Well-to-Wheels Energy and Emissions Impacts of - GREET Model

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Well-to-Wheels Energy and Emission Impacts of Vehicle/Fuel Systems Development and Applications of the GREET Model Michael Wang Center for Transportation Research Argonne National Laboratory California Air Resources Board Sacramento, CA, April 14, 2003

Transcript of Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Page 1: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Well-to-Wheels Energy and Emission Impacts of Vehicle/Fuel Systems

Development and Applications of the GREET Model

Michael WangCenter for Transportation Research

Argonne National Laboratory

California Air Resources BoardSacramento, CA, April 14, 2003

Page 2: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Vehicle and Fuel Cycles:Petroleum-Based Fuels

Vehicle Cycle

Fuel Cycle

Well to Pump

Pump to W

heels

Page 3: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

WTW Analysis Is a Complete Energy/Emissions Comparison

As an example, greenhouse gases are illustrated here

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Methan

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Cell Veh

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Eelectr

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H2 FCV (E

lectro

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Pump to Wheels Well to Pump

Page 4: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

WTW Analysis for Vehicle/Fuel Systems Has Been Evolved in the Past 20 Years

Historically, evaluation of vehicle/fuel systems from wells to wheels (WTW) was called fuel-cycle analysisPioneer transportation WTW analyses began in 1980s

Early studies were motivated primarily by EVsCurrent studies are motivated primarily by FCVs

Transportation WTW analyses have taken two general approachesLife-cycle analysis of consumer productsTransportation fuel-cycle analysisMost transportation studies have followed the fuel-cycle analysis approach

For transportation technologies, especially internal combustion engine technologies, the significant energy and emissions effects occur in the fuel usage stage first and fuel production stage secondConsequently, efforts have been in addressing energy use and emissions of vehicle operations and fuel productionSince 1995, the U.S. Department of Energy has been supporting the GREET model development at Argonne National Laboratory

Page 5: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

The GREET (Greenhouse gases, Regulated Emissions, and Energy use in Transportation) Model

GREET includes emissions of greenhouse gasesCO2, CH4, and N2O VOC, CO, and NOx as optional GHGs

GREET estimates emissions of five criteria pollutantsTotal and urban separately VOC, CO, NOx, Sox, and PM10 (PM2.5 not included)

GREET separates energy use intoAll energy sources Fossil fuels (petroleum, natural gas, and coal)Petroleum

Page 6: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

The GREET Model and Its Documents Are Available at: http://greet.anl.gov

Page 7: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

At Present, There Are More Than 790 GREET Registered Users Worldwide

Consulting Environ OrganizationGovernment IndustryOthers University

Industries, universities, and governmental agencies are major GREET users

Asia North AmericaEurope Other

Most GREET users are in North America

Page 8: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

The Simplified Calculation Logic for Individual Production Activities in GREET

InputsEmissionFactors

CombustionTech. Shares

EnergyEfficiencies

FacilityLocation Shares

Fuel TypeShares

Energy Use byFuel Type

TotalEmissions

UrbanEmissions

Calculations

Page 9: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

The Simplified Calculation Logic for Individual Transportation Activities in GREET

Energy Intensity (Btu/ton-mile)

Energy Intensity (Btu/ton-mile)

Transport Distance (mi.)

Transport Distance (mi.)

Energy Consumption (Btu/mmBtu Fuel Transported)

Emission Factors(g/mmBtu fuel burned)

Emission Factors(g/mmBtu fuel burned)

Share of Process Fuels

Emissions by Mode (g/mmBtu Fuel Transported)

Mode ShareMode Share

Energy Use by Mode (Btu/mmBtu Fuel Transported)

Emissions (g/mmBtu Fuel Transported)

Page 10: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

GREET Considers Upn Well-to-Pump Steps Through Iteration Calculations

FeedstockRecovery

Fuel Production

Vehicle Operation

FeedstockRecovery

Fuel Production

FeedstockRecovery

Fuel Production

n = 1n = 2n = 3

Page 11: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

GREET Is Designed to Conduct Stochastic Simulations

Distribution-Based Inputs Generate Distribution-Based Outputs

Page 12: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

GREET Has More Than 30 Fuel Pathway Groups

Petroleum

Conv. & Reform. Gasoline

Conv. & Reform. DieselLiquefied Petroleum Gas

Compressed Natural Gas

Liquefied Natural GasDimethyl Ether

MethanolFT Diesel and NaphthaNatural Gas

Gaseous and Liquid H2

Ethanol

Biodiesel

CornCellulosic Biomass

SoybeanVarious Sources Electricity

Flared Gas

Landfill Gas

Crude Naphtha

Liquefied Petroleum Gas

Liquefied Natural GasDimethyl EtherFT Diesel and Naphtha

MethanolGaseous and Liquid H2

Methanol

Electricity Gaseous and Liquid H2

Page 13: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Some Additional Fuel Production Pathways Are to Be Added to GREET

Biomass gasification to produceEthanolMethanolHydrogen

Coal gasification to produce hydrogenHydrogen production from ethanol and methanol at refueling stationsNuclear thermal cracking of water for hydrogen productionSodium borohydride (NaBH4) H2 production and storageMetal hydride hydrogen storage

Page 14: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Two ANL WTW Publications Are Cited by Many Organizations

Page 15: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Petroleum Refining Is the Key Energy Conversion Step for Gasoline

Petroleum Recovery (97%)

Gasoline at Refueling Stations

Petroleum Transportand Storage (99%)

Transport, Storage, and Distribution of Gasoline (99.5%)

MTBE or EtOH for Gasoline

WTP Overall Efficiency: 80%

Petroleum Refining to Gasoline (84.5-86%, Depending on Oxygenates and Reformulation)

Petroleum Refining to Gasoline (84.5-86%, Depending on Oxygenates and Reformulation)

Page 16: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Key Issues for Simulating Petroleum Fuels

Gasoline sulfur content will be reduced nationwide to 30 ppm beginning in 2004 vs. 150-300 ppm current levelDiesel sulfur content will be reduced to 15 ppm in 2006 from the current level of ~300 ppmIn addition, marginal crude has high sulfur contentDesulfurization in petroleum refineries adds stress on refinery energy use and emissionsEthanol could replace MTBE as gasoline oxygenate

Energy and emission differences between ethanol and MTBEProduction of gasoline blend stock for ethanol vs. MTBE

Page 17: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Production and Compression Are Key Steps for Centralized G.H2 Pathways

NA NG Recovery (97.5%)

Compressed G.H2 at Refueling Stations

LNG Gasification in Ports

LNG Production (88.0%)LNG Production (88.0%)

LNG Transport via Ocean Tankers 98.5%)

G.H2 Transport via Pipelines (96.3%)

nNA NG Recovery (97.5%)WTP Overall Efficiency: NA NG: 58%nNA NG: 55%

Steam or Electricity Export

NA: North American nNA: non-North AmericanNG: natural gas

G.H2 Compression at Refueling Stations (89.5% & 95.0% for NG & Electric)

G.H2 Compression at Refueling Stations (89.5% & 95.0% for NG & Electric)

G.H2 Production (71.5%) G.H2 Production (71.5%)

NA NG Processing (97.5%)

nNA NG Processing 97.5%)

NG Transport via pipelines

Page 18: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

H2 Liquefaction Has Higher Energy Losses Than H2 Compression

NA NG Recovery (97.5%)

NA NG Processing (97.5%)

L. H2 at Refueling Stations

L.H2 Transport via Ocean Tankers (96.9%)

L.H2 Transport (98.9%)

nNA NG Recovery (97.5%)

nNA NG Processing (97.5%)

H2 Liquefaction (71.0%)

H2 Liquefaction (71.0%)G.H2 production

(71.5%)G.H2 production

(71.5%)H2 Liquefaction

(71.0%)H2 Liquefaction

(71.0%)

G.H2 production (71.5%)

G.H2 production (71.5%)

WTP Overall Efficiency: NA NG: 43%nNA NG: 42%

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Resource and Infrastructure IssuesResult in Many Potential H2 Pathways

Produced from natural gas via steam methane reforming (SMR) now, and in the foreseeable futureSMR plant emissions need to be taken into accountRegional or station SMR production

Could reduce or avoid expensive distribution infrastructure But production emissions move close to urban areas

Some amount of central SMR CO2 emissions can be potentially sequesteredEnergy and emission effects of electrolysis H2 depend on electricity sourcesGasification for H2 production

Coal: CO2 and criteria pollutant emissions, but CO2 can be potentially sequesteredBiomass: criteria pollutant emissions

Nuclear H2 has zero air emissions, but nuclear waste will continue to be an issue

Page 20: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

WTP Energy Losses Could Significantly Affect Efficiencies and GHG Emissions

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Page 21: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

GREET Includes More Than 50 Vehicle/Fuel Systems

Conventional Spark-Ignition Vehicles• Conventional gasoline, federal reformulated

gasoline, California reformulated gasoline• Compressed natural gas, liquefied natural

gas, and liquefied petroleum gas• Methanol and ethanol

Compression-Ignition Direct-Injection Hybrid Electric Vehicles: Grid-Independentand Connected• Conventional diesel, low sulfur diesel, dimethyl

ether, Fischer-Tropsch diesel, and biodiesel

Battery-Powered Electric Vehicles• U.S. generation mix• California generation mix• Northeast U.S. generation mix

Fuel Cell Vehicles• Gaseous hydrogen, liquid hydrogen, methanol,

federal reformulated gasoline, California reformulated gasoline, low sulfur diesel, ethanol, compressed natural gas, liquefied natural gas, liquefied petroleum gas, and naphtha

Spark-Ignition Hybrid Electric Vehicles: Grid-Independent and Connected• Conventional gasoline, federal

reformulated gasoline, California reformulated gasoline, methanol, and ethanol

• Compressed natural gas, liquefied natural gas, and liquefied petroleum gas

Compression-Ignition Direct-Injection Vehicles• Conventional diesel, low sulfur diesel,

dimethyl ether, Fischer-Tropsch diesel, and biodiesel Spark-Ignition Direct-Injection Vehicles

• Conventional gasoline, federal reformulated gasoline, and California reformulated gasoline

• Methanol and ethanol

Page 22: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

GREET Fuel Economy Ratios of Vehicle Technologies (Relative to GVs)

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Page 23: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Tailpipe Emissions Will Continue to DeclineTier 2 Standards (Fully in Effect in 2009, g/mi. for 100K miles)

NMOG CO NOxc PM HCHO Bin 10a,b 0.156/0.230 4.2/6.4 0.6 0.08 0.018/0.027 Bin 9a,b 0.090/0.180 4.2 0.3 0.06 0.018 Bin 8a 0.125/0.156 4.2 0.20 0.02 0.018 Bin 7 0.090 4.2 0.15 0.02 0.018 Bin 6 0.090 4.2 0.10 0.01 0.018 Bin 5 0.090 4.2 0.07 0.01 0.018 Bin 4 0.070 2.1 0.04 0.01 0.011 Bin 3 0.055 2.1 0.03 0.01 0.011 Bin 2 0.010 2.1 0.02 0.01 0.004 Bin 1 0.000 0.0 0.00 0.00 0.000 a The high values apply to HLDTs. The low values applied to cars and LLDTs. b Bins 10 and 9 will be eliminated at the end of 2006 model year for cars and LLDTs and at the end of 2008 model years for HLDTs. c Corporate average NOx standard will be 0.07 g/mi. and will be fully in place by 2009.

Page 24: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

GREET Takes These Steps to Estimate Vehicular Emissions

Emissions of VOC, CO, NOx, CH4, and PM10Baseline gasoline and diesel vehicles:

HC, CO, NOx and CH4 are estimated with EPA’s Mobile modelPM10 is estimated with EPA’s Part model

Advanced or alternative-fueled vehicles:Their emission change rates relative to GVs or DVs are estimated with testing results or engineering analysisTheir emission levels are calculated with the estimated emission change rates and baseline GV or DV emissions

SOx emissions for each vehicle type are calculated from sulfur contained in fuelsCO2 emissions for each vehicle type are estimated from carbon balanceN2O emissions are based on limited testing results; CARB and EPA efforts here will greatly reduce tailpipe N2O uncertainties

Page 25: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

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Natural gas feedstockCrude oil

feedstock

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Page 26: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

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Page 27: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

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Page 28: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

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Crude oil feedstock

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Page 29: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Per-Mile Urban In-Use VOC Emissions of Selected Vehicle/Fuel Systems

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Page 30: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Per-Mile Urban In-Use NOx Emissions of Selected Vehicle/Fuel Systems

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Page 31: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Comparison of Five Publicly Available WTW Studies

MIT: On the Road in 2020 (2000)GM, ANL, BP, ExxonMobil, and Shell (2001)Wang of ANL: Journal of Power Sources (2002)MIT: Update of the 2000 Study (2003)Rousseau of ANL: SAE 2003 Congress paper (2003)Studies available but not included in comparison

ADL study for DOE (2002)GM European WTW study (2002)

Studies to be available soonGM, ANL, ChevronTexaco, and Shell (2003)ANL SUV WTW study (2003)

Page 32: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Comparison of Five Recent WTW Studies: Energy Use Changes

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Page 33: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Comparison of Five Recent WTW Studies: GHG Emission Changes

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Page 34: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

ConclusionsWTW analysis becomes necessary when comparing vehicle technologies powered by different fuels

Advanced vehicle/fuel technologies could significantly reduce energy use and GHG emissions

Fuel pathways need to be carefully examined for achieving intended energy and emission benefits by advanced vehicle/fuel systems

For criteria pollutantsAs vehicle tailpipe emissions continue to decline, WTP emissions could become a significant share of total WTW emissions

To reduce vehicle-induced WTP emissions, fuel producers will need to be actively engaged

Page 35: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Limitations of the Current GREET Version

So far, PM emissions have been measured and regulated for PM10. PM2.5 and smaller-size PM are more damaging; relative differences between PM10 and PM2.5 could be very different among vehicle technologiesBlack carbon emissions’ contribution to GHG emissions could be potentially largeSecondary formation of PM emissions from NOx and SOx could be important ambient PM emission sourcesLack of adequate tailpipe N2O emission measurements for vehicles powered by different fuelsFuel consumption and GHG emissions of accessory power systems such as AC could be significant sources

Page 36: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

Outstanding Issues in WTW Analyses Need to Be Addressed Continuously

Multiple productsSystem expansion vs. allocation (GREET takes both)System expansion: allocation vs. attribution of effects

Technology advancement over timeCurrent vs. emerging technologies – leveling comparison fieldStatic snap shot vs. dynamic simulations of evolving technologies and market penetration over time

Dealing with uncertaintiesRisk assessment vs. sensitivity analysisRegional differences, e.g, CA vs. the rest of the U.S.

Trade-offs of impactsWTW results are better for identifying problems than for giving the answers

Page 37: Well-to-Wheels Energy and Emissions Impacts of - GREET Model

On-Going GREET Efforts

Adding new fuel pathwaysIntegrating GREET into EPA’s MOVES modelAssisting DOE in evaluating its vehicle technology portfolioDeveloping a fully functioning CA version?