Fuel-Borne Reductants for NOx Aftertreatment: Preliminary EtOH SCR Study

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Fuel-Borne Reductants for NOx Aftertreatment: Preliminary EtOH SCR Study Oak Ridge National Laboratory: Caterpillar: John Thomas, Mike Kass, Sam Lewis, John Storey, Ron Graves, Bruce Bunting Alexander Panov, Paul Park Other contributors: Williams-Pekin: Fuel grade ethanol GE Betz: Blending agent, blend testing Gromark: Blended fuel Illinois DOCCA: Coordinated delivery Sponsor: US DOE, OFCVT, Team Leader: Steve Goguen Diesel Engine Emissions Reduction Workshop August 28, 23

Background Leading to Current Effort 1. Previous work: E-diesel, urea SCR, adsorber catalysts. 2. HC SCR receiving less attention than other aftertreatment technologies. 3. ORNL formulated concepts for fuel-borne reductant systems. EtOH seen as a removable fuel-borne reductant for HC SCR 4. Caterpillar marketed an EtOH SCR system for stationary diesels. Co-operative effort developed between Caterpillar and ORNL

Comparison of Urea SCR to EtOH SCR Urea SCR Commercial technology for stationary engines NOx Reduction > 9% achievable for 3-5 C Uses ~ 1:1 NH 3 /NOx mol ratio Aqueous solution injected into exhaust 32.5% urea freezes at 12 F Can produce/slip NH 3, N 2 O, inert PM, reactive solids EtOH SCR R&D, utility being explored NOx Reduction ~ 8% thought to be possible for 4-5 C? Uses 3:1 C/NOx mole ratio Used undiluted, can be fuelborne Freezing not an issue Unwanted products/slip likely:, NH 3, N 2 O, aldehydes, HC

Initial Project Objectives: Evaluate performance of EtOH reductant, Ag- Alumina SCR catalyst system on diesel exhaust. Look at unregulated emissions Demonstrate EtOH stripping from E-diesel & its usefulness for NOx reduction. Later: consider other fuel-borne reductants, catalysts

Ethanol Was Stripped From 15% E-Diesel NTRC Analytical Lab. Using mild distillation nearly all EtOH was removed and then recovered

Experimental Configuration Donated 1999 Cummins ISB, 5.9 L, With Cummins provided cooled EGR, upgraded fuel system, turbo., controls. Configured for Near- 24 emissions. 285 hp DC motoring dynamometer Measured gases in exhaust via standard benches FTIR and GC-MS used to look for specific HCs, N 2 O, NH 3, Acetaldehyde Injector UEGO Ag Catalyst FTIR Microdilution Tunnel Engine NGK NOx sensor Analytical Bench: O 2 NOx, CO, HC, CO 2 Analytical Bench: O 2 NOx, CO, HC, CO 2 GC-MS Bag Sample Photoacoustic Spectrometer

Cummins 5.9 L Engine BURNER

Reductant Injector and Catalyst in the Exhaust ORNL/NTRC Cell 3 7 L catalyst located 1 m downstream of the injector. Automotive EFI injector downstream of turbo outlet.

SCR Performance Experimental Methodology Shakedown, de-green catalyst for ~1 hours at 4 C. Performance Investigation at Two Engine Conditions / Space Velocities: compared conversion at a low & high space velocity while maintaining similar catalyst temperature and NOx flux. Test Speed Torque SV Cat T NOx Setting RPM ft-lbs 1/h C g/min AVL8-M3 1115 23 21 36-4 ~1.5 ~AVL8-M6 2225 18 57 36-4 ~2.1 Fuel-Reductant Combinations: Fuel Reductant 1. ECD-1 fuel-grade EtOH 2. ECD-1 stripped fuel-grade EtOH 3. E-diesel stripped fuel-grade EtOH 4. ECD-1 reagent grade EtOH

Excellent NOx Conversion Was Achieved at 21/h, 36-4 C 1 NOx conversion vs C/N ratio, 1115 RPM NOx conversion (%) 9 8 7 6 5 4 3 ECD1, fuel EtOH, test 1 2 1 Space Velocity ~ 21, 1/h Catalyst temperature: 36-39 C 1 2 3 4 5 6 7 8 9 1 carbon/nitrogen ratio (2X Ethanol/NO2)

Excellent NOx Conversion Was Achieved at 21/h, 36-4 C 1 NOx conversion vs C/N ratio, 1115 RPM NOx conversion (%) 9 8 7 6 5 4 3 2 ECD1, fuel EtOH, test 1 ECD1, fuel EtOH, test 2 ECD1, stripped EtOH, test 3 1 Space Velocity ~ 21, 1/h Catalyst temperature: 36-39 C 1 2 3 4 5 6 7 8 9 1 carbon/nitrogen ratio (2X Ethanol/NO2)

1 NOx Conversion Was Excellent at 21/h and 36-4 C Selectivity appeared to improved as catalyst is exposed to more sulfur NOx conversion vs C/N ratio, 1115 RPM 9 8 NOx conversion (%) 7 6 5 4 3 2 1.5% fuel penalty: energy basis ECD1, fuel EtOH ECD1, fuel EtOH ECD1, stripped EtOH E-diesel, stripped EtOH ECD1, fuel EtOH ECD1, high-grade EtOH 1 Space Velocity ~ 21, 1/h Catalyst temperature: 36-39 C 1 2 3 4 5 6 7 8 9 1 carbon/nitrogen ratio (2X Ethanol/NO2)

Good NOx Conversion Achieved at 57/h and 36-4 C 1 9 NOx conversion vs C/N ratio, 2225 RPM NOx conversion (%) 8 7 6 5 4 3 2 1 1.5% fuel penalty: energy basis NOx conversion very similar for the different fuel-reductant combinations 2 4 6 8 1 12 carbon/nitrogen ratio (2X Ethanol/NO2) ECD1, fuel EtOH E-diesel, stripped EtOH ECD1, fuel EtOH Space Velocity ~ 57, 1/h Catalyst temperature: 36-39 C

16 14 12 HC Slip Changed with Progression of Experiments ECD1, fuel EtOH ECD1, fuel EtOH ECD1, stripped EtOH E-diesel, stripped EtOH ECD1, fuel EtOH ECD1, high grade EtOH HC slip vs C/N ratio, 1115 RPM HC slip (ppm) 1 8 6 4 Space Velocity ~ 21, 1/h Catalyst temperature: 36-39 C 2 Reagent grade EtOH 1 2 3 4 5 6 7 8 9 1 carbon/nitrogen ratio

HC slip at high SV was about the same ppm level, mass flux is ~2.7 times greater 25 low SV, E-diesel, stripped EtOH HC slip vs C/N ratio, 21, 1/h & 57, 1/h HC slip (ppm) 2 15 1 low SV, ECD1, fuel EtOH low SV, ECD1, reagent EtOH High SV, E-diesel, stripped EtOH High SV, ECD1, fuel EtOH ~.19 g/hp-h ~.5 g/hp-h 5 Catalyst temperature: 36-39 C 2 4 6 8 carbon/nitrogen ratio

FTIR Results: Ammonia Emissions 6 NH 3 (ppm) 5 4 3 NH3 @ 21/h NH3 @ 57/h 2 1 2 4 6 8 1 12 C1:NOx Ratio

FTIR Results: N2O Emissions In the past, some catalyst formed large amounts of N 2 O 6 5 N2O @ 21/h N2O @ 57/h N 2 O Level (ppm) 4 3 2 1 2 4 6 8 1 12 C1:NOx Ratio

6 FTIR Results: NO X, Versus Acetaldehyde Emissions Acetaldehyde (ppm) 5 4 3 2 Acet @ 21/h Acet @ 57/h 1 2 4 6 8 1 12 C1:NOx Ratio

We Have Begun to Look at Other Fuel-borne Reductants Note: much higher SV and NOx flux 8 7 7 liter Ag alumina catalyst, 2225 rpm, 36 deg.c, 9 SV, % NOX conversion 6 5 4 3 2 1 EtOH Octanol Heptane 1 2 3 4 5 6 7 ethanol flow, wt% of fuel flow

Reductant stripping experiments REDUCTANT BOILING POINT, deg.c % BLENDED IN ECD1 FUEL % SEPARATED (rotovap, 1 CC, 1 minutes, 9 deg.c, 2 mm Hg vacuum) ethanol 78 2 2 1-propanol 97 2 18 1-butanol 117 2 17.5 n-hexane 69 2 4.9 n-heptane 98 2 5 1-octanol 196 2

Low Temperature Effectiveness of Catalyst 1 NOx conversion vs catalyst temperature NOx conversion (%) 9 8 7 6 5 4 3 1115 RPM ECD1, fuel ethanol SV varies from 17, to 21, 1/h C/N ~ 6 C/N ~ 3 2 1 24 26 28 3 32 34 36 38 Low Temperature Evaluation: For low SV, catalyst temperatures near 25 C, 3 C, 34 C and 37 C were examined at two C/N ratios Ag catalyst temperature (C)

GC-MS Results Clearly Show Different Nature of Slip HC for The 3 EtOH Grades Abundance 16 SV = 21, 1/h 14 12 1 8 E-diesel distilled, fuel grade EtOH: evidence of gasoline & diesel components C9 C1 6 4 Denatured, fuel grade EtOH: gasoline components seen Time--> 2 2. 3. 4. 5. 6. 7. 8. 9. Reagent grade EtOH

Observations & Conclusions Ethanol SCR effectively reduced NOx emissions of diesel exhaust for catalyst temperatures between 36-4 C moderate C1/NOx ratios 9% for 21/h and 8% for 57/h Some conversion observed at 25 C Saw catalyst performance improve with sulfur exposure Low levels of N 2 O (< 6 ppm ) were produced Ethanol was converted to acetaldehyde: slipped at 57 1/h Ammonia was produced (high C/N, low SV), but may not be problematic Fuel-borne feasibility was demonstrated by stripping EtOH from E-diesel use as reductant in the SCR system Technology may show promise - examining a broader set of parameters/conditions is warranted