Diesel Fuel Quality and Sulfur Effects on Catalyst-Based Exhaust Emission Controls: Manufacturers of Emission Controls Association May 2000.

Slides:



Advertisements
Similar presentations
Diesel Engine Technology 2007 and Beyond Diesel Engine Technology 2007 and Beyond Vice President, Chief Technical Officer International Truck and Engine.
Advertisements

Fuels and Emissions: Lessons Learned in the U.S. Lester Wyborny II U.S. Environmental Protection Agency Office of Transportation and Air Quality.
Robert Tekniepe Clark County Department of Air Quality and Environmental Management Air Quality Forum November 14, 2006 Clean Diesel Strategies.
EXHAUST GAS RECIRCULATION IN DIESEL ENGINE
Retrofit Emission Control Technologies for On-Road, Off-Road, and Stationary Diesel Engines Manufacturers of Emission Controls Association May 2000.
Reducing harmful emissions while protecting Fleet Investment.
Retrofit Emission Controls for On-Road Diesel Engines OCA Air Quality Summit Fresno, CA October 27, 2005 Manufacturers of Emission Controls Association.
Retrofit Emission Control Technologies for On- and Off-Road Diesel Engines Manufacturers of Emission Controls Association May 2002.
THE ROLE OF RETROFIT TECHNOLOGY IN REDUCING VEHICLE EMISSIONS MAY 2014 Dr RICHARD O’SULLIVAN COMMERCIAL DIRECTOR.
“Ceryx means Clean Air” The QuadCAT Four-Way Catalytic Converter An Integrated Emission Control System for Diesel Engines presented to the: February 3,
Experimental Evaluation of Various Biofuel-Diesel Blends as Diesel Engine Fuels Georgios Fontaras and Zissis Samaras Laboratory of Applied Thermodynamics.
,. CLEAN DIESEL DEMONSTRATION PROGRAM Diesel Emission Control Retrofit Users Conference Pasadena, CA February 6 -7, 2001.
California’s Experience: Air Quality Successes and Challenges Bart Croes, P.E. Chief, Air Quality Data Branch California Air Resources Board (CARB) April.
Swed Gov’t cost ben Summary (I) The proposed levels of sulphur in EU petrol for 2000 will make it difficult to further reduce automobile emissions.
1 Introduction of Clean Fuel to Vehicle Emission Reductions Integrated Vehicle Emission Reduction Strategy Workshop Jakarta, October 2001 Kiyoyuki.
Introduction and Overview Sub Workshop 4 Mobile Sources Better Air Quality 2002 Hong Kong December 16-18, 2002.
Impact of Fuel Sulfur on Vehicle Emissions Nazeer Bhore Fuels Development and Policy Planning ExxonMobil Refining and Supply Co. Fairfax, VA Latin.
2007 Program Update for ATA/TMC John Campbell 10 June 2003.
Transforming Transportation: Now and for the Future Jack Kitowski May 10, 2001 Air Resources Board California Environmental Protection Agency Air, Energy.
Performance and Emission Analysis on Oxygen Enriched variable
EPA Clean Diesel Engine Implementation Workshop Shirish Shimpi Cummins Inc. August 6-7, 2003.
The International Experience Europe Developing Road maps for Conventional Fuels in Asia Axel Friedrich Umweltbundesamt (UBA) Germany.
Nature of Air Pollution in California
Diesel Particulate Matter Emission Reduction Methods.
Reducing Emissions from Existing Trucks and Buses
Briefing on Recent Emission Control Developments May, 2000 Manufacturers of Emission Controls Association.
Sohail Ghanchi Energy Technology and Policy The University of Texas at Austin.
Tier 3 Vehicle and Fuel Standards: Final Rule National Tribal Forum on Air Quality May 21,
RETROFIT EMISSION CONTROL TECHNOLOGIES FOR HEAVY DUTY DIESEL ENGINES - THE STATE OF THE ART Sougato Chatterjee Johnson Matthey Catalysts BAQ 2004.
Cleaning Up Diesel in the Bay Area What Are the Sources? What are the Clean-Up Opportunities? Patricia Monahan Senior Analyst, Clean Vehicles Program.
EPA’s Proposal for Nonroad Diesel Engines & Fuel Bill Charmley, U.S. EPA Tri-Service Power Expo July 15, 2003.
Air Quality Management in Mumbai V.K.Phatak MMRDA.
TECHNICAL ISSUES OF INCREASED ETHANOL BLENDS Dr. Bruce Jones Director Minnesota Center for Automotive Research (MnCAR) Minnesota State University, Mankato.
Freeport Generating Project Project Description Modernization projects at Power Plant #2 Developers – Freeport Electric and Selected Development Company.
Expediting the Use of Clean-Diesel Engines with Retrofit Emission Control Technologies Air Quality Conference for Local Elected Officials May 10-11, 2001.
1 EPA’s Proposal for Nonroad Diesel Engines & Fuel May 2003 U.S. Environmental Protection Agency Office of Transportation and Air Quality Informal document.
Copies of Presentations Contact Info for Questions Workshop Q&A Document Later this Year.
Technology For 2007 And Beyond Dr. Steve Charlton Executive Director – Advanced Engineering Cummins Inc.
Clean Fuels and Vehicles: Importance for Urban Air Quality Katherine Buckley Air and Climate Program Manager U.S. Environmental Protection Agency
INGAS - Integrated GAS Powertrain Project number: Project number: DAIMLER AG INGAS 18 months meeting, Paris, 20./ InGas 18 months.
1 Meeting Air Quality Goals in California Nancy L. C. Steele, D.Env. The Tender Land November 6, 2004 California Environmental Protection Agency Air Resources.
T h e C h i n a S u s t a i n a b l e E n e r g y P r o g r a m 中 国 可 持 续 能 源 项 目 Advancing Cleaner Fuels in China Dongquan HE Ph.D. The Energy Foundation.
INGAS “24 Months Meeting ”, “Brussels, Belgium”, “27-28 October 2010” INGAS INtegrated GAS Powertrain 1 INGAS 24 months meeting Brussels - Belgium 27 -
California Environmental Protection Agency AIR RESOURCES BOARD Public Transit Bus Fleet Rule and Emission Standards for New Urban Buses California Air.
On-Board Diagnostics II (OBD II) and Emission Warranty Regulatory Update California Air Resources Board Mobile Source Control Division September 28, 2006.
BUSES BUILT WITH CARE Dave Beebe Assistant General Manager IC Corporation.
Reducing Emissions From Diesel Engines Robert Cross Chief, Mobile Source Control Division California Environmental Protection Agency AIR RESOURCES BOARD.
EPA CLEAN DIESEL ENGINE IMPLEMENTATION WORKSHOP CHUCK SALTER AUGUST 6-7, 2003.
Shaping the Future Exhaust After Treatment Systems.
Proposed Amendments to Heavy-Duty On-Board Diagnostic Requirements August 23, 2012 Heavy-Duty OBD.
Class Project Report, May 2005 ME/ChE 449 Sustainable Air Quality Highway Transportation: Trends from 1970 to 2002 and Beyond By Scott Kaminski Instructor.
ARB Phase III Reformulated Gasoline Auto Industry Comments Ann M. Schlenker DaimlerChrysler Representing the Alliance of Automobile Manufacturers September.
DIESEL EXHAUST EMISSIONS
Effects of Oil Derived Poisons on Catalyst Performance and Emission Test Considerations Presented to; GF-5 Engine Oil Emissions Systems Compatibility Task.
© 2005 Northeast States for Coordinated Air Use Management (NESCAUM) Advanced Mobile Source Training Course MS Diesel Session I. Motor Vehicle Diesel.
INGAS - Integrated GAS Powertrain 24 months Meeting, October, 2010 Project number: October 2010 Project number: October.
MY 09 Bluetec Comparison Advanced Product Planning Department Craig Iovino January 2008.
Diesel Exhaust Aftertreatment Systems for Gasoline Engine Instructors Curt Ward.
First in Service First in Value
Nonroad Diesel Engine and Fuel Standards
Emission Control Technology Implementation Feasibility
Diesel Engine Catalyst Deactivation/Ageing
Lemnos 11/9/03 Comparison of PM exhaust emissions measured at a chassis dynamometer and on-road chasing on a test track.
Test Fuel Properties FT Diesel fuel Diesel fuel Properties (8/19)
Lifetime impact of SO2-poisoning of Cu-CHA catalysts for NH3-SCR
Gasoline Engine Catalyst Deactivation/Ageing
Accelerated aging procedures for pollution control devices
Affect of Biodiesel Blends on DPF and SCR Systems
Presentation transcript:

Diesel Fuel Quality and Sulfur Effects on Catalyst-Based Exhaust Emission Controls: Manufacturers of Emission Controls Association May 2000

Presentation Outline  Introduction  Impact of Fuel Sulfur on Catalyst Emission Control Technology  Noble Metal Function  NOx Control Technology  PM Control Technology  Conclusions

Introduction  Fuel Quality Is an Integral Part of a Complete Emission Control System for Both Gasoline and Diesel Powered Vehicles  Although Other Fuel Constituents Affect Engine-Out Emissions, Fuel Sulfur Is the Single Most Important Constituent for Catalyst-Based Emission Control Technology  Sulfur in Diesel Fuel Adversely Affects the Emission Control Performance of All Catalyst-Based Emission Control Technologies

Introduction (cont.)  Near Zero Diesel Sulfur Levels Would Enable the Application of the Full Range of Control Technologies and Would Permit Each Technology to Be Optimized for Maximum Emission Control Performance  EPA Has Proposed Phase 2 On-Road HDE Standards of 0.2 g/bhp-hr NOx and 0.01 g/bhp-hr Particulate to Take Effect in the 2007 Timeframe  Fuel Sulfur Levels Will Be Instrumental in Meeting These Aggressive Targets

Zeolite or refractory oxide support Precious Metal SO 3 SO 4 = Transition Metal H 2 SO 4 O2O2O2O2 Sulfate make Sulfur inhibition Sulfate Poisoning SO 2 Sulfur Effects

Test procedure: Engine test bench, partial load, 1.9 L TDI engine Noble Metal Function: Sulfur Increases Light-Off Temperature and Reduces Peak Conversion CO Conversion (%) Exhaust temperature before catalytic converter ( o C) Regular Diesel fuel (350 ppm S) Quissel et al, VDA-Fortschrittsberichte, 12 (348), Bd. 2, (1998) CO Conversion (%) Exhaust temperature before catalytic converter ( o C) Sweden Diesel fuel (<10 ppm S) 1/2 hr Conditioned 32 hr Aging Oxidation Catalyst

Sulfur Adversely Affects Non-Precious Metal Lean NOx Catalysts

NOx Adsorbers: Sulfur Effects  Sulfur Poisoning and Inhibition  Inhibits Conversion of Unregulated Emissions (e.g. toxic HC emissions)  Prevents NOx Conversion  Increases Fuel Economy Penalty  Sulfate Make

Sulfur Poisons NOx Adsorbers Storage Sites Sulfur Poisons NOx Adsorbers Storage Sites 30s/2s 30hrs at 400 C Evaluation Temperature (C) NOx Conversion (%) Depth into Washcoat S/Ba Molar Ratio (%) 200 ppm100 ppm0 ppm 40 ppm *equivalent fuel sulfur content* The extent of poisoning increases with fuel sulfur content and duration of exposure.

Low Levels of Sulfur Are Needed to Maintain NOx Adsorber Catalyst Efficiency Miles Traveled Catalyst NOx Breakthrough, % 7 ppm Sulfur Fuel Catalyst "A" 150 ppm Sulfur Fuel Catalyst "A" 300 ppm Sulfur Fuel Catalyst "B" 0.1 ppm Sulfur Fuel Catalyst "c" 7 ppm Fuel: 1700 Miles 150 ppm Fuel: 115 Miles 300 ppm Fuel: 55 Miles Mileage Interval vs Fuel Sulfur Content which Leads to a 5% Decrease in Catalyst Efficiency (Note: T/P NOx emissions double when catalyst efficiency drops from 95 to 90% ) 0.1 ppm Fuel: >5,000 Miles

Poisoning period (hr) NOx Conversion (%) Gasoline fuel: California Phase 2 (ca. 30 ppm S) - Catalytic converter B Gasoline fuel: Super Plus (130 ppm S) Catalytic converter A Gasoline fuel: California Phase 2 (ca. 30 ppm S) Catalytic converter A Cycle during poisoning and measurement: 30/2 S lean/rich Test Procedure: Engine test bench, partial load operation Quissel et al, VDA-Fortschrittsberichte, 12 (348), Bd. 2, (1998) Advances in NOx Adsorber Sulfur Resistance

Catalytic Particulate Filters: Sulfur Effects  Sulfur Poisoning and Inhibition  Inhibits Control of Unregulated Emissions  Increases Regeneration Temperature  Formation of Sulfate

Catalytic Filter Regeneration Is Adversely Affected by Sulfur  A Low Regeneration Temperature Insures Reliable Catalytic Filter Operation and Durability  A Low Regeneration Temperature Allows Filter Technology to Be Applied to a Broad Range of Vehicle Applications  Higher Sulfur Levels in Diesel Fuel Increase a Catalytic Filter’s Regeneration Temperature  In the DECSE Program, Increasing the Fuel Sulfur Content from 3 ppm to 30 ppm Increased the Regeneration Temperature of Two Different Catalytic Filter Systems by 23 to Over 30 o C.  Experience in Countries Characterized by Very Cold Temperatures, e.g. Sweden, Indicates that There Have Been No Durability Problems with Systems Having Accumulated in Excess of 475,000 km when Diesel Fuel with <10 ppm Is Used

Impact of Sulfur on Heavy-Duty PM Emissions 90% Reduction from 2004 Std.

Impact of Sulfur on Light-Duty PM Emissions

The DECSE Study Is Showing That Low Sulfur Is Critical to Achieving a 0.01 g/bhp-hr PM Standard (System 1) From DOE website; Diesel Emission Control - Sulfur Effects; Sponsored by DOE, EMA, MECA, and National Labs OICA 13-mode cycle; CAT 3126 engine ~95% efficiency at 3 ppm sulfur ~70% efficiency at 30 ppm sulfur ~0% efficiency at 150 ppm sulfur Negative efficiency at 350 ppm sulfur

The DECSE Study Is Showing That Low Sulfur Is Critical to Achieving a 0.01 g/bhp-hr PM Standard (System 2) From DOE website; Diesel Emission Control - Sulfur Effects; Sponsored by DOE, EMA, MECA, and National Labs OICA 13-mode cycle; CAT 3126 engine ~95% efficiency at 3 ppm sulfur ~70% efficiency at 30 ppm sulfur ~0% efficiency at 150 ppm sulfur Negative efficiency at 350 ppm sulfur

Status of Reducing Impacts of Sulfur on NOx Adsorbers  MECA Members Continue Research Efforts in Decreasing Sulfur Sensitivity  BUT,  Desulfurization Frequency Needs to Be Minimized for Commercial Viability of NOx Adsorbers  Minimize Fuel Economy Penalty  Maximizes the Opportunity for Operating Conditions Conducive to Desulfurization to Be Met Under Normal In- Service Operation  To Meet Very Low Emission Levels Only an Approximately 5% Decrease in Performance Can Be Tolerated  Control of Unregulated Emissions Is Inhibited  Off-Cycle Emissions During Desulfurization  Inhibition of the Performance of Other Emission Control Devices  Sulfur Inhibition Is Cumulative

Status of Reducing Impacts of Sulfur on Catalytic Particulate Filters  MECA Members Continue Research Efforts in Decreasing Sulfur Sensitivity  BUT,  Sulfur Significantly Increase the Balance Point Temperature Due to Sulfur Inhibition which Adversely Affects Filter Regeneration  Control of Unregulated Emissions Is Inhibited  Cold Climatic Conditions Exasperate the Effects of Sulfur Inhibition  Sulfur Inhibition Is Cumulative

Conclusion  To Help Insure that Diesel Fuel Remains Competitive with Other Fuels, It Is Incumbent on the Engine Manufacturers, the Emission Controls Industry, and the Fuel Providers to Work Together to Provide a “Truly Clean” Diesel Engine so that the Public Accepts the Fuel As an Environmentally Friendly, Safe, and Efficient Means to Meet the Nation’s Transportation Needs