Personal Air and Car Travel Personal Air and Car Travel just don - - PowerPoint PPT Presentation
Personal Air and Car Travel Personal Air and Car Travel just don - - PowerPoint PPT Presentation
Personal Air and Car Travel Personal Air and Car Travel just don t do it! t do it! just don Christian Brand Christian Brand Transport Studies Unit & Transport Studies Unit & Environmental Change Institute
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Outline of the next 20 minutes
1.
Motivation and aims
2.
Methodology: travel emissions profiling
3.
Case study: travel emissions profiles
4.
Insights for policy
5.
Conclusions and outlook
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- 1. Motivation and aims
n GHG emissions from personal travel 18% of total
UK domestic emissions, still rising
n Sharp increase in leisure air travel; becoming a habit n Surprisingly little known who is contributing to the
problem and what the emissions profile of the population is
n Lack of information at household and individual
levels on annual travel activity, international travel, all modes of travel
n This lack of information makes policy formulation
difficult
n Tough choices to be made: who affected? n
Travel emissions profiles
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- 2. Methodology: emissions profiling (1)
n Methodology to
measure, evaluate and analyse CO2eq
n 12-month period n Households,
individuals (including children >6yrs)
n Personal travel
(not business)
n Multiple
techniques
n Policy implications
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- 2. Case study
n
County of Oxfordshire
n
Household survey
n
Sample size of 456 individuals (20% response)
n
Good representation of pop
n
Urban vs. rural (4 types)
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- 3. Results: travel emissions profiles (1)
Base: all 456 individual responses Base: all 456 individual responses
Other 4.3% Air (method E, AIM=3) 70.2% Ferry (national) 0.5% Rail (national) 1.9% Taxi (national) 0.3% Bus & coach (national) 1.2% Motorcycle (method A) 0.3% Car (method A) 25.5%
Average per person: 5.2 tonnes of CO 2
eq per year
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- 3. Results: travel emissions profiles (2)
§ Highly unequal distribution of emissions § Large disparities between individuals and households § A few high emitters responsible for the lion’s share
5 10 15 20 25 30 35 40 45 50 1 26 51 76 101 126 151 176 201 226 251 276 301 326 351 376 401 426 451 Observations ranked by emissions level CO2eq,tot p.a. (tonnes) CO2 equivalent per person per year "Outlier" at 91 tonnes of CO 2
eq
Individual CO Individual CO2
2 eq eq emissions from all travel activity ranked by emissions totals
emissions from all travel activity ranked by emissions totals
5 10 15 20 25 30 35 40 45 50 1 26 51 76 101 126 151 176 Observations ranked by emissions level CO2eq,tot p.a. (tonnes) Large Urban - Individuals Medium Urban - Individuals Small Urban - Individuals Rural - Individuals
Individual CO Individual CO2
2 eq eq emissions from all travel activity by geographical area
emissions from all travel activity by geographical area Household CO Household CO2
2 eq eq emissions from car travel by geographical
emissions from car travel by geographical area area
5 10 15 20 1 6 11 16 21 26 31 36 41 46 51 56 61 Observations ranked by emissions level CO2eq,tot p.a. (thousands) Large Urban - Households Medium Urban - Households Small Urban - Households Rural - Households 10,000 20,000 30,000 40,000 50,000 60,000 70,000 80,000 1 6 11 16 21 26 31 36 41 46 51 56 61 66 71 76 81 86 91 Observations ranked by emissions level kg CO2eq,tot p.a. Large Urban - Households Medium Urban - Households Small Urban - Households Rural - Households One "outlier" at 93 tCO2eq
Household CO Household CO2
2 eq eq emissions from air travel by geographical
emissions from air travel by geographical area area
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- 3. Results: travel emissions profiles (3)
§ Top 20% responsible for 61% of emissions (average 16 tonnes CO2
eq)
§ ‘High-over-Low factor’ of 90 (all modes of travel)
0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100% Car (A) Motorcycle (A) Bus & coach (Nat.) Taxi (Nat.) Rail (Nat.) Ferry Air (E, central) All modes Shares of modal CO2eq,tot totals Highest emissions quintile 4th emissions quintile 3rd emissions quintile 2nd emissions quintile Lowest emissions quintile
Bases: 266 (car), 12 (motorcycle), 313 (bus & coach), 210 (taxi) Bases: 266 (car), 12 (motorcycle), 313 (bus & coach), 210 (taxi), 239 (rail), 68 (ferry), 269 (air) , 239 (rail), 68 (ferry), 269 (air)
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- 3. Results: travel emissions profiles (4)
n CO2 eq emissions are mainly influenced by income, age,
working status, car availability, household composition and size
n Overall weak or non-existent correlation with household
location, accessibility and gender
n Top 10% typically in their 30s and 40s, in full- or part-time
work and earning £30,000 p.a. or more
n Bottom 10% typically women, children or residents older
than 75 years, not economically active, non-car drivers and
- n low income of less than £10,000 p.a.
n Some variation cannot be explained by this analysis –
lifestyles, attitudes better to explain behaviour?
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E N D S r e p
- r
t , F e b ‘ 7
- 4. Policy implications (1)
The Guardian, March 2007
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- 4. Policy implications (2)
n Focus on personal air (and car) travel n Policy should target high emitters – but how
effectively?
n Moderate tax rises unlikely to curb growth in carbon
emissions
n Cap-and-trading of personal carbon (travel +
household energy) may be better to change behaviour.
n Would challenge the highest emitters: top 10% of
population may use up any in a couple of months
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- 5. Conclusions and outlook
n Personal Air and Car Travel – some of us ‘do it every day’ n Unequal distribution amongst the population – 20/60 rule? n Socio-economic and other factors can explain some of the
variation in emissions, but not all
n Travel emissions profiling as a tool for:
q Carbon measurement and monitoring q Awareness raising and feedback
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Further information
n Reports on the study at
www.tsu.ox.ac.uk/research/oxontravel
n Web-based survey still viewable
(guest login: “oxontravel”, password: “onthemove”)
n Contact details
Christian Brand, University of Oxford christian.brand@ouce.ox.ac.uk
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- 2. Methodology: emissions profiling (2)
Household and individuals
n
HH size and structure, incomes, occupation, age, gender, vehicle ownership
n
Accessibility to key services and public transport
Primary data collection in surveys – lots and lots and lots...
Private vehicle information
n
Make, model, age, fuel type, engine size
n
Annual vehicle mileage
n
Road type, trip distances
n
Shared use within HH
n
Fuel purchases and use Air travel
n
Origin, destination, stopovers
n
Duration estimate
n
Occupancy estimate Cycling, walking, bus, taxi, rail, ferry
n
Day-to-day travel (e.g. commuting) – peak/off-peak
n
Casual travel (e.g. holidays, visiting friends)
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- 2. Methodology: emissions profiling (3)
50 100 150 200 250 300
- 2,000
4,000 6,000 8,000 10,000 12,000 flight distance (no detour penalty) gCO2
dir or fuel per passenger-km
0.0 0.2 0.4 0.6 0.8 1.0 1.2 1.4 g [other pollutants] per passenger-km CO2 short haul (g/pkm) CO2 long haul (g/pkm) Fuel short haul (g/pkm) Fuel long haul (g/pkm) NOX short haul (g/pkm) NOX long haul (g/pkm) CO short haul (g/pkm) CO long haul (g/pkm)
Air distance-emissions curves for fuel use and various pollutants used in air travel model
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- 3. Results: travel emissions profiles
n
Air and car travel dominate overall carbon emissions
n
Emissions from public transport very small
n
Highly unequal distribution of emissions
n
‘Hockey-stick’ shape of emissions ranking curves remarkably similar for different units of analysis, geographical location, modes
- f travel, …
n
Large disparities between individuals and households: some 20% of the respondents drove but did not fly although the same number flew but did not drive
n
Top 10% of emitters responsible for 43% of emissions and the bottom 10% for only 1%
n
Higher emissions of urban population (due to higher propensity to travel by air?)
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- 3. Results: travel emissions profiles (5)
0% 10% 20% 30% 40% 50% 60% 70% 80% 90% 100% Second emissions quintile Third emissions quintile Fourth emissions quintile Highest emissions quintile
emissions quintile shares of all respondents in each income group
Highest income group £30-40k £20-30k £10-20k Lowest income group
§ Example: highly significant disproportionality between CO2
eq