TABLE C-1 Heavy-Duty On-Road Vehicles
|
Model Year |
Requirement |
Result |
EPA |
|
|
Model Year |
Comparison with California |
|||
|
1999 |
Carl Moyer Program |
Incentive program to reduce NOx and PM emissions (funded 7,000 projects to date) |
— |
EPA has no comparable program |
|
2000 |
School bus program |
Incentive program to retrofit or purchase improved buses (3,475 buses improved) |
2004 |
Federal enforcement settlement with Toyota provided funding for retrofit of school buses |
|
2004 |
Vehicle computer software upgrade |
Required 1993-1999 trucks to modify software to reduce excessive NOx emissions |
— |
EPA has no comparable program |
|
2004 |
Particulate filters on refuse trucks |
Reduced PM by up to 85% in residential neighborhoods |
— |
EPA has no comparable program |
|
2005 |
Additional test procedures for certification |
Reduce potential of excessive emissions during real-world driving |
2007 |
Adopted a similar program (2 years later) |
|
2007 |
First diagnostic system |
Identifies failed emission control parts |
— |
EPA has no comparable program |
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OCR for page 326
State and Federal Standards for Mobile-Source Emissions
Appendix C
Summary of Milestones in CARB Mobile-Source Emissions Regulations and Comparison with EPA
TABLE C-1 Heavy-Duty On-Road Vehicles
Model Year
Requirement
Result
EPA
Model Year
Comparison with California
1999
Carl Moyer Program
Incentive program to reduce NOx and PM emissions (funded 7,000 projects to date)
—
EPA has no comparable program
2000
School bus program
Incentive program to retrofit or purchase improved buses (3,475 buses improved)
2004
Federal enforcement settlement with Toyota provided funding for retrofit of school buses
2004
Vehicle computer software upgrade
Required 1993-1999 trucks to modify software to reduce excessive NOx emissions
—
EPA has no comparable program
2004
Particulate filters on refuse trucks
Reduced PM by up to 85% in residential neighborhoods
—
EPA has no comparable program
2005
Additional test procedures for certification
Reduce potential of excessive emissions during real-world driving
2007
Adopted a similar program (2 years later)
2007
First diagnostic system
Identifies failed emission control parts
—
EPA has no comparable program
OCR for page 326
State and Federal Standards for Mobile-Source Emissions
TABLE C-2 Small Off-Road and Utility Engines
Model Year
Requirement
Result
EPA
Model Year
Comparison with California
1995
First small off-road engine emission standards
Improved engine design reduced emissions 30-70%
1997
EPA adopted similar program (2 years later)
2000
First small off-road engine durability requirement
Use of catalysts, advanced two-stroke design and increased use of four-stroke engines for handheld equipment. Improved engine technologies for non-handheld equipment
2001
EPA adopted similar program (1 year later)
2005
California aligned with federal standards
Improved engine design and requirements similar in all 50 states for engines smaller than 50 cc
2005
Initiated at the federal level first and then adopted by CARB
2006
First small off-road engine evaporative emission requirements
Low fuel permeation fuel tank and fuel lines and use of carbon canister
—
Federal standards in development
2007-2008
HC and NOx standards reduced for engines greater than 80 cc in displacement
Emissions reduced by 33-38% using catalyst
—
Federal standards in development
OCR for page 326
State and Federal Standards for Mobile-Source Emissions
TABLE C-3 Off-Road Diesel Engines
Model Year
Requirement
Result
EPA
Model Year
Comparison with California
1996
First emission standards for engines over 175 hp (130 kW)
Improved engine design technologies
1996
Adopted California requirements from 50-175 hp (37-130 kW)
1999
Carl Moyer Program
Incentive program to reduce NOx and PM (as noted earlier 7,000 projects to date)
—
EPA has no comparable program
2000
Agreement with manufacturers to align California and federal standards
Similar requirements in all 50 states
—
EPA and CARB standards aligned
TABLE C-4 Recreational Marine Engines
Model Year
Requirement
Result
EPA
Model Year
Comparison with California
2001
Set Tier 1 outboard marine and personal watercraft engines
Improved engine technologies reducing HC and NOx emissions by 75% from uncontrolled
2006
EPA adopted similar requirements but will not fully match California until 2006 (5 years later)
2003
Tier 1 standard for inboard and sterndrive marine engines
Improved engine technologies with minor emission reductions
—
EPA has no comparable requirement but notice of advanced rulemaking issued in 2002
2004
Tier 2 outboard marine and personal watercraft engines
Improved engine design resulting in 80% HC and NOx emission reductions compared to uncontrolled
—
EPA has no comparable requirement
OCR for page 326
State and Federal Standards for Mobile-Source Emissions
Model Year
Requirement
Result
EPA
Model Year
Comparison with California
2007
Tier 2 inboard and stern drive marine engine requirements
Use of catalysts producing 67% emission reduction compared with uncontrolled
—
EPA has no comparable requirements but notice of advanced rulemaking issued in 2002
2008
Tier 3 outboard and personal watercraft engine requirements
Increases use of four-stroke engines and use of direct injection two-stroke engines
—
EPA has no comparable requirements
TABLE C-5 Fuels and Vapor Recovery
Model Year
Requirement
Result
EPA
Model Year
Comparison with California
1971
Fuel volatility limit of 9 RVP during ozone season
Large evaporative emission reductions
1989
EPA adopted similar program (18 years later)
—
—
—
1974
Federal regulations required large service stations to sell unleaded gasoline nationwide
1976
Stage 1 and Stage 2 vapor recovery required (transfer from cargo to service station and transfer to vehicle respectively)
Evaporative emission reductions
1990
Clean Air Act amendments of 1990 set similar requirements in non-attainment areas outside of California
1992
Phase 1 of cleaner burning gasoline
Full phase-out of lead, deposit control additives, RVP of 7.8, and wintertime oxygenates
1992
EPA adopted a partial program at the same time
OCR for page 326
State and Federal Standards for Mobile-Source Emissions
Model Year
Requirement
Result
EPA
Model Year
Comparison with California
1993
Cleaner burning diesel fuel
Sulfur content limit of 500 ppmw and aromatic hydrocarbon limit of 10% by volume (20% for smaller refiners)
1993
EPA adopted a partial program at the same time
1996
Phase 2 of clean burning gasoline
Control of 8 major fuel properties: RVP 7.0 cap in ozone season, oxygenates, benzene limits, aromatic limits, olefin limits, sulfur limits, and 50% and 90% distillation limits
2000
EPA adopted a partial program 4 years later
2001
Enhanced Stage 1 vapor recovery (98% capture efficiency)
VOC emissions reduced
—
EPA has no similar requirement but many states have adopted the California requirement
2003
Phase 2 vapor recovery must be compatible with ORVR systems on vehicles
Improves nozzle design or processor to minimize tank pressure
—
EPA has no similar requirement but many states are adopting California requirement
2006
Reduce sulfur in diesel fuel to 15 ppmw
Enables the use of advanced after-treatment devices to meet 2007 heavy-duty vehicle requirements
2006
EPA adopted 1 year before California but not applied to nonroad sources until 2010, not to stationary sources, and no aromatic hydrocarbon limit
All tables adapted from CARB, unpublished material, 2005.