Annex C
Andy Gouldson, Robert Fraser Williamson, Andrew Sudmant & Amelia Duncan
Contact:
a.gouldson@leeds.ac.uk
robert@williamsonconsulting.org
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a. Measuring an Area’s Carbon Footprint
b. Developing a Baseline of Past, Present and Future Emissions
c. Setting Science-Based Carbon Reduction Targets
d. Identifying and Evaluating Carbon Reduction Opportunities
e. Aggregating Up to See the Bigger Picture
f. Developing Targets and Performance Indicators
3. Developing a Baseline of Past, Present and Future Emissions for York
4. Setting Science-based Carbon Reduction Targets for York
5. Aggregating Up: The Bigger Picture for York
6. Developing Targets and Performance Indicators
7. Focusing on Key Sectors in York:
8. Innovative Stretch Measures in York
Appendix 1: League Table of the Most Carbon Effective Options for York
Appendix 2: League Table of the Most Cost Effective Options for York
Appendix 3: Detailed Sectoral Emissions Reduction Potential by Scenario
Appendix 4: Marginal Abatement Chart for York
Appendix 5: Methodology Explored
Background:
· Scientific evidence calls for rapid reductions in global carbon[1] emissions if we are to limit average levels of warming to 1.5°C and so avoid the risks associated with dangerous or runaway climate change.
· Globally, the IPCC suggests that we will have used up the global carbon budget that gives us a good chance of limiting warming to 1.5°C degrees within a decade. This science underpins calls for the declaration of a climate emergency.
· Dividing the global carbon budget up by population gives York a total carbon budget of just over 10 million tonnes from 2020. Based only on the fuel and electricity directly used within its boundaries (i.e. it’s scope 1 and 2 emissions), York currently emits c.888,000 tonnes of carbon a year, and as such it would use up its carbon budget just over 12 years.
· This assessment does not include it’s broader carbon footprint – for example relating to longer distance travel or the goods and services that are produced elsewhere but consumed within York (i.e. it’s scope 3 emissions).
Baselines and Targets:
· Scope 1 and 2 carbon emissions from York have fallen by 44% since the turn of the millennium. With on-going decarbonisation of grid electricity, and taking into account population and economic growth within the city-region, we project that York’s 2000 level of annual emissions will have fallen by a total of 51% in 2030 and 54% in 2050.
· If it is to stay within its carbon budget, York needs to add to adopt science-based carbon emissions reduction targets the build on the emissions reductions already achieved to secure 65% reductions on its 2000 level of emissions by 2025, 76% by 2030, 84% by 2035, 89% by 2040, 92% by 2045 and 95% by 2050.
· Without further activity to address its carbon emissions, we project that York’s annual emissions will exceed its carbon budget by 802,000 tonnes in 2030, and 746,000 tonnes in 2050.
The Cost-Effective Options:
· To meet these carbon emissions reduction targets, York will need to adopt low carbon options that close the gap between its projected emissions in future and net zero emissions. This can be partially realised through cost-effective options that would more than pay for themselves through the energy cost reductions they would generate whilst often also generating wide social and environmental benefits in the area.
· More specifically, the analysis shows that York could close the gap between its projected emissions in 2030 and net zero emissions by 47% purely through the adoption of cost-effective options in houses, public and commercial buildings, transport and industry.
· Adopting these options would reduce York’s total projected annual energy bill in 2030 by £287 million whilst also creating 3,570 years of employment in the city. They could also help to generate wider benefits including helping to tackle fuel poverty, reducing congestion and productivity losses, improving air quality, and enhancements to public health.
· The most carbon effective options for the city to deliver these carbon cuts include improved deep retrofitting of heating, lighting and insulation in houses, cooling and insulation in offices, shops and restaurants, and a range of measures across the transport sector including mode shift to non-motorised transport and the wider up-take of electric vehicles.
The Need for Ambition and Innovation:
· The analysis also shows that York could close the projected gap to net-zero emissions in 2030 by 69% through the adoption of options that are already available, but that some of these options would not pay for themselves directly through the energy savings that they would generate. Many of these options would, however, generate wider indirect benefits both economically and socially in the city.
This means that although it can achieve significant reductions in emissions by focusing on established cost-effective and technically viable measures, York still has to identify other more innovative interventions that could deliver the last 31% of shortfall between projected emissions in 2030 and a net zero target.
· Options identified elsewhere that could be considered in York include targeting a complete transition to net zero homes and public/commercial buildings by 2030, promoting the rapid acceleration of active travel (e.g. walking and cycling), tackling food waste, reducing meat and dairy consumption and reducing concrete and steel consumption/promoting adoption of green infrastructure including accelerated tree planting plans.
· As well as reducing York’s direct (scope 1 and 2) carbon footprint, some of these more innovative measures (e.g. reducing meat and dairy or concrete and steel consumption) could start to focus on tackling York’s broader consumption-based (i.e. scope 3) carbon footprint.
Next Steps:
· York needs to adopt a clear and ambitious climate action plan. The case for the adoption of such a plan is supported by the evidence that much – but not all - of the action that is required can be based on the exploitation of win-win low carbon options that will simultaneously improve economic, social and health outcomes across the city.
· The climate action plan should adopt science-based targets for emissions reduction. As well as longer term targets, it should adopt 5-yearly carbon reduction targets.
· The action plan should focus initially on York’s direct (scope 1 and 2) carbon footprint as these emissions are most directly under the city’s influence, but in time it should also widen its scope to consider its broader (scope 3) carbon footprint.
· The action plan should also set out the ways in which York will work towards achieving these science-based targets, drawing on the deployment KPIs listed in this report. Action should also be taken to monitor and report progress on emissions reductions.
· It is important to stress that delivering on these targets will require action across the city and the active support of the public, private and third sectors. Establishing an independent York Climate Commission could help to draw actors together and to build capacities to take and track action.
· Leadership groups should be formed for key sectors such as homes, public and commercial buildings, transport and industry, with clear plans for delivery of priority actions in each sector. All large organisations and businesses in the city should be asked to match broader carbon reduction commitments and to report back on progress.
Climate science has proven the connection between the concentration of greenhouse gases in the atmosphere and the extent to which the atmosphere traps heat and so leads to global warming. The science tells us – with a very high level of confidence – that such warming will lead to increasingly severe disruption to our weather patterns and water and food systems, and to ecosystems and biodiversity. Perhaps most worryingly, the science predicts that there may be a point where this process becomes self-fuelling, for example where warming leads to the thawing of permafrosts such that they release significant quantities of greenhouse gases leading to further warming. Beyond this point or threshold, the evidence suggests that we may lose control of our future climate and become subject to what has been referred to as dangerous or ‘runaway’ climate change.
Until recently, scientists felt that this threshold existed at around 2 degrees centigrade of global warming, measured as a global average of surface temperatures. However, more recent scientific assessments (especially by the Intergovernmental Panel on Climate Change or IPCC in 2017) have suggested that the threshold should instead be set at 1.5 degrees centigrade. This change in the suggested threshold from 2 degrees to 1.5 degrees has led to calls for targets for decarbonisation to be made both stricter (e.g. for the UK to move from an 80% decarbonisation target to a net zero target), and to be brought forward (e.g. from 2050 to 2030).
Globally, the IPCC
suggests that from 2020 we can only emit 344 billion tonnes of
CO2 if we want to give ourselves a 66% chance of
avoiding dangerous climate change. We are currently emitting over
37 billion tonnes of CO2 every year, which means that we
will have used up our global carbon budget within a decade. It is
this realisation – and the ever accumulating science on the
scale of the impacts of climate change - that led to calls for
organisations and areas to declare a climate emergency and to
develop and implement plans to rapidly reduce GHG emissions.
Any area’s carbon footprint – measured in terms of the total impact of all of its greenhouse gas emissions - can be divided into three types of greenhouse gas emissions.
- Those coming from the fuel (e.g. petrol, diesel or gas) that is directly used within an area and from other sources such as landfill sites or industry within the area. These are known as Scope 1 emissions.
- Those coming from the electricity that is used within the area, even if it is generated somewhere else. These are known as Scope 2 emissions. Together scope 1 and 2 emissions are sometimes referred to as territorial emissions.
- Those associated with the goods and services that are produced elsewhere but imported and consumed within the area. After taking into account the carbon footprint of any goods and services produced in the area but that are exported and consumed elsewhere, these are known as Scope 3 or consumption-based emissions.
In this report we focus on Scope 1 and 2 emissions, and exclude consideration of long-distance travel and of Scope 3 or consumption-based emissions. We do this because Scope 1 and 2 emissions are more directly under the control of actors within an area, and because the carbon accounting and management options for these emissions are better developed. We stress though that emissions from longer distance travel (especially aviation) and consumption are very significant, and also need to be addressed.
To set science-based carbon reduction targets for an area, we take the total global level of emissions that the IPCC suggests gives us a 66% chance of limiting average levels of warming to 1.5 degrees, and divide it according to the share of the global population living in the area in question. This enables us to set the total carbon budget for an area that is consistent with a global budget. To set targets for carbon reduction, we then calculate the annual percentage reductions from the current level that are required to enable an area to stay within its overall carbon budget.
Our analysis then includes assessment of the potential contribution of c.130 * energy saving or low carbon measures for:
- households and for both public and commercial buildings (including better insulation, improved heating, more efficient appliances, some small scale renewables)
- transport (including more walking and cycling, enhanced public transport, electric and more fuel efficient vehicles)
- industry (including better lighting, improved process efficiencies and a wide range of other energy efficiency measures).
We stress that the list of options that is assessed may not be exhaustive; other options could be available and the list can potentially be expanded.
For the options included, we assess the costs of their purchase, installation and maintenance, the direct benefits (through energy and fuel savings) of their adoption in different settings and their viable lifetimes. We also consider the scope for and potential rates of deployment of each option. This allows us to generate league tables of the most carbon and cost-effective options that could be deployed within an area.
It is important to note that we base the analysis on current capital costs, although future costs and benefits are adjusted for inflation and discounting factors. This could be pessimistic if costs fall and benefits increase as some options become more widely adopted, or if the costs increase as the rates of deployment increase. It is also important to note that, although we consider the employment generation potential of different options, we do not consider the wider indirect impacts of the different options relating to their social, economic or environmental implications.
Beyond the range of currently available options, we also consider the need for more innovative or ‘stretch’ options to be developed and adopted within the area if it is to meet its carbon reduction targets. These need to be developed in each area, but the some of the ideas for innovative options identified elsewhere include targeting a full transition to net zero homes and public/commercial buildings by 2030, promoting the rapid acceleration of active travel (e.g. walking and cycling), tackling food waste, reducing meat and dairy consumption and reducing concrete and steel consumption/promoting adoption of green infrastructure.
Based on this bottom-up analysis of the potential for different options to be adopted within the area, we then aggregate up to assess the potential for decarbonisation within that area, and the costs and benefits of different levels of decarbonisation. We then merge the aggregated analysis of the scope for decarbonisation with the baseline projections of future emissions to highlight the extent to which the gap between the projected and required emissions levels that can be met through different levels and forms of action.
To break this gap down, we merge interventions into three broader groupings:
- Cost-Effective (CE) options where the direct costs of adoption are outweighed by the direct benefits that they generate through the energy savings they secure, meaning the portfolio of measures as a whole has a positive economic impact in present value. These options may also generate indirect benefits, for example through job creation, fuel poverty and improved air quality and public health.
- Cost-Neutral (CN) options where the portfolio of interventions mentioned above is expanded to consider investments that may not be as cost effective on their own terms, but where the range of measures as a whole will have near-zero net cost.
- The Technical Potential (TP) options where the direct costs are not (at present) covered by the direct benefits. However, the cost of many low carbon options is falling quickly, and again these options could generate important indirect benefits such as those listed above.
As it is unlikely that adopting all of the cost-effective or even
technically viable options will enable an area to reach net-zero
emissions, we also highlight the need for a fourth group of
measures:
- The innovative or ‘stretch’ options that includes low-carbon measures that are not yet widely adopted. Some of the options within this group may well be cost and carbon effective, and they may also generate significant indirect benefits, but whilst we can predict their carbon saving potential, data on their costs and benefits is not yet available.
Linked to the analysis detailed above, we extend our evaluation of potential emissions reductions across York’s economy to substantive, real-life indicators for the levels of investment and deployment required to achieve targets. These Key Performance Indicators (KPIs) illustrate the scale of ambition required to reach the emissions savings presented in the Technical Potential scenario and are disaggregated by sector.
As well as
presenting an aggregated picture, we also focus on the emissions
saving potential in the housing, public and commercial buildings,
transport, and industry sectors. We focus in on overall investment
needs and returns, and present more detailed league tables of the
most carbon and cost effective options that could be adopted in
each sector.
Analysis shows that York’s baseline (scope 1 and 2) emissions have fallen by 44% since 2000, due to a combination of increasingly decarbonised electricity supply, structural change in the economy, and the gradual adoption of more efficient buildings, vehicles and businesses.
With full decarbonisation of UK electricity by 2050, and taking into account economic growth (assumed at 2.5% p.a.), population growth (assumed at 0.1% p.a.) and on-going improvements in energy and fuel efficiency, we project that York’s baseline (scope 1 and 2) emissions will only fall by a further 7% by 2030, 9% by 2040, and 10% by 2050. This is a total of just under 54% between 2000 and 2050.
Figure.1: York’s Scope 1 and 2 GHG emissions (2000-2050)
Currently, 32% of York’s emissions come from transport, with the domestic housing sector then responsible for 31% of emissions, public & commercial buildings for 22% and industry 16%. Emissions related to land-use contribute c.0.5% and are not considered technically in this report. By 2050, we project emissions from transport will decrease very slightly (still producing c.31%) with a significant 10% increase in the proportion of emissions from housing. Small decreases are forecast in the proportion of emissions from public & commercial buildings and industry, largely a result of expansion in the output of the domestic buildings sector over this period.
Figure.2: York’s Present and Projected Emissions by Sector
Related to this emissions baseline, after evaluating the range of energy sources York consumes (spanning electricity, gas, all solid and liquid fuels across sectors) we find that in 2019 £299 million was spent on energy across the city. Transport fuels generated the majority of this demand (44%), followed by domestic buildings (35%) then public & commercial buildings and industry (13% and 9% respectively). By projecting demand and energy prices into future with reasonable baseline assumptions over population, inflationary measures and efficiency gains across the economy, we find that York’s business as usual energy expenditure will likely grow to just under £320 million per year in 2030 and c.£435 million per year in 2050, with transport expenditure growing in its contribution to York’s total (see Figure 3 below).
Figure.3:
York’s
Present and Projected Energy Expenditure by
Sector
The Inter-governmental Panel on Climate Change (IPCC) has argued that from 2020, keeping within a global carbon budget of 344 gigatonnes (i.e. 344 billion tonnes) of CO2 emissions would give us a 66% chance of limiting average warming to 1.5 degrees and therefore avoiding dangerous levels of climate change. If we divide this global figure up on an equal basis by population, this gives York a total carbon budget of c.10 megatonnes (i.e. 10 million tonnes) over period between the present and 2050.
At current rates of emissions output, York would use up this budget in just over 12 years at some point during the spring of 2032. However, York could stay within its carbon budget by reducing its emissions by just over 7% year on year. This would mean that to transition from the current position where emissions are 44% lower than 2000 levels to a local pathway that is consistent with the world giving itself a 66% chance of avoiding dangerous, runaway climate change, York should adopt carbon reduction targets (on 2000 levels) of:
· 65% by 2025
· 76% by 2030
· 84% by 2035
· 89% by 2040
· 92% by 2045
· 95% by 2050.
Such a trajectory would mean that the majority of all future carbon cuts needed for York to transition to a 1.5 degree consistent pathway need to be delivered in the next 10 years.
Figure.4: York’s Baseline and Science-Based-Target Emissions Pathways
a) Emissions reductions
Our analysis predicts that the gap between York’s business as usual emissions in 2030 and the net zero target could be closed by 47 % (379ktCO2e) through the adoption of Cost-Effective (CE) options, by a further 15% (118ktCO2e) through the adoption of additional Cost-Neutral (CN) options at no net cost, and then by an additional 7% (53ktCO2e) through the further adoption of all technically viable (TP) options. This means that York still has to identify the innovative or stretch options that could deliver the last 31% (252ktCO2e) of the gap between the business as usual scenario and net zero in 2030.
Figure.5: York’s BAU Baseline with Cost-Effective, Cost-Neutral, & Technical Potential Scenarios
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2025 |
2030 |
2035 |
2040 |
2045 |
2050 |
Reduction on BAU Baseline |
CE |
38% |
47% |
44% |
44% |
44% |
41% |
CN |
46% |
62% |
59% |
59% |
59% |
58% |
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TP |
51% |
69% |
65% |
66% |
65% |
65% |
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Reduction on Present Emissions |
CE |
35% |
43% |
39% |
37% |
37% |
35% |
CN |
43% |
56% |
51% |
50% |
50% |
49% |
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TP |
47% |
62% |
57% |
56% |
55% |
55% |
Table.1: York’s Potential 5-Year Emissions Reduction Percentages
b) The most carbon and cost-effect options
Figure 6 below presents the emissions savings that could be achieved through different groups of measures in York. Appendices 1 and 2 present league tables of specific measures and their potential emissions savings over this period.
Figure.6: Simplified Emissions Reduction Potential by Measure for York
Simplified league tables of the most cost and carbon effective options in York are presented below (see Appendices 1 & 2 for more detailed league tables).
Rank |
Measure |
Cost Effectiveness (£/tCO2e) |
1 |
Fabric improvements in Retail buildings |
-571 |
2 |
Diesel Car to Bus (diesel) Journeys |
-458 |
3 |
Improved cooling in Retail buildings |
-393 |
4 |
Petrol Car to Bus (diesel) Journeys |
-373 |
5 |
Diesel Car to Walk Journeys |
-345 |
6 |
Diesel Car to Bicycle Journeys |
-345 |
7 |
Petrol Car to Bicycle Journeys |
-323 |
8 |
Petrol Car to Walk Journeys |
-323 |
9 |
Fabric improvements in Public buildings |
-276 |
10 |
Petrol Car to Plug-in hybrid Journeys |
-214 |
Table.5: York’s Top-10 Most Cost-Effective Emission Reduction Options
Rank |
Measure |
Emissions Reduction Potential 2020-50 (ktCO2e) |
1 |
Insulating Domestic buildings |
906 |
2 |
Upgraded Heating controls in Domestic buildings |
846 |
3 |
Electrical upgrades in Domestic buildings |
669 |
4 |
Installing heat pumps in Domestic & Office buildings |
653 |
5 |
Petrol Car to Bicycle Journeys |
636 |
6 |
Petrol Car to Walk Journeys |
636 |
7 |
Fabric improvements in Retail buildings |
515 |
8 |
Petrol Car to Bus (electric) Journeys |
485 |
9 |
Upgraded boilers in Domestic buildings |
481 |
10 |
Electricity demand reduction in Domestic buildings |
475 |
Table.6: York’s Top-10 Most Carbon Effective Emission Reduction Options
Some of the ideas for innovative options identified elsewhere that could also be considered for York include targeting a full transition to net zero homes and public/commercial buildings by 2030, promoting the rapid acceleration of active travel (e.g. walking and cycling), tackling food waste, reducing meat and dairy consumption and reducing concrete and steel consumption/promoting adoption of green infrastructure. These are highlighted in section 8.
c) Investment needs, paybacks and employment creation
Exploiting the cost-effective options in households, public and commercial buildings, transport, industry and waste could be economically beneficial. Although such measures would require total investments of around £1.1 billion over their lifetimes (equating to investments of 110m a year across all organisations and households in the city for the next decade), once adopted they would reduce York’s total energy bill by £287 million p.a. in 2030 whilst also creating 3,570 years of employment – or 357 full-time jobs for the next decade.
By expanding this portfolio of measures to at no net cost to York’s economy (the Cost-Neutral scenario), investments of £2.3 billion over their lifetimes (or £230m a year for the next decade) would generate 5,887 years of employment (or 588 jobs for the next decade) whilst reducing York’ emissions by 62% of projected 2030 levels.
Exploiting the all technically viable options would be more expensive (at least at current prices, c.£3 billion or £300m a year for the next decade) but realise further emissions savings – eliminating 69% of the projected shortfall in York’s 2030 emissions, whilst saving hundreds of millions of pounds on an annual basis.
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2025 |
2030 |
2035 |
2040 |
2045 |
2050 |
Cumulative Investment (£M) |
CE |
763 |
1,160 |
1,162 |
1,163 |
1,164 |
1,164 |
CN |
1,442 |
2,223 |
2,254 |
2,256 |
2,257 |
2,257 |
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TP |
1,934 |
2,964 |
2,995 |
2,997 |
2,997 |
2,997 |
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Annual Energy Expenditure Savings (£M) |
CE |
203 |
287 |
284 |
285 |
281 |
284 |
CN |
188 |
258 |
256 |
248 |
239 |
233 |
|
TP |
187 |
255 |
252 |
245 |
235 |
227 |
Table.2: Potential 5-Year Investments and Energy Expenditure Savings
Sector |
Scenario |
Investment (£M) |
Domestic |
CE |
584 |
CN |
924 |
|
TP |
1,170 |
|
Public & Commercial |
CE |
448 |
CN |
504 |
|
TP |
909 |
|
Industry |
CE |
17 |
CN |
198 |
|
TP |
287 |
|
Transport |
CE |
115 |
CN |
631 |
|
TP |
631 |
Table.3: Potential Investments by Sector & Economic Scenario
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Total |
Domestic |
Industry |
Transport |
Public & Commercial |
|
Years of Employment |
CE |
3,570 |
1,250 |
58 |
157 |
2,106 |
CN |
5,887 |
1,975 |
676 |
864 |
2,371 |
|
TP |
8,623 |
2,503 |
982 |
864 |
4,274 |
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Jobs (20-year Period) |
CE |
179 |
62 |
3 |
8 |
105 |
CN |
294 |
99 |
34 |
43 |
119 |
|
TP |
431 |
125 |
49 |
43 |
214 |
Table.4: Potential Job Creation by Sector & Economic Scenario
To give an indication of the levels of activity required to deliver on these broader targets, the tables below detail total deployment across different sectors in York through to 2050. We also give an indication of the rate of deployment required in the city if it is to even approximate its climate targets. These lists are not exhaustive, and also apply by measure; any one building or industrial facility will usually require the application of several measures over the period. These figures effectively become Key Performance Indicators (KPIs) for the delivery of climate action across the city.
Domestic Homes:
Measure |
Total Homes Applied |
Mean Annual Rate of Installation (homes) |
Lighting Upgrades |
51,631 |
2,963 |
Floor Insulation |
48,546 |
2,732 |
Glazing Upgrades |
45,597 |
2,589 |
Gas Boiler Upgrades & Repairs |
46,800 |
2,506 |
Solar PV |
35,810 |
2,055 |
Thermostats & Heating Controls |
35,116 |
1,976 |
Solar thermal |
36,430 |
1,955 |
Loft insulation |
32,283 |
1,748 |
Wall Insulation |
23,111 |
1,290 |
Draught Proofing |
18,401 |
1,044 |
Cavity wall Insulation |
15,350 |
856 |
Heat Pumps |
3,780 |
215 |
Public & Commercial Buildings:
Measure |
Floorspace Applied (m2) |
Mean Annual Rate of Installation (m2) |
Lighting/Heating Controls and Sensors |
1,450,231 |
82,076 |
Retail Heating Upgrades |
1,420,740 |
80,425 |
Wind Turbines |
795,241 |
45,815 |
Office Lighting Upgrades |
398,040 |
23,006 |
Office Fabric Improvements |
279,564 |
15,595 |
Office Heat Pumps |
114,492 |
6,328 |
Office Solar PV |
93,984 |
5,168 |
Transport:
Measure |
Deployment |
Additional EVs Replacing Conventional Private Cars |
1,536 |
Additional Electric-Buses Procured and In-service |
85 |
High Quality Protected Cycling Highways Built |
9 kilometres |
Increase in Public Transport Ridership |
4M trips per annum |
Table.7: York’s Sectoral Emissions Reduction KPIs
At full deployment (technical potential) across York, we calculate that there is potential to avoid over 14MtCO2e in emissions that will otherwise be produced in the city between 2020 and 2050. The transport sector will contribute most significantly toward this total, with a decarbonisation potential of between 4MtCO2e (cost-effective scenario) and 6MtCO2e (technical potential) through the period. However, domestic housing , industry and public and commercial buildings also play a major role:; upgrading and retrofitting of York’s built environment (including the domestic, public and commercial sectors) could reduce emissions by up to c.8MtCO2e over the same period at full technical potential, with industry similarly showing the potential to decarbonise nearly 500ktCO2e under the same conditions.
Figure.7 York’s Emissions Reduction Potential (2020-2050) by Sector
Figure.8: York’s Emissions Reduction Potential By Sector & Economic Scenario (2020-50)
In the following section, summaries of the emissions reduction potential and economic implications of investment are presented for the four main sectors. For display and continuity purposes, each sector is displayed with a summary of the same metrics: (1) emissions reduction potential over time in the three economic scenarios, (2) 5-year totals for cumulative emissions savings, investment requirements and annual energy expenditure reductions, and (3) a simplified table of the most cost effective low carbon measures applied in each sector across York.
|
|
2025 |
2030 |
2035 |
2040 |
2045 |
2050 |
Emissions Reductions (ktCO2e) |
CE |
111 |
154 |
143 |
144 |
153 |
143 |
CN |
121 |
183 |
167 |
169 |
174 |
170 |
|
TP |
148 |
222 |
203 |
206 |
209 |
209 |
|
Annual Energy Expenditure Savings (£M) |
CE |
67 |
110 |
113 |
116 |
113 |
118 |
CN |
83 |
137 |
140 |
141 |
142 |
147 |
|
TP |
70 |
114 |
116 |
118 |
118 |
122 |
|
Cumulative Investment (£M) |
CE |
368 |
584 |
584 |
584 |
584 |
584 |
CN |
575 |
924 |
924 |
924 |
924 |
924 |
|
TP |
727 |
1,170 |
1,170 |
1,170 |
1,170 |
1,170 |
Rank |
Measure |
Cost Effectiveness (£/tCO2e) |
1 |
Electrical & Appliance upgrades in Domestic buildings |
-208 |
2 |
Lighting improvements in Domestic buildings |
-145 |
3 |
Electricity demand reduction in Domestic buildings |
-137 |
4 |
Draught-proofing in Domestic buildings |
-50 |
5 |
Installing heat pumps in Domestic buildings |
-37 |
6 |
Upgraded Heating controls in Domestic buildings |
-28 |
7 |
Glazing improvements in Domestic buildings |
-27 |
8 |
Installing biomass boilers in Domestic buildings |
-24 |
9 |
Solar thermal devices in Domestic buildings |
-18 |
10 |
Upgraded boilers in Domestic buildings |
-11 |
|
|
2025 |
2030 |
2035 |
2040 |
2045 |
2050 |
Emissions Reductions (ktCO2e) |
CE |
50 |
74 |
61 |
60 |
60 |
60 |
CN |
60 |
90 |
73 |
72 |
72 |
73 |
|
TP |
67 |
100 |
82 |
81 |
80 |
81 |
|
Annual Energy Expenditure Savings (£M) |
CE |
65 |
107 |
105 |
110 |
113 |
117 |
CN |
21 |
35 |
34 |
36 |
37 |
39 |
|
TP |
33 |
53 |
52 |
55 |
57 |
59 |
|
Cumulative Investment (£M) |
CE |
278 |
448 |
448 |
448 |
448 |
448 |
CN |
314 |
504 |
504 |
504 |
504 |
504 |
|
TP |
565 |
909 |
909 |
909 |
909 |
909 |
Rank |
Measure |
Cost Effectiveness (£/tCO2e) |
1 |
Fabric improvements in Retail buildings |
-571 |
2 |
Improved cooling in Retail buildings |
-393 |
3 |
Fabric improvements in Public buildings |
-276 |
4 |
Lighting improvements in Public buildings |
-200 |
5 |
Improved cooling in Office buildings |
-198 |
6 |
Heating improvements in Public buildings |
-139 |
7 |
Lighting improvements in Retail buildings |
-132 |
8 |
Improved cooling in Public buildings |
-97 |
9 |
Heating improvements in Office buildings |
-82 |
10 |
Heating improvements in Retail buildings |
-53 |
|
|
2025 |
2030 |
2035 |
2040 |
2045 |
2050 |
Emissions Reductions (ktCO2e) |
CE |
148 |
148 |
137 |
127 |
116 |
105 |
CN |
182 |
208 |
204 |
198 |
191 |
183 |
|
TP |
182 |
208 |
204 |
198 |
191 |
183 |
|
Annual Energy Expenditure Savings (£M) |
CE |
68 |
67 |
64 |
59 |
54 |
49 |
CN |
75 |
78 |
73 |
65 |
56 |
47 |
|
TP |
75 |
78 |
73 |
65 |
56 |
47 |
|
Cumulative Investment (£M) |
CE |
100 |
111 |
113 |
114 |
115 |
115 |
CN |
355 |
598 |
629 |
631 |
631 |
631 |
|
TP |
355 |
598 |
629 |
631 |
631 |
631 |
Rank| |
Measure* |
Cost Effectiveness (£/tCO2e) |
1 |
Diesel Car to Bus (diesel) |
-458 |
2 |
Petrol Car to Bus (diesel) |
-373 |
3 |
Diesel Car to Walk |
-345 |
4 |
Diesel Car to Bicycle |
-345 |
5 |
Petrol Car to Bicycle |
-323 |
6 |
Petrol Car to Walk |
-323 |
7 |
Petrol Car to Plug-in hybrid |
-214 |
8 |
Diesel Car to Plug-in hybrid |
-136 |
9 |
Petrol Car to EV |
-133 |
10 |
Petrol Car to Bus (electric) |
-129 |
|
|
2025 |
2030 |
2035 |
2040 |
2045 |
2050 |
Emissions Reductions (ktCO2e) |
CE |
5 |
4 |
2 |
0 |
0 |
0 |
CN |
19 |
16 |
12 |
8 |
7 |
7 |
|
TP |
24 |
21 |
16 |
11 |
10 |
10 |
|
Annual Energy Expenditure Savings (£M) |
CE |
3 |
3 |
3 |
1 |
1 |
0 |
CN |
9 |
9 |
9 |
6 |
4 |
0 |
|
TP |
10 |
10 |
10 |
7 |
5 |
0 |
|
Cumulative Investment (£M) |
CE |
3 |
17 |
17 |
17 |
17 |
17 |
CN |
40 |
198 |
198 |
198 |
198 |
198 |
|
TP |
57 |
287 |
287 |
287 |
287 |
287 |
Rank* |
Measure |
Cost Effectiveness (£/tCO2e) |
1 |
Improving Efficiency of Boilers and Steam Piping in Industry |
307 |
2 |
Fan Correction, Repairs, & Upgrades in Industry |
663 |
3 |
Condensing & Insulation Measures to Boilers & Steam Piping in Industry |
719 |
4 |
Pump Upgrades, Repairs and Maintenance in Industry |
825 |
5 |
Compressed Air Systems in Industry |
1,055 |
6 |
Furnace Efficiency and Heat Recovery Mechanisms in Industry |
3,213 |
7 |
Refrigeration Efficiency and Technical Upgrades in Industry |
15,656 |
Even with full delivery of the broad programme of cross-sectoral, city-wide low carbon investment described above, there remains an emissions shortfall of 31% between York’s 2030 BAU baseline and the net zero target. Here we briefly consider the productivity of certain key technologies and interventions that may well be able to plug this gap into the future. Many of these so-called ‘stretch options’ are innovative by nature but they will be required to reach York’s targets in future.
|
2025 |
2030 |
2035 |
|
Annual Emissions Reduction Potential (ktCO2e) |
Zero Carbon Heavy Goods Transport |
11 |
48 |
48 |
Industrial Heat and Cooling Electrification |
12 |
12 |
7 |
|
870 Ha. Reforested Annually 2020-29* |
47 |
120 |
148 |
|
Electrification of Domestic Heat |
6 |
33 |
48 |
|
Electrification of Domestic Cooking |
2 |
11 |
15 |
|
Electrification of Commercial/Public Heating |
3 |
8 |
3 |
Table.7: Stretch Measures’ Decarbonising Potential ( * Sequestration Values)
Figure 10 below shows the impact that the adoption of these stretch measures would have on York’s carbon emissions, with the red dotted line showing the ‘business as usual’ baseline, the purple dotted line showing emissions after adoption of all technically viable options and the blue dotted line showing emissions after all technically viable and stretch options. This indicates that York would still have some residual emissions through to 2050. For illustration, the green dotted line shows that in theory York could offset is residual emissions through a UK based tree planting scheme, however this would require the planting of 39 million trees, which even with the densest possible planting would require 8,700 hectares of land, equivalent to 32% of the total land area of the city.
Figure.10: Sectoral Emissions Shortfall Reduction with Stretch Measures
Based on the analysis presented above, we recommend that if York wants to stay within its share of the global carbon budget, it needs to adopt a clear and ambitious climate action plan.
The case for the adoption of such a plan is supported by the evidence that much – but not all - of the action that is required can be based on the exploitation of win-win low carbon options that will simultaneously improve economic, social and health outcomes across the city.
A climate action plan for York should adopt science-based targets for emissions reduction, including both longer term targets and 5-yearly carbon reduction targets.
The action plan should focus initially on York’s direct (scope 1 and 2) carbon footprint as these emissions are most directly under the city’s influence, but in time it should also widen its scope to consider its broader (scope 3) carbon footprint.
The action plan should clearly set out the ways in which York will work towards achieving these targets, drawing on the deployment KPIs listed in this report. Action should also be taken to monitor and report progress on emissions reductions.
It is important to stress that delivering on these targets will require action across the city and the active support of the public, private and third sectors. Establishing an independent York Climate Commission could help to draw actors together and to build capacities to take and track action.
Such a Commission could act as a critical friend to the city, helping to promote stakeholder engagement and build buy-in and a sense of common ownership for the climate action plan, as well as in supporting, guiding and tracking progress towards its delivery.
Through such a Commission, cross-sectoral leadership groups could be formed for key sectors such as homes, public and commercial buildings, transport and industry, with clear plans for the delivery of priority actions in each sector. All large organisations and businesses in the city should be asked to match broader carbon reduction commitments and to report back on progress.
Measure* |
Emissions Reduction Potential (ktCO2e) |
Insulating Domestic buildings |
906 |
Upgraded Heating controls in Domestic buildings |
846 |
Electrical upgrades in Domestic buildings |
669 |
Installing heat pumps in Domestic buildings |
653 |
Petrol Car to Bicycle |
636 |
Petrol Car to Walk |
636 |
Fabric improvements in Retail buildings |
515 |
Petrol Car to Bus (electric) |
485 |
Upgraded boilers in Domestic buildings |
481 |
Electricity demand reduction in Domestic buildings |
475 |
Diesel Car to Walk |
464 |
Diesel Car to Bicycle |
464 |
Installing solar PV in Domestic Buildings |
444 |
Petrol Car to EV |
439 |
Petrol Car to Bus (diesel) |
395 |
Petrol Car to Plug-in hybrid |
375 |
Petrol Car to Hybrid |
375 |
Diesel Car to EV |
370 |
Diesel Car to Bus (electric) |
341 |
Fabric improvements in Public buildings |
338 |
Diesel Car to Plug-in hybrid |
276 |
Lighting improvements in Domestic buildings |
276 |
Draught-proofing in Domestic buildings |
257 |
Installing biomass boilers in Domestic buildings |
252 |
Hybrid Car to EV |
240 |
Glazing improvements in Domestic buildings |
228 |
Diesel Car to Bus (diesel) |
224 |
Heating improvements in Public buildings |
213 |
Solar thermal devices in Domestic buildings |
193 |
Condensing & Insulation Measures to Boilers & Steam Piping in Industry |
185 |
Installing air source heat pumps in Office buildings |
163 |
Solar thermal devices in Public buildings |
148 |
Lighting improvements in Office buildings |
133 |
Improving Efficiency of Boilers and Steam Piping in Industry |
131 |
Solar thermal devices in Retail buildings |
125 |
Wind microgeneration associated with Public buildings |
103 |
Improved lighting controls and sensors in Public buildings |
89 |
Upgrading heating controls in Office buildings |
86 |
Improved lighting controls and sensors in Office buildings |
86 |
Improved cooling in Office buildings |
85 |
Improved lighting controls and sensors in Retail buildings |
72 |
Diesel Car to Hybrid |
66 |
Lighting improvements in Public buildings |
66 |
Compressed Air Systems in Industry |
54 |
Pump Upgrades, Repairs and Maintenance in Industry |
49 |
Heating improvements in Retail buildings |
42 |
Fan Correction, Repairs, & Upgrades in Industry |
34 |
Furnace Efficiency and Heat Recovery Mechanisms in Industry |
34 |
Installing solar PV in Public buildings |
13 |
Fabric improvements in Office buildings |
10 |
Improved cooling in Public buildings |
10 |
Refrigeration Efficiency and Technical Upgrades in Industry |
7 |
Improved cooling in Retail buildings |
7 |
Installing solar PV in Office buildings |
5 |
Heating improvements in Office buildings |
5 |
Installing air source heat pumps in Retail buildings |
4 |
Upgraded heating controls in Retail buildings |
4 |
Installing air source heat pumps in Public buildings |
4 |
Lighting improvements in Retail buildings |
4 |
Wind microgeneration associated with Retail buildings |
4 |
Upgraded heating controls in Public buildings |
4 |
Solar thermal devices in Office buildings |
4 |
Installing solar PV in Retail buildings |
3 |
Wind microgeneration associated with Office buildings |
3 |
TOTAL |
14,306 |
Measure* |
Cost Effectiveness (£/tCO2e) |
Fabric improvements in Retail buildings |
-571 |
Diesel Car to Bus (diesel) |
-458 |
Improved cooling in Retail buildings |
-393 |
Petrol Car to Bus (diesel) |
-373 |
Diesel Car to Walk |
-345 |
Diesel Car to Bicycle |
-345 |
Petrol Car to Bicycle |
-323 |
Petrol Car to Walk |
-323 |
Fabric improvements in Public buildings |
-276 |
Petrol Car to Plug-in hybrid |
-214 |
Electrical upgrades in Domestic buildings |
-208 |
Lighting improvements in Public buildings |
-200 |
Improved cooling in Office buildings |
-198 |
Lighting improvements in Domestic buildings |
-145 |
Heating improvements in Public buildings |
-139 |
Electricity demand reduction in Domestic buildings |
-137 |
Diesel Car to Plug-in hybrid |
-136 |
Petrol Car to EV |
-133 |
Lighting improvements in Retail buildings |
-132 |
Petrol Car to Bus (electric) |
-129 |
Petrol Car to Hybrid |
-114 |
Improved cooling in Public buildings |
-97 |
Heating improvements in Office buildings |
-82 |
Insulating Domestic buildings |
-76 |
Diesel Car to Bus (electric) |
-63 |
Heating improvements in Retail buildings |
-53 |
Lighting improvements in Office buildings |
-53 |
Draught-proofing in Domestic buildings |
-50 |
Diesel Car to EV |
-41 |
Fabric improvements in Office buildings |
-38 |
Installing heat pumps in Domestic buildings |
-37 |
Upgraded Heating controls in Domestic buildings |
-28 |
Glazing improvements in Domestic buildings |
-27 |
Upgrading heating controls in Office buildings |
-26 |
Installing biomass boilers in Domestic buildings |
-24 |
Solar thermal devices in Domestic buildings |
-18 |
Diesel Car to Hybrid |
-12 |
Upgraded heating controls in Public buildings |
-11 |
Upgraded boilers in Domestic buildings |
-11 |
Upgraded heating controls in Retail buildings |
-8 |
Installing air source heat pumps in Retail buildings |
-1 |
Hybrid Car to EV |
3 |
Installing solar PV in Domestic Buildings |
3 |
Installing air source heat pumps in Public buildings |
10 |
Solar thermal devices in Retail buildings |
19 |
Improved lighting controls and sensors in Retail buildings |
29 |
Installing air source heat pumps in Office buildings |
30 |
Installing solar PV in Public buildings |
40 |
Installing solar PV in Office buildings |
53 |
Installing solar PV in Retail buildings |
55 |
Improved lighting controls and sensors in Office buildings |
71 |
Solar thermal devices in Public buildings |
76 |
Solar thermal devices in Office buildings |
112 |
Wind microgeneration associated with Office buildings |
158 |
Improved lighting controls and sensors in Public buildings |
174 |
Wind microgeneration associated with Public buildings |
196 |
Wind microgeneration associated with Retail buildings |
307 |
Improving Efficiency of Boilers and Steam Piping in Industry |
307 |
Fan Correction, Repairs, & Upgrades in Industry |
663 |
Condensing & Insulation Measures to Boilers & Steam Piping in Industry |
719 |
Pump Upgrades, Repairs and Maintenance in Industry |
825 |
Compressed Air Systems in Industry |
1,055 |
Furnace Efficiency and Heat Recovery Mechanisms in Industry |
3,213 |
Refrigeration Efficiency and Technical Upgrades in Industry |
15,656 |
|
|
|
2020 |
2021 |
2022 |
2023 |
2024 |
2025 |
2026 |
2027 |
2028 |
2029 |
2030 |
2031 |
2032 |
2033 |
2034 |
2035 |
2036 |
2037 |
2038 |
2039 |
2040 |
2041 |
2042 |
2043 |
2044 |
2045 |
2046 |
2047 |
2048 |
2049 |
2050 |
Domestic Housing |
Reduction on BAU Emissions (ktCO2e) |
CE |
5% |
10% |
17% |
23% |
31% |
40% |
47% |
54% |
57% |
58% |
55% |
58% |
56% |
53% |
54% |
51% |
50% |
49% |
51% |
52% |
50% |
52% |
52% |
50% |
49% |
52% |
51% |
51% |
48% |
47% |
47% |
CN |
5% |
12% |
19% |
25% |
35% |
44% |
54% |
60% |
64% |
66% |
65% |
64% |
64% |
61% |
61% |
59% |
59% |
59% |
59% |
59% |
59% |
59% |
59% |
59% |
58% |
59% |
57% |
57% |
56% |
55% |
56% |
||
TP |
7% |
14% |
23% |
32% |
43% |
53% |
65% |
72% |
78% |
80% |
79% |
79% |
77% |
76% |
75% |
72% |
73% |
72% |
72% |
73% |
72% |
72% |
72% |
71% |
71% |
71% |
70% |
69% |
68% |
68% |
69% |
||
Reduction on 2020 Emissions (ktCO2e) |
CE |
5% |
10% |
17% |
23% |
30% |
40% |
47% |
54% |
57% |
58% |
55% |
58% |
56% |
53% |
55% |
51% |
51% |
50% |
52% |
53% |
52% |
53% |
54% |
52% |
51% |
55% |
55% |
55% |
51% |
51% |
51% |
|
CN |
5% |
11% |
18% |
25% |
34% |
43% |
53% |
60% |
64% |
66% |
66% |
64% |
64% |
61% |
62% |
60% |
60% |
60% |
60% |
60% |
60% |
61% |
61% |
61% |
60% |
62% |
61% |
61% |
61% |
59% |
61% |
||
TP |
7% |
14% |
22% |
31% |
43% |
53% |
64% |
72% |
79% |
81% |
80% |
79% |
77% |
76% |
75% |
73% |
74% |
74% |
73% |
74% |
74% |
74% |
74% |
74% |
74% |
75% |
74% |
73% |
73% |
73% |
75% |
||
Public & Commercial buildings |
Reduction on BAU Emissions (ktCO2e) |
CE |
4% |
8% |
13% |
19% |
25% |
29% |
34% |
39% |
43% |
45% |
46% |
46% |
45% |
44% |
41% |
41% |
41% |
42% |
42% |
43% |
44% |
44% |
45% |
45% |
46% |
46% |
46% |
48% |
48% |
48% |
49% |
CN |
5% |
10% |
16% |
23% |
30% |
35% |
40% |
47% |
51% |
54% |
56% |
55% |
53% |
53% |
50% |
49% |
49% |
50% |
51% |
52% |
52% |
53% |
54% |
54% |
55% |
55% |
56% |
57% |
57% |
57% |
59% |
||
TP |
5% |
11% |
18% |
25% |
34% |
39% |
45% |
52% |
57% |
61% |
63% |
62% |
60% |
59% |
56% |
55% |
54% |
56% |
57% |
58% |
58% |
59% |
60% |
60% |
62% |
61% |
62% |
64% |
64% |
64% |
66% |
||
Reduction on 2020 Emissions (ktCO2e) |
CE |
4% |
8% |
12% |
17% |
22% |
26% |
29% |
34% |
37% |
38% |
38% |
38% |
35% |
34% |
32% |
32% |
31% |
31% |
31% |
31% |
31% |
31% |
32% |
31% |
32% |
31% |
31% |
32% |
31% |
31% |
31% |
|
CN |
5% |
9% |
15% |
21% |
27% |
31% |
35% |
41% |
44% |
46% |
47% |
45% |
42% |
42% |
39% |
38% |
37% |
38% |
37% |
38% |
37% |
37% |
38% |
37% |
38% |
37% |
37% |
38% |
37% |
37% |
38% |
||
TP |
5% |
10% |
17% |
23% |
30% |
35% |
39% |
45% |
49% |
51% |
52% |
50% |
47% |
47% |
43% |
42% |
41% |
42% |
42% |
42% |
42% |
42% |
42% |
42% |
42% |
42% |
42% |
42% |
42% |
41% |
42% |
||
Transport |
Reduction on BAU Emissions (ktCO2e) |
CE |
54% |
54% |
55% |
55% |
56% |
56% |
57% |
57% |
58% |
58% |
59% |
59% |
58% |
58% |
57% |
57% |
56% |
56% |
55% |
54% |
54% |
53% |
52% |
52% |
51% |
50% |
49% |
48% |
47% |
47% |
46% |
CN |
58% |
60% |
63% |
65% |
67% |
69% |
72% |
74% |
77% |
80% |
83% |
83% |
83% |
84% |
84% |
84% |
84% |
84% |
84% |
84% |
84% |
84% |
84% |
83% |
83% |
82% |
82% |
81% |
81% |
80% |
80% |
||
TP |
58% |
60% |
63% |
65% |
67% |
69% |
72% |
74% |
77% |
80% |
83% |
83% |
83% |
84% |
84% |
84% |
84% |
84% |
84% |
84% |
84% |
84% |
84% |
83% |
83% |
82% |
82% |
81% |
81% |
80% |
80% |
||
Reduction on 2020 Emissions (ktCO2e) |
CE |
54% |
54% |
53% |
53% |
53% |
52% |
52% |
52% |
52% |
52% |
52% |
52% |
51% |
50% |
50% |
49% |
48% |
47% |
46% |
46% |
45% |
44% |
43% |
43% |
42% |
41% |
40% |
40% |
39% |
38% |
37% |
|
CN |
58% |
59% |
60% |
62% |
63% |
65% |
67% |
68% |
69% |
72% |
74% |
73% |
73% |
73% |
73% |
72% |
72% |
72% |
71% |
71% |
70% |
70% |
69% |
69% |
68% |
68% |
67% |
67% |
66% |
66% |
65% |
||
TP |
58% |
59% |
60% |
62% |
63% |
65% |
67% |
68% |
69% |
72% |
74% |
73% |
73% |
73% |
73% |
72% |
72% |
72% |
71% |
71% |
70% |
70% |
69% |
69% |
68% |
68% |
67% |
67% |
66% |
66% |
65% |
||
Industry
|
Reduction on BAU Emissions (ktCO2e) |
CE |
2% |
3% |
4% |
4% |
4% |
4% |
4% |
4% |
4% |
3% |
3% |
3% |
3% |
3% |
3% |
2% |
2% |
1% |
1% |
0% |
0% |
0% |
0% |
0% |
0% |
0% |
0% |
0% |
0% |
0% |
0% |
CN |
6% |
10% |
14% |
17% |
16% |
16% |
16% |
15% |
15% |
14% |
14% |
14% |
13% |
13% |
12% |
12% |
11% |
10% |
9% |
9% |
8% |
8% |
7% |
7% |
7% |
7% |
8% |
8% |
8% |
8% |
8% |
||
TP |
8% |
12% |
17% |
20% |
20% |
19% |
19% |
19% |
18% |
18% |
18% |
17% |
17% |
17% |
16% |
15% |
14% |
13% |
13% |
12% |
12% |
11% |
11% |
11% |
11% |
11% |
11% |
11% |
11% |
11% |
12% |
||
Reduction on 2020 Emissions (ktCO2e) |
CE |
2% |
2% |
3% |
4% |
4% |
4% |
3% |
3% |
3% |
3% |
3% |
2% |
2% |
2% |
2% |
2% |
1% |
1% |
1% |
0% |
0% |
0% |
0% |
0% |
0% |
0% |
0% |
0% |
0% |
0% |
0% |
|
CN |
6% |
9% |
13% |
15% |
14% |
14% |
14% |
13% |
13% |
12% |
12% |
11% |
11% |
10% |
10% |
9% |
8% |
7% |
7% |
6% |
6% |
5% |
5% |
5% |
5% |
5% |
5% |
5% |
5% |
5% |
5% |
||
TP |
8% |
11% |
15% |
19% |
18% |
17% |
17% |
16% |
16% |
15% |
15% |
14% |
13% |
13% |
12% |
12% |
11% |
10% |
9% |
9% |
8% |
8% |
7% |
7% |
7% |
7% |
7% |
7% |
7% |
7% |
7% |
Sector |
Measure |
Application Data |
Commercial |
Office T5 Lighting (conversions & new luminaries) |
kWh/m2 - £2018 CAPEX/OPEX/EoL - |
Retail PIR Movement & Daylight Sensors |
kWh/m2 - £2018 CAPEX/OPEX/EoL - |
|
… |
||
Transport |
Private EV Penetration |
kWh/m2 - £2018 CAPEX/OPEX/EoL - |
Public EV Buses |
kWh/m2 - £2018 CAPEX/OPEX/EoL - |
|
… |
||
Domestic |
Detached House Cavity Wall Insulation |
kWh/m2 - £2018 CAPEX/OPEX/EoL - |
High-Rise Flat Draught Proofing Measures |
kWh/m2 - £2018 CAPEX/OPEX/EoL - |
|
… |
||
Industrial |
Boilers/Steam Systems Upgrades |
kWh/m2 - £2018 CAPEX/OPEX/EoL - |
Furnaces/Process Heaters Improvements |
kWh/m2 - £2018 CAPEX/OPEX/EoL - |
|
… |
[1] For simplicity, we use the term ‘carbon’ as shorthand for all greenhouse gases, with all figures in this report relating to the carbon dioxide equivalent (CO2e) of all greenhouse gases unless otherwise stated. Note that our assessment therefore differs from other assessments that focus only on CO2.
* We evaluate over 130 separate low carbon technologies/interventions applied across sectors, with variable place-specific data on how their productivity and economics will change by application. This results in over 1000 unique data points customised to York’s economy, infrastructures and demography.
Note: Due to the high cost-effectiveness of many transport mode-shift options, the TP scenario has been removed and emissions pathways are covered by CE and CN only.
* Journey transitions
* For display purposes interventions in industry have been aggregated here into the 7 relevant process types
* Measures listed here have been grouped and summed across multiple applications for display purposes; ‘ICE’ and ‘NMT’ refer to Internal Combustion Engine and Non-Motorised Transport respectively; Transport measures refer to transitions between travel modes.
* Measures listed here have been grouped and summed across multiple applications for display purposes; the cost per tonne of emissions reduction displayed here are mean values across applications.