transportation energy –what is best?

60
Transportation Energy – What is Best? Mark Delucchi Research Scientist Transportation Sustainability Research Center Institute of Transportation Studies University of California, Berkeley IEE Seminar UC Santa Barbara April 27, 2017

Upload: others

Post on 03-Dec-2021

3 views

Category:

Documents


0 download

TRANSCRIPT

Transportation Energy – What is Best?

Mark DelucchiResearch Scientist

Transportation Sustainability Research CenterInstitute of Transportation StudiesUniversity of California, Berkeley

IEE SeminarUC Santa Barbara

April 27, 2017

Outline

• What I mean by “best?”• What do we care about – what are we trying to fix?

– Some external costs in the US– Global trends in air pollution, water use, nutrient discharge, biodiversity

• Qualitative evaluation of solutions to transport problems• Quantitative comparison of some alternatives for LDVs

– Water consumption of alternative-fuel LDVs– Land use of alternative-fuel vehicles– CO2-equivalent lifecycle GHGs from biofuel LDVs– Social lifetime cost of alternative-fuel LDVs

• Comments on other modes• The context for considering solutions

– The changing energy context– The radically changing social context

• What are the important research questions?• Summary and conclusions

What do we – I – mean by “best?”

• Qualitatively: maximize the potential for long-term human welfare, with an emphasis on the well-being of the least well-off and on the sustainability of all earth’s ecosystems – at least (or acceptable) cost

• Consider a wide range of evaluation criteria

• This is not necessarily the same as maximizing net benefits in a traditional social-cost benefit analysis:

– Takes a longer term view, with low (near-zero) “discount rate”– Does not trade-off rich-person “amenity” values with impacts on human health,

education, and basic opportunity

Measuring the problems: external costs of motor-vehicle use, U.S., 1990 (109 1991 $)

Cost item Low High Q

Accidental pain, suffering, and death 30 120 A3, D

Travel delay, imposed by other drivers that displaces unpaid activities 35 140 A2

Air pollution: human health impacts from motor-vehicle emissions 19.3 283 A1

Air pollution: human health impacts from upstream emissions, road dust 5.3 167 A1

Air pollution: damages to visibility, crops, materials, and forests 7.8 50.9 B-A1

Climate change due to fuel-cycle emissions of GHGs (U. S. /global damages) 0.0 /2.4 3.5 /25.2 A1, B

Noise from motor vehicles 0.5 15 A1

Water pollution: oils spills, fuel leaks, urban runoff, road de-icing 2.8 7.3 C,D

Expected loss of GNP due to sudden changes in the price of oil 1.6 25 C [A1]

Pecuniary cost increased payments to foreign countries for non-transport oil 4.0 8.4 A3

Strategic Petroleum Reserve, military expenditures related to oil use 0.7 8.0 A3

Source: estimates for entire in-use highway fleet in 1990 from Delucchi (2008). SCC is $1-$10 metric-tonne-CO2e for global damages, $0-1.40 US.Q = qaulity of the estimate.

MV external costs in the US: the business-as-usual future

Recent past Future

VMT Per mile Exposure, Effects Unit Value

Accidents é é? ê êê* − ê − ê é é

Congestion é é? − − − − é é

Air pollution é é? ê ê é é é é

Climate change é é? − ê é é é^ é^

Energy use é é? − ê é é é é

Noise é é? − − ? ? é é

*With widespread vehicle automation. ^Improved methods have increased SCC by an order of magnitude

Average emission rate of gasoline+diesel vehicle fleet, US

Source: BTS (2017g).

0.00

5.00

10.00

15.00

20.00

25.00

30.00

35.00

40.00

45.00

50.00

1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010

gram

s/m

ile

Total HC

Exhaust CO

Exhaust NOx

PM2.5, NOx, highway vehicles and total, w.r.t 1990, US

Source: USEPA (2017b)

0.00

0.20

0.40

0.60

0.80

1.00

1.20Highway vehicles PM2.5All sources PM2.5Highway vehicles NOxAll sources NOx

Emissions of CO2-equivalent GHGs from transport, US

Source: Table 11.8 of Davis et al. (2016).

0

200

400

600

800

1000

1200

1400

Milli

on m

etric

tons

CO

2e

Passenger Vehicles

Heavy Trucks

Water

Air

Rail

Pipeline

Leaks from underground petroleum storage tanks: cumulative confirmed releases and cumulative releases not cleaned up

Source: 1990-2015 from BTS (2017d); 2016 from USEPA (2017a).

0

100,000

200,000

300,000

400,000

500,000

600,000

Federal fiscal year

Cumulative total confirmed releasesCumulative releases not cleaned up

Petroleum spills impacting navigable US waterways

Source: BTS (2017e). Note: 2010 is 207-million-gallon Deepwater Horizon blowout.

0

1,000,000

2,000,000

3,000,000

4,000,000

5,000,000

6,000,000

7,000,000

8,000,000

9,000,000

10,000,000

1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013 2014 2015

gallo

ns Total, all spills

Vessel sources, total

Highway noise barrier construction in the US

Source: BTS (2017f).

0

50

100

150

200

250

300

350

400

1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000 2001 2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013

mile

s or

milli

on $

Total length of barriers (miles)

Cost (million 2013 $)

Global trends in important indicators of air pollution, water use, nutrient

discharge, and biodiversity

HC and NOx emission stds for gasoline cars in OECD

Source: OECD (2012h).

0

1

2

3

4

5

6

1970 1975 1980 1985 1990 1995 2000 2005 2010

gram

s pe

r km

US HC all cars

US NOx

US HC+NOx all cars

JPN HC

JPN NOx

EUR HC

EUR NOx

EUR HC+NOx

PM2.5, NOx, mobile sources, w.r.t 1990, UK and Italy

Source: OECD (2015a).

0.00#

0.20#

0.40#

0.60#

0.80#

1.00#

1.20#

1.40#

1990# 1991# 1992# 1993# 1994# 1995# 1996# 1997# 1998# 1999# 2000# 2001# 2002# 2003# 2004# 2005# 2006# 2007# 2008# 2009# 2010# 2011# 2012#

PM2.5#road#transport,#United#Kingdom#

PM2.5#other#mobile#sources,#United#Kingdom#

NOx#road#transport,#United#Kingdom#

NOx#other#mobile#sources,#United#Kingdom#

PM2.5#road#transport,#Italy#

PM2.5#other#mobile#sources,#Italy#

NOx#road#transport,#Italy#

NOx#other#mobile#sources,#Italy#

SOx, NOx, and BC emissions by region

Source: OECD (2012i).

0

20

40

60

80

100

120

140

160

180

SO2 NOx BC SO2 NOx BC SO2 NOx BC

OECD BRIICS RoW

Emis

sion

s (in

dex

2010

= 1

00)

2010 2030 2050

SO2 NOx SO2 NOx SO2 NOx

Global premature deaths from some environmental risks

Source: OECD (2012j).

0.0 0.5 1.0 1.5 2.0 2.5 3.0 3.5 4.0

Particulate Matter

Ground-level ozone

Unsafe Water Supply and Sanitation*

Indoor Air Pollution

Malaria

Deaths (millions of people)

2010

2030

2050

Global mortality from fossil-fuel air-pollution in 2050

Country High Middle Low

India 1,667,221 805,227 195,433

China 1,380,050 638,165 148,273

Nigeria 984,287 514,900 132,376

Pakistan 361,391 180,243 44,816

Bangladesh 280,467 130,598 30,780

Russian Federation 225,543 102,559 23,534

Ethiopia 182,850 78,819 17,493

Sudan 151,527 72,899 17,302

United States of America 103,679 45,761 11,734

Egypt 89,901 41,491 10,136

Subtotal top 10 5,426,915 2,610,662 631,878

Total for 139 countries 7,376,181 3,487,163 838,205

Source: Jacobson, Delucchi et al. (2017).

Source: Wada and Bierkens (2014)

Nonrenewable/total groundwater use, 1960, 2010, 2099

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

India USA China Pakistan Iran Mexico Saudi Arabia

1960

2010

2099

Source: World Bank (2017a).

Renewable internal freshwater resource (m3/capita)

0

2000

4000

6000

8000

10000

12000

1997 1999 2001 2003 2005 2007 2009 2011 2013 2015

YEAR

High-income countries

Middle-income countriesLow-income countries

Global water demand 2000 and 2050

0

1 000

2 000

3 000

4 000

5 000

6 000

2000 2050 2000 2050 2000 2050 2000 2050

OECD BRIICS RoW World

Km

3

electricity manufacturing livestock domestic irrigation

Source: OECD (2012a). See also Byers et al. (2016) on water use of CCS.

People living in water-stressed river basins 2000 and 2050

Source: OECD (2012b). See also Mekonnen and Hoekstra (2016).

0

1 000

2 000

3 000

4 000

5 000

6 000

7 000

8 000

9 000

10 000 20

00

2050

BL

2050

RE

2000

2050

BL

2050

RE

2000

2050

BL

2050

RE

2000

2050

BL

2050

RE

OECD BRIICS RoW World

Mill

ions

of p

eopl

e

severe water stress medium water stress low water stress no water stress

Global agricultural area, various estimates, to 2050

Source: OECD (2012c).

30

35

40

45

50

55

60

65

70

1980 1990 2000 2010 2020 2030 2040 2050

Agric

ultu

ral a

rea

(milli

ons

of k

m2 )

FAO/IMAGE

IAASTD

MEA scenarios

Outlook Baseline

0 -

Source: World Bank (2017b).

Fertilizer consumption (kg per ha of arable land)

0

20

40

60

80

100

120

140

160

2002 2003 2004 2005 2006 2007 2008 2009 2010 2011 2012 2013

YEAR

High-income countries

Middle-income countries

Low-income countries

River discharges of nutrients into the sea, 1950 to 2050

Source: OECD (2012d).

0

2

4

6

8

10

12

14

16

Arctic Ocean Atlantic Ocean Indian Ocean Medit + Black Sea Pacific Ocean

Mill

ion

s o

f to

nn

es

of N

pe

r ye

ar

1950 1970 2000 2030 2050

Effects of different pressures on species abundance, 2010, 2030, 2050

MSA = means species abundance as a % of species in pristine ecosystems.

Source: OECD (2012e).

50%

60%

70%

80%

90%

100%

2010 2030 2050 2010 2030 2050 2010 2030 2050 2010 2030 2050

OECD BRIICS RoW World

MS

A

Infr+Encr+Frag

Climate Change

Nitrogen

Former Land-Use

Forestry

Pasture

Bioenergy

Food Crop

Remaining MSA 0"#

Global forest area change, to 2050

Source: OECD (2012f).

75

80

85

90

95

100

105

110

115

2010 2020 2030 2040 2050

Fo

rest

co

ver

(201

0 =

100

%)

Primary Forest OECD

Primary Forest BRIICS

Primary Forest RoW

Primary Forest World

Total Forest OECD

Total Forest BRIICS

Total Forest RoW

Total Forest World

Terrestrial species abundance per biome, to 2050

MSA=means species abundance as a % of species in pristine ecosystems.

Source: OECD (2012g).

Polar/Tundra

Grassland/Steppe

Scrubland/Savanna

Boreal forests

Temperate forests

Tropical forests

Hot desert

Total MSA

0

10

20

30

40

50

60

70

80

90

100

2000 2010 2020 2030 2050

Me

an

Sp

ec

ies

Ab

un

da

nc

e (

%)

Everything is pretty bad now

Most things will get worse

It is and will be especially bad in poorer countries

SUMMING UP THE PROBLEMS

Qualitative evaluation of solutions to transport problems

Criterion Best options Comments w.r.t. to energy

AccidentsVehicle automation, mode shift, traffic

separation, travel reduction, traffic control, behavior/licensing control, vehicle safety

technology, emergency response…

Compatible with all energy systems, but some minor advantages for electric-

drive systems

CongestionMode shift, automation, travel reduction, traffic

control, pricing, expanded infrastructure, supportive land-use planning…

Compatible with all energy systems, but some (very) minor advantages for

electric-drive systems

Air pollution Zero-emission modesNeed non-combustion power source:

electrification with zero-emission primary energy

Climatechange

Zero fossil-fuel use, zero negative land-use change worldwide

Prima facie electrification with zero-emission primary energy is good, but

what about bioenergy?

Oil use Zero oil use worldwide Electrification or biofuels

Noise Low-speed vehicles; non-combustion power sources Electric-drive systems

Water use Need formal evaluation of water intensity of energy options

Biodiversity Energy and infrastructure systems with minimal land footprint in important ecosystems

Need formal evaluation, but prima facie bioenergy is worst choice

Cost Need formal evaluation. Usually it is assumed that the zero-emission options that provide the greatest social and environmental benefits are too costly, but is this correct?

Quantitative comparison: water consumption of alternative-fuel vehicles

Fuel petrol FTD H2 H2 Elec. Elec. E85 biodiesel E85

Feedstock oil NG NG WWS US grid WWS irr. CS irr. soy nirr. CS

Vehicle ICEV ICEV FCV FCV BEV BEV ICEV ICEV ICEV

gal-H2O/mi 0.10 0.27 0.065 0.035 0.25 0.005 20 10 0.26

Notes: FTD = Fischer-Tropsch Diesel, H2 = hydrogen, Elec. = electricity, E85 = 85% ethanol, NG = natural gas, WWS = wind, water, or solar power, US grid = US average electricity mix, irr. = irrigated, nirr. = not irrigated, CS = corn stover.

Source: King and Webber (2008). See also Spang et al. (2014), and Byers et al. (2016) on water use of CCS.

Area to Power 100% of U.S. Onroad Vehicles

Cellulosic E85

4.7-35.4%of US

Geoth BEV0.006-0.008%

Solar PV-BEV0.077-0.18% of US

Slide contributed by Mark Z. Jacobson, Dept. of Civil & Environmental Engineering, Stanford University

Key features of the Lifecycle Emissions Model

• Includes alternative transportation fuels, material and vehicle lifecycles, infrastructure, HDVs, LDVs, bus and rail transit, small vehicles, electricity, heating and cooking fuels, and more

• Has international data for analysis of up to 30 different countries.• Projects energy use and emissions through 2050• Comprehensive accounting of biofuel lifecycles, including explicit

representation of the global nitrogen cycle and detailed treatment of changes in land use

• Detailed treatment of the CO2-equivalent impact (based on present-value of damages) of a wide range of long- and short-lived GHGs and pollutants including aerosols

• Can be used to model emissions impacts of complete passenger and freight transportation scenarios

• Has some rudimentary representations of price/economic effects

Quantitative comparison: CO2-equivalent lifecycle GHG emissions of alternative-fuel vehicles

CO2-equivalent lifecycle GHGs from biofuel LDVs

Source: From current beta version of the Lifecycle Emissions Mode (LEM); see Delucchi et al. (2003) for documentation of a prior version.

26 mpg LDV, US year 2040, g/mi and % ∆ vs. gasoline

Quantitative comparison of some alternatives: social lifetime cost of alternative-fuel vehicles

The Advanced-Vehicle Cost and Energy-Use Model (AVCEM)

A detailed, integrated model of vehicle design, energy use, manufacturing cost, lifetime operating cost, and external costs, for H2 and methanol fuel cell vehicles, pure battery EVs, hybrid EVs, and alternative fuel ICEVs

Calculation logic of AVCEM

The Advanced-Vehicle Cost and Energy-Use Model (AVCEM):

A detailed, integrated model of vehicle design, energy use, manufacturing cost, lifetime operating cost, and external costs, for H2 and methanol fuel cell vehicles, pure battery EV, hybrid EVs, and alternative fuel ICEVs.

Studies of the social cost of carbon

IAM = Integrated Assessment Model; SCC = social cost of carbon; n.r. = not reported; part. = partially. “Extreme climate impacts?” includes extreme climate sensitivity to emissions, irreversible impacts, high-cost/low-probability impacts, and potentially large but difficult to quantify damage categories. Note that here “low” and “high refer to values of the SCC itself, and not to the LCHB and HCLB scenarios established here.

Quantitative comparison: social lifetime cost, 2020Compact car, Li-ion battery, FUDS cycle (present value of costs)

Source: Current beta version of AVCEM; see Delucchi et al. (2000) for documentation of prior version.

Comments on other modes

• Heavy trucks (inferences from results for light trucks?)

• Trains – electrify

• Ships – electrify ports; batteries and fuel cells while traveling

• Airplanes – batteries short haul? LH2? Biofuels from waste?

THE CHANGING ENERGY CONTEXT

Source: World Bank (2017d).

Access to electricity (% of population)

0

10

20

30

40

50

60

70

80

90

100

1990 1992 1994 1996 1998 2000 2002 2004 2006 2008 2010 2012 2014 2016

YEAR

High-income countries

Middle-income countries

Low-income countries

Source: World Bank (2017e).

Primary energy use per GDP (MJ/$2011 PPP GDP)

0

2

4

6

8

10

12

14

16

18

1990 1992 1994 1996 1998 2000 2002 2004 2006 2008 2010 2012 2014 2016

YEAR

High-income countries

Middle-income countries

Low-income countries

Source: World Bank (2017c).

Electricity from renewables (excl. hydro) (% of total)

0

1

2

3

4

5

6

7

8

9

YEAR

High-income countries

Middle-income countries

LCOE of WWS vs. BAU (cents/kWh in 2050)

LCOE = levelized cost of electricity; WWS = wind, water, and solar power; BAU = business as usual; LCHB = low cost, high benefits; HCLB = high cost, low benefits; T&D = transmission and distribution. Year 2013 dollars. Discount rate is 1.5% (LCHB) or 4.5% (HCLB).

Source: M. Z. Jacobson, M. A. Delucchi, et al. (2015).

THE RADICALLY CHANGING SOCIAL CONTEXT

VMT vs. GDP, Drivers, Affordability

Sources: FHWA, BEA, BTS, and others. See Appendix A for details.

0.00

0.50

1.00

1.50

2.00

2.50

60 61 62 63 64 65 66 67 68 69 70 71 72 73 74 75 76 77 78 79 80 81 82 83 84 85 86 87 88 89 90 91 92 93 94 95 96 97 98 99 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15

w.r.t1990

YEAR

Personaldisposableincome(real)

GDP(real)

VMT-Allvehicles

VMT-LDVs

Vehiclesexcl.motorcycles

PMT-LDVs

Drivers/Pop.>16

LDVMTaffordability(milesper$fuel)

What’s going on? Younger generations like driving less and alternatives more

Source: National Association of Realtors and Portland State University (2015).

…are much less attached to having their own car…

Survey data presented by Susan Handy at the 2015 Asilomarconference indicate that:

• Millennials were driven around by their parents much more than were other generations

• Millennials were much less likely to get a driver’s license within a year of being eligible then were other generations (see next slide)

• Millennials have used Uber, Lyft, or other ride-sharing services much more than have other generations

Source: Handy (2015). See also Schwartz (2015).

Licensed drivers, % of age-group population, 1983-2014

Source: Sivak and Schoettle (2016).

Source: Handy (2015).

…less interested in buying a car…

...and more interested in living without being car-dependent

Source: National Association of Realtors and Portland State University (2015).

These travel trends are (partly) driven by underlying demographic and social changes

Source: Pew Research Center (2014).

Regarding those views on government…

Source: USA Today (2014).

Maybe at the bottom of this:

• New technologies and associated cultural norms allow people to socialize and build identities in ways less centered on automobiles

• Higher levels of education and increased exposure to diversity, combined with declining crime and pollution in cities, make high-density living more appealing

• Economic conditions combined with changes in social/sexual norms make it less imperative to pair-bond and procreate early, which extends the period of time that people can move and relocate more freely

• Early development of large social networks, extended periods of dependency on family, school, and social support systems, and increased exposure to other cultures increase acceptance of government role in providing infrastructure and services

• Social/cultural/economic context is changing– Underlying forces not likely to abate– Changes how we conceive of and evaluate potential solutions

• The development of land-based bioenergy exacerbates water-and land-use problems compared with the best land-management practices

• Zero-emission renewables have a bright future– Even 100% renewable energy in all sectors is technically and economically feasible

• Therefore: the set of solutions to evaluate should include bold visions of fully electrified transportation powered entirely by zero-emission electricity

IMPLICATIONS FOR THINKING ABOUT SOLUTIONS

So what are the important research questions?

• What are our objectives? What are our evaluation criteria?

• What will the future be like?

• What kind of solutions can we envision?

• The usual issues associated with modeling and evaluating solutions.

• Understanding international differences in constraints and opportunities

– In particular, how to minimize impacts and maximize welfare in poorer countries

Summary and conclusions

• Dramatic changes in values and technology provide a great opportunity to plan and develop new, sustainable energy, transportation, and land-use systems.

• Electrifying all transport, using the most sustainable primary energy sources (wind, water, and solar power), is the best solution to a wide range of social and environmental problems.

• Our research suggests that electrification probably does not cost (much) more than does a BAU scenario, but provides large benefits. Electrification also appears to have higher net benefits than do biofuels, except perhaps in aviation.

Wait – but what about “practicality,” you say?

This Modern World, Daily Kos, May 16, 2016, http://www.dailykos.com/blog/Tom%20Tomorrow

Well….we did go to the moon...

And more prosaically:

We didn’t get the interstate highway system by putting a tax on horse manure.

All things…Near or far,HiddenlyTo each other linked are,That thou canst not stir a flowerWithout troubling of a star

From ‘The Mistress of Vision’, by Francis Thompson

REFERENCES

Available from me.