www.its.berkeley.edu/volvocenter environmental impacts of e-bikes in chinese cities baq 2006...

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www.its.berkeley.edu/volvocent Environmental Impacts of E- bikes in Chinese Cities BAQ 2006 Sub-workshop 16: Tailpipe Emissions from 2-3 Wheelers December 14, 2006 Christopher R. Cherry PhD Candidate Institute of Transportation Studies University of California, Berkeley Jonathan Weinert PhD Candidate Institute of Transportation Studies University of California, Davis Chaktan Ma Graduate Researcher Institute of Transportation Engineering Tsinghua University Partnership with: Pan Haixiao-Tongji University Xiong Jian-Kunming University of Science a Technology Yang Xinmiao-Tsinghua University

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www.its.berkeley.edu/volvocenter

Environmental Impacts of E-bikes in Chinese Cities

BAQ 2006Sub-workshop 16: Tailpipe Emissions from 2-3 WheelersDecember 14, 2006

Christopher R. CherryPhD CandidateInstitute of Transportation StudiesUniversity of California, Berkeley

Jonathan WeinertPhD CandidateInstitute of Transportation StudiesUniversity of California, Davis

Chaktan MaGraduate ResearcherInstitute of Transportation EngineeringTsinghua University

Partnership with: Pan Haixiao-Tongji University Xiong Jian-Kunming University of Science and Technology Yang Xinmiao-Tsinghua University

www.its.berkeley.edu/volvocenter

Outline

• Brief Introduction

• Research Objective

• Approach, Methodology, Data

• Results

• Future Research

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Emergence of Electric Two-Wheelers in large Chinese Cities

Most large Chinese cities have banned or heavily restricted gasoline motorcycles in the city center. In response, electric bicycles and scooters that can ride in the bike lane have gained popularity and mode share.

0

2,000,000

4,000,000

6,000,000

8,000,000

10,000,000

12,000,000

Pro

duct

ion (unit) .

E-bikes

All Autos

Personal Cars

Sources: Jamerson (2004) LuYuan Electric Bike Company (2006), Yu (2004), China Statistical Yearbook (2005)

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Emergence of Electric Bicycles in large Chinese Cities

• Several cities have (attempted) bans on e-bikes– Guangzhou, Beijing, Fuzhou

• What are the effects of these bikes on the transportation system? – Environmental implications

• Energy use and emissions– -Production and Use

• Hazardous Waste-Lead Acid Batteries

– Safety of electric bikes and others in lanes– Congestion– Increased mobility and accessibility

• Compared to what modes?

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Research Objective-Approach

• Identify Life-cycle environmental impacts of e-bikes in Chinese cities (production, use, disposal)– Energy– Emissions

• Compared to what modes? Bus and Bike

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Environmental Impacts-Production

• Production Energy Use and Emissions

– Raw Materials – Energy intensities

and emission intensities from raw material production

– Assembly Processes

– Assumes 5 batteries over lifespan, and 3 sets of tires (10 year lifespan)

Sources: China statistical yearbook (2004, 2005), China industrial yearbook (2004), China Data Online, Mao et al. (2006), Price et al. (2001)

TABLE 1: Material Inventory, Emissions and Energy Use

Associated Energy and Emissions of Manufacturing Processes

BSEB SSEB

Energy Use (tonne SCE) 0.178 0.260

Energy Use (kWh) 1449 2117

Greenhouse Gas (Tonne CO2eq) 0.599 0.865

Air Pollution (SO2) (kg) 1.561 2.194

Air Pollution (PM) (kg) 5.817 8.158

Waste Water (kg) 1486 2086

Solid Waste (kg) 4.457 7.127

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Environmental Impacts-Use • SSEB E-bike Energy Use

1.3kWh/100km– 6.6% electricity transmission loss (national

average), 6.1% in-plant electricity use– 50,000 km life=735kWh=0.09 tonne SCE

• Emissions from Electricity Production– Kunming1: 52% hydro, 48% coal– Shanghai: 2% hydro, 98% coal– All China: 15% hydro, 75% coal, 8% gas,

2% nuclear

1. China Statistical Yearbook 2005, Energy Foundation China 2005

Electric bike Emissions (g km-1)

Kunming Shanghai All China

SO2 0.076 0.156 0.119

NOX 0.017 0.035 0.027

PM 0.004 0.008 0.006

CO2 6.961 14.342 11.474

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Environmental Impacts-Lead • Battery Pollution

– 95% of electric bikes use lead acid batteries – Lead batteries last about 300 recharges or 1-2 years (10,000 km)– China Lead Acid Battery Recycling/Loss Rates1

• 4.8% Loss Rate During Manufacture• 27.5% Loss Rate During Mining, Smeltering and Recycling• 62% Recycling Rate

– 36V (10.3kg), 48V (14.7kg) lead content– 36V-3.214 kg lost during manufacture, 3.914 kg lost due to low recycle rate– 48V-4.689 kg lost during manufacture, 5.586 kg lost due to low recycling rate

• Electric bikes indirectly emit 712-1028 mg/km into environment!• If 100% recycled, still 321-469mg/km into environment

– For Sake of Comparison-in the USA: • 4% loss from virgin production, 2% from recycling and 1% from manufacturing• A 7.9L/100km (30mpg) car running on leaded fuel emits 33mg/km

1Mao et al. (2006) 2Lave et al.(1995)

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Lifecycle Impacts Figure 4: Life Cycle Energy and Emissions-SSEB

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10%

20%

30%

40%

50%

60%

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80%

90%

100%

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0.37 1.53 8.20 8.75 2234 38.87 50.67

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What Are E-biker’s Alternatives? • The net environmental impacts are relative

to the next best alternatives.– 3 E-bike surveys conducted in Spring 2006

• Shanghai, Kunming, Shijiazhuang

– Vast majority of respondents would shift to bus or bicycle if e-bikes banned

– Bicycles are most benign-zero use emissions and low production emissions

– Buses are big polluters, but also big people movers

Image source: Cervero (2005)

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Bus Emissions Comparative Emissions of Chinese Buses and E-bikes

Use Phase Only Full Lifecycle

Bus 1

(g km-1)Bus

(g pax-1 km-1)

SSEB(all China)

(g pax-1 km-1)

SSEB(all China)

(g pax-1 km-1 )

CO 7.97 0.159 Unknown Unknown

CO2 1275 25.49 11.47 30.60

HC 0.728 0.015 Unknown Unknown

NOX 13.51 0.270 0.027 Unknown

SO2 0.073 0.0015 0.119 0.164

PM 0.769 0.015 0.006 0.175

Lead (Pb) 0.248 0.005 0.862 0.862

• Majority of E-bike environmental impact during production phase

• Majority of Bus impact during use phase

1 Air Resources Board (2001, 2002), Nylund and Erkkila (2005), Embarq (2006)

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Other Impacts of E-bikes• Other impacts:

– contribution to congestion?• Are e-bikes any worse than bicycles?

– safety?• Crash/fatality rate much lower than cars, slightly higher than

bicycles

– mobility and accessibility?• Buses cannot provide equal levels of personal mobility in Chinese

cities-access and egress lost time

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Job Accessibility in Kunming-20 Min

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Conclusions• Rather than ban e-bikes, target regulation toward

problematic areas– Lead battery tax=“pull” industry toward better batteries

• E-bikes in infancy and performance will improve– Need predictable standards/regulation for industry to invest in R&D– Longer lifespan and better technology

• Could delay car ownership• Must consider benefits of e-bikes in policy analysis• Some things e-bike industry cannot fix

– Electricity production industry– Raw material production industries (lead and steel)

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Future Work• Public Health Effects of Local vs. Regional Emissions• Investigate Full Life Cycle of Alternative Modes• Identify Regional Impact of E-bike Use and Project Future

Technologies (battery, power plant) and Impacts• Investigate Other Externalities

– Safety– Congestion– Accessibility

• Questions?• Contact: [email protected]

www.ce.berkeley.edu/~cherry