Enhancing Community Resilience as Wildfire Risk Increases

SUMMARY

As climate change increases the risk of wildfires, individuals, communities, and governments will need to put more effort into protecting homes at the wildland-urban interface, where communities border on wilderness areas. Canada’s FireSmart program is a well-recognized and effective tool to support informed local action and help build capacity and knowledge. Additional regulatory and financial tools are, however, also needed to reduce costs from property damage.

CLIMATE CHANGE INCREASES THE RISK OF WILDFIRE FOR COMMUNITIES

As climate change leads to increased temperatures and drier conditions, wildfires are likely to become more frequent, grow more intense, and last longer across many regions in Canada. Studies show that the number of dry, windy days that let fires start and spread could increase by as much as 50% in western Canada and 200% in eastern Canada (Climate Atlas, 2020). In fact, wildfire activity has already increased, with the average area burned in recent years double the size of what it was in the early 1970s (NRCan, 2016).

Wildfires can be devastating and costly for communities and individuals. Researchers estimate the 2016 Fort McMurray fire cost almost $9 billion through physical, financial, health, mental, and environmental impacts (Snowdon, 2017). The fire destroyed more than 2,400 structures and displaced 85,000 people in the largest evacuation in Canadian history (Westhaver, 2017). One of the most compelling examples of the profound societal impact of the Fort McMurray fire was the staggering rise in mental health concerns such as depression and suicidal thoughts among grade 7-12 students eighteen months afterward (Brown et al. 2019).

Wildfire smoke can also affect the health of people far from the fire through reduced lung function, bronchitis, exacerbation of asthma, and increased risk of death. Air pollution from fires is a particular risk to pregnant women, children, the elderly, and those with pre-existing cardiovascular or respiratory conditions (BCCDC, 2020). Prolonged exposure to smoke from wildfires, as people in British Columbia and California experienced in 2018, increases the risk of immediate and future health problems. In addition, people living in wildfire-prone areas may experience exposure to smoke year after year.

An increase in the frequency and intensity of fires will mean that we see more of these large-scale traumatic events. As Figure 1 illustrates, Canada has an estimated 32.3 million hectares of wildland-urban interface, with 60% of all cities, towns, settlements, and remote communities facing interface fire risk (Canada Wildfire, 2018).

Figure 1: Map of the Wildland-Urban Interface in Canada
Source: Canada Wildfire, 2018

HOW CAN COMMUNITIES REDUCE THEIR RISK?

After the Fort McMurray fire, people wondered why some homes survived and others did not. There were cases where the fire destroyed all homes in a neighbourhood except one. According to detailed assessments, most home ignitions were caused by embers from the forest fire, rather than direct contact with flames of the burning forest (Westhaver, 2017). So, the homes that survived must have either had features that protected them from embers, or the absence of common ignition hazards like leaves in gutters or a wooden deck.

Comparing the characteristics of homes after the fire, experts found that surviving homes had low to moderate hazard level across 20 factors for ignition potential. Destroyed homes predominantly had high to extreme hazard level ratings. The review did not find any one critical hazard factor. Rather, a single weakness could result in a home’s destruction (Westhaver, 2017). For instance, the ignition hazard could be a woodpile or shrubs next to the house, gutters with dried leaves, long grass, wood chips in the garden, wood siding, wood decks, or a roof with low fire resistance.

ALBERTA’S FIRESMART PROGRAM

One of the recommendations of the review of the Fort McMurray fire was to increase emphasis on reducing home vulnerability, through programs such as FireSmart. FireSmart, created by the Alberta-based multidisciplinary non-profit association Partners in Protection (PiP), helps communities and individuals take initiative to reduce their wildfire risk. It aims to build capacity and knowledge for people living in areas at risk of wildfire. Expanding from its roots in Alberta, FireSmart is now adopted in other provinces and at the national level (FireSmart Canada, 2018a). It receives funding from federal, provincial, and territorial governments, as well as insurance companies (ICLR, 2019).

FireSmart recommends removing ignition hazards, including wooden decks and siding, within 10 metres of the home (Figure 2). Over the longer term, homeowners that have enough financial resources can invest in more costly solutions such as more protective roofing materials (FireSmart Canada, 2019a; 2018a; 2018b). For more detail, see table in this case study.

Figure 2: FireSmart Home Ignition Zone
Source: FireSmart (2019b)

To help homeowners make decisions to reduce fire risk, FireSmart uses trained firefighters to assess homes directly, pointing out simple preventative measures as well as longer-term investment options. They then return after a couple of years to assess progress. FireSmart Alberta has also developed a mobile app that allows homeowners to conduct self-assessment and identify key vulnerabilities on their own, with access to information resources and expert networks.

Government of Alberta via Flickr (CC-by-NC-ND-2.0)

For example, some types of roofs are more fire resistant than others. Class A materials, such as asphalt shingles, fibreglass, clay or concrete tiles, and metal roofing (with the old roof removed) are the most fire resistant. Class C materials, such as cedar shakes, have a low fire resistance (FireSmart Lesser Slave Region, 2020). Clear information can make it easier for homeowners to demand fire resistant roofing materials and techniques.

The FireSmart program also encourages entire communities to adopt a plan, track progress, and make investments in risk reduction. As more properties within a community adopt FireSmart practices, the heat and speed of fire can be reduced for everyone (FireSmart, 2019b). The town of Canmore, Alberta, won FireSmart’s Community Protection Achievement award in 2019. Its Wildfire Mitigation Strategy outlines FireSmart activities for the town and includes an updated hazard assessment, wildland fuel type and wildfire behaviour potential maps, and vegetation management options. It also makes recommendations for each of the seven FireSmart disciplines: vegetation management; development; public education; legislation; inter-agency cooperation; cross-training; and emergency planning (Canmore, 2020).

WHAT ELSE CAN BE DONE?

While FireSmart programs are a useful resource for homeowners, they place the burden of protection on individuals and communities—and not everyone is in a position to act. Homeowners may not be able to afford a new roof or siding. Lower-income, remote, and Indigenous communities may also have limited resources and competing priorities.

Strengthen Building Codes and Regulations

In 2016, a federal-provincial review found that most communities are not actively participating in FireSmart (CCFM, 2016). Experts have questioned whether there should be a greater role for provincial and federal governments in promoting fire resilience, given the broader public benefit of individual risk reduction efforts (Westhaver, 2017; Tymstra et al. 2019). Quebec is the only province that has regulatory standards that guide local governments in reducing wildfire risk (Tymstra et al. 2019). In most provinces and municipalities, building codes do not require builders to use fire resistant materials, which leaves homeowners shouldering the cost of renovation when seeking to reduce their risk. While new national codes are being developed to reflect climate change risk, it could be years before they trickle down to provincial codes (CP, 2020; ICLR, 2019). The National Fire Protection Association had proposed stricter building codes for wildland interface communities in 2011, but the idea was rejected at the time due to concerns about the burden of enforcement (CP, 2012). In the absence of building codes, FireSmart Canada, the Canadian Homebuilders Association, and the Intact Centre on Climate Adaptation are working to develop a FireSmart checklist for developers and homebuilders building in wildland-urban interface areas (Moudrak, 2020).

Undertake Meaningful Consultation

Research by Walker (2020) also highlights the importance of meaningful consultation when FireSmart programs are implemented, particularly when wildfire risk extends across multiple jurisdictions in a small geographical area. When the FireSmart program was implemented in the La Ronge region of Saskatchewan, for example, some Indigenous and non-Indigenous community members voiced concerns over how the local vegetation was being cut back in areas used for medicinal plant gathering and land-based education programs.

Limit Urban Sprawl

Many cities also continue to sprawl further into the wild, seeking inexpensive land for residential developments, increasing their risk and the overall cost of wildfires (McMahon, 2018). Few governments have been willing to limit development, and wildfire hazard maps that could help identify areas unsuitable for development are not yet commonly available (ICLR, 2019).

Invest in Risk Reduction

The response of governments to a changing fire regime in Canada has thus far been largely reactive, with financing focused on wildfire response and recovery. However, it is increasingly clear that investment in risk reduction is significantly more cost effective (IAWF, 2020). Further, the most effective wildfire risk management strategies involve a combination of home ignition reduction (through programs such as FireSmart) and forest management practices that reduce the likelihood and severity of wildfires (Calkin et al., 2014). In preparation for a fire-prone future, proactive, largescale investment in these types of integrated strategies by federal, provincial, and local governments could dramatically reduce the impacts of wildfire on Canadians.

FIRESMART ADVICE FOR HOMEOWNERS IN WILDFIRE-PRONE AREAS

For more information visit https://firesmartcanada.ca/homeowners/

ACKNOWLEDGEMENTS

This case study was prepared by Rachel Samson of the Canadian Climate Institute, with staff contributions from Jonathan Arnold, Ryan Ness and Dylan Clark.

The Institute wishes to acknowledge the contributions of:

Blair Feltmate
Chair, Expert Panel on Adaptation, Canadian Climate Institute and Head, Intact Centre on Climate Adaptation, University of Waterloo

Natalia Moudrak
Director of Climate Resilience Intact Centre on Climate Adaptation, University of Waterloo

Laura Stewart
FireSmart Specialist, Alberta Agriculture and Forestry

Maureen G. Reed, PhD
Distinguished Professor and Assistant Director, Academic UNESCO Co-Chair in Biocultural Diversity, Sustainability, Reconciliation and Renewal School of Environment and Sustainability

Heidi Walker
PhD Candidate, University of Saskatchewan School of Environment and Sustainability

REFERENCES

BCCDC. 2020. “Wildfire Smoke and Your Health.” British Columbia Centre for Disease Control. http://www.bccdc.ca/ resource-gallery/Documents/Guidelines%20and%20Forms/Guidelines%20and%20Manuals/Health-Environment/BCCDC_WildFire_FactSheet_HowToPrepare.pdf

Brown, M.R.G., Agyapong, V., Greenshaw, A.J. et al. 2019. “After the Fort McMurray wildfire there are significant increases in mental health symptoms in grade 7–12 students compared to controls.” BMC Psychiatry 19, 18. https://doi. org/10.1186/s12888-018-2007-1

Canmore. 2020. “FireSmart.” Town of Canmore. https://canmore.ca/municipal-services/emergency-services/emergency-management/firesmart

Calkin et al. 2014. “How risk management can prevent future wildfire disasters in the wildland-urban interface.” Proceedings of the National Academy of Sciences. Jan 2014, 111 (2) 746-751; DOI: https://doi.org/10.1073/pnas.1315088111

Canada Wildfire. 2018. “Mapping Canadian wildland fire interface areas.” https://www.canadawildfire.org/mapping-wui

CCFM. 2016. “Canadian Wildland Fire Strategy: A 10-year Review and Renewed Call to Action.” Canadian Council of Forest Ministers. https://cfs.nrcan.gc.ca/publications/download-pdf/37108

Climate Atlas of Canada. 2020. “Forest Fires and Climate Change.” https://climateatlas.ca/forest-fires-and-climate-change

CP. 2020. ‘‘A new focus for us’: Canada’s building code being modernized to address climate change.” CBC News. 1 January 2020. https://www.cbc.ca/news/technology/climate-change-canada-building-codes-1.5412390

CP. 2012. “Building-code changes rejected for wildfire-prone areas.” CBC News. 3 December 2012. https://www.cbc.ca/ news/canada/edmonton/building-code-changes-rejected-for-wildfire-prone-areas-1.1177036

FireSmart Canada. 2020. “FireSmart Begins at Home Manual.”https://firesmartcanada.ca/wp-content/uploads/2019/10/ FS_Generic-HomeOwnersManual_Booklet-November-2018-Web.pdf

FireSmart Canada. 2019a. “FireSmart Community Recognition Program.” https://www.firesmartcanada.ca/ firesmart-communities/firesmart-canada-community-recognition-program/

FireSmart Canada. 2019b. “Ignition Zone.” https://www.firesmartcanada.ca/firesmart-communities/firesmart-canada-community-recognition-program/ignition-zone/

FireSmart Canada. 2018a. “About FireSmart.” https://www.firesmartcanada.ca/about-firesmart/

FireSmart Canada. 2018b. “FireSmart Home Assessment.” https://www.firesmartcanada.ca/mdocs-posts/ firesmart-home-assessment/

FireSmart Lesser Slave Region. 2020. “FireSmart for Homeowners.” https://livefiresmart.ca/homeowners/

IAWF. 2020. “Reduce Wildfire Risks or Pay More for Fire Disasters.” International Association for Wildland Fire. https:// www.iawfonline.org/article/reduce-wildfire-risks-or-pay-more-for-fire-disasters/

ICLR. 2019. “Fort McMurray Wildfire: Learning from Canada’s costliest disaster.” Institute for Catastrophic Loss Reduction. https://www.iclr.org/wp-content/uploads/2019/10/Fort-McMurray-Wildfires_Canadian-Copright.FINAL-2_One-Page.pdf

McMahon, Tamsin. 2018. “In wildfire-prone B.C. and California, urban sprawl and bad planning are fuelling future infernos. What can we do?” The Globe and Mail. 24 February 2018. https://www.theglobeandmail.com/world/article-in-wildfire-prone-bc-and-california-urban-sprawl-and-bad-planning/

Moudrak, Natalia. 2020. Personal Communication with Natalia Moudrak from the Intact Centre on Climate Adaptation. https://www.intactcentreclimateadaptation.ca/

NRCan. 2016. “Peatland fires and carbon emissions.” Natural Resources Canada. https://www.nrcan.gc.ca/climate-change/impacts-adaptations/climate-change-impacts-forests/forest-carbon/peatland-fires-carbon-emissions/13103

Reed, M.G. and Walker, H., with Fletcher, A. 2020. “Accounting for gender and diversity in adaptation planning and action: Speaking from Canadian experiences”. Presentation for Adaptation 2020, Feb 20, 2020. More information available from the authors.

Snowdon, Wallace. 2017. “Fort McMurray wildfire costs to reach almost $9B, new report says.” CBC News, 17 January 2017. https://www.cbc.ca/news/canada/edmonton/fort-mcmurray-wildfire-costs-to-reach-almost-9b-new-report-says-1.3939953

Stewart, Laura. 2019. Personal communication with Laura Stewart, FireSmart Provincial Representative for Alberta. June 2019.

Tymstra et al. 2019. “Wildfire Management in Canada: Review, challenges and opportunities.” Progress in Disaster Science. 5 (2020) 100045. https://doi.org/10.1016/j.pdisas.2019.100045

Walker, H. 2020 (forthcoming). “Building inclusive responses to climate hazards: Learning from experiences of wildfire in northern Saskatchewan.” (Doctoral dissertation in progress). University of Saskatchewan, Saskatoon, Canada. More information available from author.

Westhaver, Alan. 2017. “Why Some Homes Survived: Learning from the Fort McMurray wildland/urban interface fire disaster.” https://www.iclr.org/wp-content/uploads/PDFS/why-some-homes-survived-learning-from-the-fort-mcmurray-wildland-urban-interface-fire-disaster.pdf

Climate Legislation in the United Kingdom

Summary

The United Kingdom (UK)’s Climate Change Act 2008 was the first law of its kind. It makes long-term emissions reduction targets legally-binding, opening the door to citizen lawsuits if the government misses them, and introduces interim targets or “carbon budgets” to keep the UK on track. It also established an independent advisory body to provide advice to governments on meeting targets and to monitor progress. Notably, the scope of the legislation is not limited to climate change mitigation, but also introduced governance and processes related to adaptation. The Act has since been cited as a model by other jurisdictions who have introduced similar legislation. This case study reviews the six defining features of the UK’s legislation.

FEATURES OF UK LEGISLATION

1. Legislating climate accountability processes

The 2008 Act enshrined a long-term emissions reduction target of 80% below 1990 levels by 2050 as well as five-year “carbon budgets”—interim, cumulative emission-reduction milestones to put the UK on track to meet its 2050 target. In 2019, the UK passed legislation that increased its 2050 target to net-zero emissions, meaning that any UK emissions in 2050 would be balanced out by actions to offset an equivalent amount of emissions from the atmosphere.

2. Clearly defining roles and responsibilities

UK Government Duties

The Act defines the duties and powers of UK government departments and devolved administrations with regards to climate change policy. The Minister of State for Energy and Clean Growth is the minister responsible for meeting the legislated long-term targets and overseeing the UK carbon budgets. The primary UK government departments responsible for implementing climate change policies are the Department for Business, Energy, and Industrial Strategy (BEIS) and the Department for Environment and Rural Affairs (Defra). BEIS leads on policy to reduce greenhouse gas (GHG) emissions in the UK and internationally, whereas Defra leads on domestic adaptation policy.

Committee on Climate Change

To provide independent oversight, the Act established a publicly funded Committee on Climate Change (CCC), which advises the UK government and devolved administrations on how to reduce GHG emissions and prepare for and address the impacts of climate change today and in the future. The primary duties of the committee are to:

  1. Perform independent analysis;
  2. Engage with stakeholders and the public to promote informed discussions on climate change;
  3. Provide independent advice on setting and meeting carbon budgets and preparing for climate change; and
  4. Monitor progress.

The CCC is comprised of a Chairman and eight independent members and is supported by a secretariat of roughly 30 staff. The CCC members are experts in the fields of climate change, science, economics, behavioural science, and business.

Funding for the CCC is provided by the UK government as well as the devolved administrations of Scotland, Wales, and Northern Ireland.

Devolved administrations

The Act recognizes the roles of the devolved administrations in climate policy. The devolved administrations have their own emissions reduction targets and climate change policies, but also contribute to meeting the UK’s carbon budgets and implementing UK-wide policies. The CCC is available as a resource for the devolved administrations to provide advice and report on progress for their respective carbon budgets and emissions reduction targets.

Each devolved administration has taken a different approach. Under the Environment (Wales) Act 2016, the Welsh Government committed to a net Welsh emissions account of at least 80% reductions from the baseline year (1) by 2050, as well as five-year cumulative carbon budgets beginning with the period of 2016 to 2020. Through its 2009 Climate Change Act, the Parliament of Scotland elected to set annual emissions targets at least twelve years in advance, rather than follow the UK’s five-year approach. Scotland has legislated an emissions reduction target of net zero by 2045. Northern Ireland does not have its own climate change legislation and emissions reduction targets.

In the UK, long-term targets may only be amended following significant developments in climate change science or international policy or law, and budgets may only be amended following significant changes affecting the basis on which the budget was set.

3. Establishing interim emissions reduction milestones

In order to meet its long-term emissions reduction targets, the UK Climate Change Act dictates that the government must set five-year carbon budgets at the national level from 2008 to 2050 with three budgets set at a time. These budgets are cumulative, meaning that they restrict the amount of GHGs the UK can legally emit in a given period. The government is required to consider, though not follow, the advice of the CCC when setting budgets.

Source: Committee on Climate Change

Long-term targets may only be amended following significant developments in climate change science or international policy or law, and budgets may only be amended following significant changes affecting the basis on which the budget was set.

4. Producing action plans to meet milestones

The Government is required to develop and implement plans to meet carbon budgets and adapt to climate impacts. These plans must be tabled before Parliament, though the Act does not establish a set timeline for publication.

The Act does not prescribe how the Government must meet its targets or which policies must be used. However, it does lay out a set of considerations that must be taken into account by government and the CCC when making decisions or recommendations regarding action plans.

The UK model offers some flexibility in terms of meeting its carbon budgets, but with limits. When a budget is going to be missed by a small amount, the government is able to borrow one percent from the next budgetary period. Likewise, when net emissions are below the allowance, they can be carried forward to the next budgetary period. However, any amount carried forward must be recommended by the CCC and, to date, they have consistently recommended against it. The Act also allows Government to purchase international carbon credits in order to meet its carbon budgets.

The Act does not include any punitive enforcement mechanisms to prevent governments from weakening the stringency of their policy measures. However, the fact that the target is legislated opens the door to litigation by citizen groups if the government fails to meet its statutory obligations under the Act.

5. Monitoring and reporting

Legislation dictates that, each year, the Secretary of State must table in Parliament a statement on annual UK GHG emissions. The CCC is also mandated to prepare and present to Parliament progress reports, including an annual report on the implementation of carbon budgets and a bi-annual report on adaptation. The Secretary of State is required to, in turn, present to Parliament a response to the CCC’s reports within a set timeline outlined in legislation.

At the conclusion of a budget period, the Government is required to publish a final report outlining, among other things, the net UK carbon account for the period and whether emissions will be banked or borrowed for the next budget. If the carbon account exceeds the allowed amount, the report must provide a rationale as well as outline proposals and policies to address the excess emissions.

6. Beyond emissions reductions

The Act goes beyond a singular focus on reducing emissions, notably to legislate governance and processes related to climate change adaptation. For example, the Act requires the establishment of an Adaptation Sub-Committee of the CCC. Whereas the CCC advises on how to reduce GHG emissions, the Adaptation Sub-Committee provides advice on how to adapt to the risks posed by climate change. The Adaptation Sub-Committee is comprised of a Chairman and five independent members.

Legislation also introduced additional adaptation-related measures. For example, the Act mandates that the Government produce a climate change risk assessment every five years as well as a National Adaptation Programme. In addition to the National Adaptation Programme, the Act also granted the government Adaptation Reporting Power, which allows them to require certain organizations to report on how they are adapting to climate change.

Beyond adaptation, the Act also ingrains broader social and economic considerations into the process for setting budgets and developing action plans to meet them. For example, the legislation establishes a set of considerations that must be taken into account by both the CCC and the government when providing advice or making decisions relating to carbon budgets. These considerations include (but are not limited to) impacts on the economy and the competitiveness of particular sectors, differences in circumstances between England and the devolved administrations, and social circumstances, notably how specific decisions or advice could contribute to, or prevent, fuel poverty.

LESSONS FOR CANADA

Independent, expert advice is essential

The CCC has garnered a strong reputation with diverse stakeholders in the UK (including across political parties) as a credible, authoritative, and trusted voice on climate change—and its advice has been broadly accepted by governments. For example, the first five UK carbon budgets were all set at the levels recommended by the CCC, despite changes of government (as discussed below). It suggests that an independent, expert advisory body is key to ensuring consistent and credible climate policy, as well as evidence-based decision making. As a result, its example has been replicated in other countries that have implemented climate accountability legislation.

Climate legislation could establish a similar body in Canada. Like the CCC, it could have a clear mandate enshrined in law, adequate resources to conduct research and analysis, and sufficient power to hold governments to account, including authority to monitor and report on progress. Similar to the CCC, a Canadian advisory body could be available as a resource to other levels of government to provide independent, expert advice on climate policy.

Legislation can acknowledge devolution of power

While the UK has a centralized governance structure, the Act recognizes the roles of the devolved administrations of Wales, Scotland, and Northern Ireland. Although the devolved administrations have, to varying degrees, implemented their own emissions reduction targets and climate change policies, they also contribute to meeting the national UK carbon budget. A similar approach could be adopted in Canada, whereby other levels of governments have their own targets and policies, but also contribute to national goals.

Adaptation should feature in climate accountability legislation

Notably, the Act goes beyond a singular focus on reducing emissions to also recognize the importance of preparing for, and adapting to, the impacts of climate change. As described above, the Act includes a number of measures related to climate adaptation. While Canada can learn from the inclusion of adaptation planning in the UK’s legislation, it is worth noting that the Act has been criticized for its lack of focus on adaptation action.

The Act has been relatively durable, despite political changes

Implemented more than a decade ago, the UK Act has shown a strong degree of political durability. The Act was originally passed under a Labour government and was broadly endorsed by all political parties at the time. Since then, the Act has been primarily administered by Conservative governments and continues to be widely supported, even through several changes in government.

An important factor in maintaining political will and cross-party consensus is the relative flexibility that is built into the Act. While legislation sets out the long-term destination and some parameters for how to get there, it leaves decisions—like policy instrument choice—up to the government of the day. The Act also grants governments a degree of flexibility in meeting the budgets, permitting governments to carry forward over-achievements from previous periods or borrow up to 1% from subsequent ones.

However, some observers have cast doubts as to whether this political durability will last. While there was widespread political support in 2008 for the first three carbon budgets, adopting the fourth proved to me more fraught, with the UK Cabinet divided over whether to accept the CCC’s advice. The Prime Minister ultimately intervened and adopted the advice, albeit with some caveats, notably the ability to review and revise the budget again in 2014. The political commitment to the Act will likely be tested more and more as the task of meeting budgets becomes increasingly difficult.

In addition, the UK’s withdrawal from the European Union (EU) (commonly referred to as “Brexit”) raises concerns about the durability of the Act and the impact on the UK’s ability to deliver on its legislated commitments. Seeing as the Act is a domestic law, Brexit does not change the UK’s legal duties to meet its emissions reductions targets, nor its overall approach to attaining them.

While it is too soon—in early 2020—to know whether and how Brexit could affect the Act, it is not too early to identify some issues. For example, Brexit may impact the accounting of carbon budgets. For example, if the UK leaves the EU Emissions Trading Scheme, the accounting rules for how its national carbon budgets are measured could change. Second, Brexit will impact policy for meeting carbon budgets and long-term targets. Notably, strained relations between the UK and the EU could impede joint efforts on climate action. In addition, the UK will need to introduce new policies and regulations in instances where EU schemes no longer apply. However, this also presents an opportunity for the UK to develop more stringent policies and regulations than the current EU approaches. Regardless, implementing Brexit will be a significant distraction for UK governments and will present challenges that may threaten UK progress towards its carbon budgets and long-term emissions reduction targets.

ASSESSING THE UK’S PROGRESS TO DATE AND LOOKING AHEAD

Since the introduction of the Act in 2008, the UK has experienced notable emissions reductions—particularly in the power sector—while maintaining continued economic growth. In 2018, UK emissions were 44% below 1990 levels, well beyond the target of 37% by 2020. The UK met both its first (2008 to 2012) and second (2013 to 2017) carbon budgets and is on track to outperform its third (2018 to 2022).

However, the UK is currently not on track to meet its fourth and fifth carbon budgets, let alone its newly legislated net-zero target. According to a 2019 report by the CCC, the UK government and all devolved administrations must significantly and urgently ramp up policy in order to get back on track.

Meeting the first three carbon budgets was relatively straightforward, as the UK government benefited from low-hanging fruit and factors outside their control. Three-quarters of emissions reductions between 2012 and 2016 came from using less coal for power generation. In addition, lower economic growth as a result of the financial crisis in the late 2010s meant lower energy demand, and therefore lower emissions. However, now that coal-fired electricity generation has reached very low levels, the UK must shift its attention to pursuing emissions reductions in more challenging sectors of the economy to meet future carbon budgets and the 2050 target.

While climate accountability legislation is by no means a silver bullet and cannot guarantee that government efforts will be successful in reducing emissions, the UK example illustrates the value of establishing a legislated process to identify and tackle challenges that arise—through independent oversight, transparent monitoring and reporting, and regular opportunities for course correction.

(1) In the Welsh legislation, the baseline year for carbon dioxide, methane, and nitrous oxide is 1990 and the baseline year for hydrofluoro-carbons, perfluorocarbons, sulphur hexafluoride, and nitrogen trifluoride is 1995.

(2) In the Scottish legislation, the baseline year for carbon dioxide, methane, and nitrous oxide is 1990 and the baseline year for hydrofluoro-carbons, perfluorocarbons, sulphur hexafluoride, and nitrogen trifluoride is 1995.

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Climate Change Act, 2008. http://www.legislation.gov.uk/ukpga/2008/27/introduction Climate Change (Scotland) Act, 2009. http://www.legislation.gov.uk/asp/2009/12/contents

Committee on Climate Change. “Carbon Budgets: How We Monitor Emissions Targets.” https://www. theccc.org.uk/tackling-climate-change/reducing-carbon-emissions/carbon-budgets-and-targets/

Committee on Climate Change. “Meeting Carbon Budgets – Implications of Brexit for UK Climate Policy.” https://www.theccc.org.uk/publication/meeting-carbon-budgets-implications-of-brexit-for-uk-climate-policy/

Committee on Climate Change. 2019. Reducing UK Emissions: 2019 Progress Report to Parliament Committee on Climate Change. www.theccc.org.uk/publications

Committee on Climate Change. “UK Regulations: The Climate Change Act.” https://www.theccc.org.uk/ tackling-climate-change/the-legal-landscape/the-climate-change-act/

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