral policies. 3. Avoid loopholes and apply the correct carbon accounting of biogenic emissions from biowaste or biomass. The reformed ESD should contribute to correct carbon accounting of bioenergy emissions and secure strict compliance with bioenergy sustainability criteria in order to guarantee real emissions savings. 4. Avoid the use of surplus allowances from the EU Emission Trading System (ETS) to increase the appropriate incentives for the development of a low-carbon economy where real emissions reductions are guaranteed. 5. Support Member States ability to meet their climate targets and provide guidance for governance and compliance, including annual reduction targets and effective corrective actions to avoid non-compliance, as well as transparency mechanisms to allow effective monitoring of Member States action. Why is this important? Under the Effort Sharing Decision (ESD), EU Member States are committed to reducing GHG emissions in sectors outside the EU ETS including waste, transport, buildings and agriculture. These sectors represent almost 60% of the greenhouse gas emissions in the EU. The Effort Sharing Decision could be an important tool to incentivise Member States to develop effective climate mitigation actions in these sectors. However, current 2020 targets to decrease emissions by 10% have been proven to lack ambition these have been met without major transformations, and the use of carbon allowances and accounting loopholes has undermined the effectiveness of this climate policy. 2 So far, the ESD has posed the risk of turning into another missed opportunity to transform the EU into a long-lasting low-carbon economy. Under the new ESD, Member States will be obliged to reduce their GHG emissions by 30%, but these higher targets will not necessarily deliver real mitigation action at the scale of transformation needed unless there is strong coordination and alignment with other sectoral policies. Failing that, these sectors will likely remain largely unimproved, and a number of loopholes both in GHG emission accounting and governance will threaten the implementation of the ESD. The commitment to enact the Paris Agreeement and pursue a maximum increase of 1.5ºC is dependent upon the EU making this effort to meet the target. With the appropriate support, climate solutions in the EU waste and resource-efficiency sectors are a low-hanging fruit, one that the EU needs to take advantage of if it is to honour its climate commitments. 2 Öko-Institute, (2015) Enhanced flexibilities for the EU s 2030 Effort Sharing Decision. (http://www.oeko.de/ oekodoc/2373/2015-537-en.pdf)

The climate mitigation potential in the waste sector In 2011, the European Commission published its Roadmap to a low-carbon economy, setting targets, which included reductions in domestic emissions of 80% by 2050 compared to 1990. 3 Along with significant reductions in the emissions generated by the power, industrial and transport sectors, the Roadmap indicated that increased resource efficiency through waste recycling, better waste management and behavioural change could also play an important role in achieving this objective. Amongst other studies, the European Commission s impact assessment noted that high recycling scenarios could lead to an additional 62 million tonnes CO 2 equ. saving by 2030 over and above Diamond Geezer - CC BY-NC-ND 2.0 Several Member States have highlighted the contribution made by improved waste management to reduced greenhouse gas emissions those that were expected to be delivered by existing legislation (which appear to be of the order 50 million tonnes CO 2 eq.). 4 Figure 1: Indicative Climate Change Key Impacts of Key Waste Management Activities 3 European Commission (2011), A Roadmap for moving to a competitive low carbon economy in 2050 4 European Commission (2014), Impact Assessment Accompanying the Document, Proposal for a Directive of

Generally, therefore, studies indicate that in Europe, even though much progress has already been made in respect of reducing climate change emissions from waste, further savings of the order 100-200 million tonnes CO 2 eq. could be made simply through conventional waste management approaches: conventional waste prevention measures could deliver more substantial reductions, whilst measures designed to achieve a circular economy could further enhance emissions reduction through reuse, repair and remanufacturing. To illustrate the point, Figure 1 5 shows the impacts associated with recycling and waste prevention, in each case, showing the impact relating to one tonne of material, excluding the biogenic CO 2 emissions, over a 100 year time period the period conventionally used in life cycle assessments. It confirms, for example, that the benefit associated with using one tonne less plastic packaging can be a saving in the order of 3 tonnes CO 2 equivalent, whilst recycling the same type of material might result in a benefit of around 500 kg CO 2 equivalent per tonne of plastic. Using one tonne less plastic packaging can be a saving in the order of 3 tonnes CO 2 equivalent, whilst recycling the same type of material might result in a benefit of around 500 kg CO 2 equivalent per tonne of plastic. and preventing food waste. The figure also shows that the activity of treatment or disposal of residual waste generally increases climate change emissions, whilst recycling and waste prevention are activities which contribute to emissions reduction. Furthermore, the difference in the impacts between landfill and incineration is almost trivial when compared with the benefits which might be achieved from recycling, or preventing the use of, dry materials, Looking forward, and reflecting on the above results, it is clear that a climate friendly strategy in the waste sector will be one in which materials are continually cycling through the economy, and where the leakage of materials into residual waste treatments is minimised. the European Parliament and of the Council Amending Directives 2008/98/EC on waste, 94/62/EC on packaging and packaging waste, 1999/31/EC on landfill of waste, 2000/53/EC on end-of-life vehicles, 2006/66/ EC on batteries adn accumulators and waste batteries and accumulators and 2012/19/EU on waste electrical and electronic equipment, Brussels, 2.7.2014, SWD(2014) 207 final. 5 The data in Figure 1 is taken from life cycle analyses (for the production and dry recycling impacts) and from Eunomia s in-house treatment models.

Key Recommendations for the Effort Sharing Decision 1. Be aligned with the Waste Hierarchy, embedded in the proposed Circular Economy Package. 6 Changing waste management practices can have a significant impact on climate change mitigation, primarily from waste prevention and recycling, particularly of dry materials. In comparison, residual waste treatment such as landfills and incinerators actually contribute towards climate change. (Fig. 1). The Waste Hierarchy is an invaluable tool for resource and waste policies worldwide. 7 In the EU, the Waste Hierarchy guides the Waste Framework Directive which is currently under discussion within the Circular Economy Package. According to these policies and latest scientific research on this topic, changing waste management practices can generate significant climate change benefits, mostly from waste prevention and recycling, particularly of dry materials (Fig 1). In comparison, residual waste treatment such as landfills and incinerators actually contribute to climate change. Additionally the IPCC s latest report AR5, refers to waste prevention, reuse and recycling activities in the waste sector that can deliver the largest climate benefits. 8 Moreover to illustrate the potential contribution of the waste sector to a low-carbon economy, recent research calculated the climate contribution from the optimal implementation of the Circular Economy Package waste targets (2014 version). Assuming the implementation of a 70% recycling, 30% of food waste reduction, and an 80% recycling of packaging waste, the EU would save 190 million/tones CO 2 -eq/year, which would be the equivalent to the total annual emissions of the Netherlands. In light of the above, the Effort Sharing Decision should set mitigation targets for the waste sector which are consistent with the Circular Economy Package whilst making sure that support is given to follow the higher tiers in the Waste Hierarchy. 6 Waste Hierarchy https://www.zerowasteeurope.eu/wp-content/uploads/2016/04/foodwastehierarchy-940x726.jpg 7 Hoomweg, D. & Bhada-Tata, P. What a Waste: A Global Review of Solid Waste Management (World Bank, 2012). 8 IPCC AR5. Working group III. Chapter 11.

While further investigation is needed to determine how best to account for and report emission savings from waste related activities into national inventories, the ESD should not ignore the realities of the sector and include a set of recommendations that would enhance the policy coherence amongst climate, energy and waste. Particularly, the ESD should: 1. Make explicit reference to the Waste Hierarchy and scientific research which gives priority to waste reduction, reuse, recycling, composting and sustainable consumption and production as key mitigation strategies in the waste sector. 2. Recognise the particular policies governing the waste sector, i.e. the Circular Economy Package and propose climate mitigation targets for the waste sector in alignment with the waste-related targets, i.e. 65% recycling, 30% recycling packaging waste, 30% reduction of food waste. 3. Introduce accounting mechanisms to quantify the emissions savings from waste recycling and waste prevention activities at national level, even if only as information notes in the national inventories. This simple action would allow a much more accurate representation of climate mitigation achieved through recycling and waste prevention activities and therefore would provide an incentive to increase the virtuous cycle. 2. Increase ambition in line with the Paris Agreement. ESD targets for the waste sector should not only consider the mandate from the Circular Economy Package; it should also follow the long-term goal to limit global Unreported emissions from incineration of waste act as a loophole in EU GHG emission accounting warming to well below 2 C, and pursue efforts for keeping it at a 1.5 C increase. The Paris Agreement requires the transition across sectors to a low-carbon economy, ensuring actual emission reductions and creative solutions for a long-lasting, inclusive change. Zero waste solutions, alongside climate action in other sectors, will contribute to achieving the global target of a maximum of 1.5 degrees global warming, embracing the principles of conservation of materials, the reduction of toxics, equitable distribution, and access to resources. Zero waste solutions including waste reduction, redesign, composting, biogas, producer responsibility, consumption changes, and recycling could be implemented today, using existing innovations, and with immediate results.

The reformed ESD should avoid the loophole of unreported emissions and contribute to correct carbon accounting of bioenergy emissions. The Network of Zero Waste Municipalities 9 is showing ground-breaking results: several cities in Italy have successfully implemented 80% of separate collection for example, and others follow closely. 10 In contrast with the primitive idea of burning waste, recycling and composting create jobs, save money, and protect the environment and public health. These efforts go handin-hand with clean production, producer responsibility, and waste minimisation programs for dangerous and hard-to-recycle materials. Together, these practical solutions provide some of the best-decentralised urban actions for reducing climate pollution, conserving energy and natural resources and present enormous opportunities for developing local living economies. 3. Avoid loopholes and apply correct carbon accounting of biogenic emissions. There are methodological issues with emission accounting that a reformed ESD should consider and correct as necessary, particularly concerning the accounting of biogenic emissions. So far, the IPCC guidance on how to develop inventories has been interpreted, erroneously, so as to imply that when considering alternative approaches to managing waste, CO 2 emissions of non-fossil origin can be ignored. This issue gives rise to a misunderstanding that some technologies for waste disposal or residual waste energy extraction, can reduce GHG emissions. Within UNFCCC inventories, the combination of the various assumptions made under the industry, energy and waste sections makes the issue of biogenic carbon problematic, and may be leading to significant underestimations of the contribution made by biogenic CO 2 to global climate change. The implications for the emissions accounting methodologies in the waste sector are significant when the only reported emissions are those from landfills and incineration. First, the emission of biogenic waste incineration varies with the amount of organic waste (for example, food scraps and paper) compared with the amount of fossil fuel products (e.g. plastic) contained in the waste. But if we take the conventional incinerator estimates as to the presence of biomass in municipal solid waste, it is considered that an average of 50% of CO 2 emissions from burning waste are biogenic, so only half of the actual CO 2 emitted are reported. Studies show a wide range of biogenic emissions of waste from 43% to 61%. 1112 A reformed ESD should correct these accounting issues and apply accurate methodologies. 9 http://www.zerowasteeurope.eu/zerowastecities.eu/ 10 http://www.zerowasteeurope.eu/zw-library/case-studies/ 11 Mohn, et al., Fossil and Biogenic CO2 from Waste Incineration Based on a Yearlong Radiocarbon Study, Waste Management, Volume 32, Issue 8, August 2012, Pages 1516-1520. 12 A. Koehler et al., Probabilistic and Technology - Specific Modeling of Emissions from Municipal Solid - Waste Incineration, Environ. Sci. Technol. 2011, 45 (8), pp 3487-3495

4. Avoid the use of surplus allowances from the EU ETS Given the mandate of the Paris Agreement and the level of ambition that is necessary to meet the targets, using the surplus of EU ETS allowances will not be an effective way to reduce emissions, but just another false solution. Several studies have pointed out to the enormous amount of allowances currently present in the EU carbon market. Enabling the use of these allowances into the ESD compliance will jeopardise the effectiveness and success of this policy, as pointed out by recent research. 13 Furthermore, it s worth noting that the cement industry, which is actively promoting the incineration of waste across the EU with severe environmental, social and economical consequences, 14 has been recently reported as the Final Carbon Fatcat. 15 In this sense, not only the cement industry has been exposed for taking enormous advantage of its surplus of allowances, but its in fact undermining the potential for a low-carbon and circular economy with major pollution consequences. The case of the cement industry illustrates the deep structural flaws in the EU ETS and the need to further regulate the most carbon intensive sectors in the EU. Therefore, while the EU ETS is under reform, the ESD will not benefit from carrying over some of the EU ETS dysfunctions, and it should rather concentrate in providing appropriate support for real transformation to a low-carbon economy, that is, achieving real emission reductions. 5. Support Member States ability to meet their climate targets from a sectoralbased approach. The success of the ESD 2030 will be determined by its ability to offer tailored guidance for climate mitigation in each sector, seeking alignment and policy coherence with other EU sectoral policies. As expressed above, there is wide expertise in the waste sector on what are the best mitigation options and strategies, so it offers a particularly low-hanging fruit when it comes to climate solutions. Moreover, an effective ESD will provide guidance for governance and compliance to Member States, giving priority to transparency and accurate monitoring. To that purpose, it will be instrumental to establish annual reduction targets and effective corrective actions to avoid non-compliance, as well as public reporting mechanisms that are publicly accessible. 13 Sandbag, The Effort Sharing Dinosaur, May 2016 14 Vilella, M., Arribas, C., Cement, Waste and Carbon Markets. Problems related to waste incineration in cement kilns under the EU ETS. February 2013. 15 Sandbag, The Final Carbon Fatcat, February 2016. https://sandbag.org.uk/reports/final-carbon-fatcat/ Zero Waste Europe gratefully acknowledges financial assistance from LIFE financial instrument of the European Community. The sole responsibility for the content of this publication lies with Zero Waste Europe. It does not necessarily reflect the opinion of the funder mentioned above. The funder cannot be held responsible for any use that may be made of the information contained therein.