Coupled NO and C3H6 Trapping, Release and Conversion on Pd-BEA

Slides:



Advertisements
Similar presentations
Selective Catalytic Reduction (SCR) by NH 3 in a Fixed-Bed Reactor HEE JE SEONG The Department of Energy and Geo-Environmental Engineering The Pennsylvania.
Advertisements

Heterogeneous Catalysis & Solid State Physics Dohyung Kim May 2, 2013 Physics 141A.
CO x -Free Hydrogen by Catalytic Decomposition of Ammonia on Commercial Fe and Ru Catalysts: An Experimental and Theoretical Study Caitlin Callaghan Barry.
Business Development and Carbon Capture: Future Technologies for Green Energy Christopher W. Jones Georgia Institute of Technology School of Chemical.
Catalytic cracking Catalytic cracking
Ghent University - UGent Department of Flow, Heat and Combustion Mechanics Simulations of hydrogen auto-ignition Ivana Stanković.
Methane Powered Heavy Duty Engine with Low Fuel Consumption and Euro VI Emission Compliance X. Auvray 1, N. Sadokhina 1, G. Smedler 2, U. Nylén 3, M. Holmström.
Insert Short Title of Project Insert Names Insert Project Information Combination of Chemical-Looping Combustion and Hydrothermal Conversion Combining.
2010 Diesel Emission Reduction Consortium Experimental Studies of Exhaust Chemistry and Aftertreatment Professor Thatcher Root Department of Chemical and.
Temperature dependence of reaction rates
University of Wisconsin Engine Research Center Diesel Stoichiometric Combustion SANGSUK LEE & Rolf D. REITZ Motivation  Diesel engines face difficulties.
Sohail Ghanchi Energy Technology and Policy The University of Texas at Austin.
RETROFIT EMISSION CONTROL TECHNOLOGIES FOR HEAVY DUTY DIESEL ENGINES - THE STATE OF THE ART Sougato Chatterjee Johnson Matthey Catalysts BAQ 2004.
Development and Implementation of CO and HC Emission Models for use in an Integrated Diesel Engine, Emissions and Aftertreatment System Model Nilesh L.
Bimetallic Silver Catalysts for the Reformate-Assisted Hydrocarbon Selective Catalytic Reduction (HC-SCR) of Nitrogen Oxides Richard Ezike Ph.D. Defense.
Concawe Nanoparticles from road vehicle exhaust: an artefact or a reality? Diane Hall BP/CONCAWE Lemnos Meeting: Round Table Discussion 11 th September.
A Green Chemistry Module Nucleophilic Aromatic Substitution Presidential Green Chemistry Challenge Award Elimination of Chlorine in the Synthesis of 4-Aminodiphenylamine.
John Kim CHE359 11/25/08. Search for Alternative Fuels Peak Oil is approaching or already passed. Oil market is becoming more and more volatile. Need.
Diesel Fuel Quality and Sulfur Effects on Catalyst-Based Exhaust Emission Controls: Manufacturers of Emission Controls Association May 2000.
INGAS - Integrated GAS Powertrain Project number: Project number: DAIMLER AG INGAS 18 months meeting, Paris, 20./ InGas 18 months.
INGAS 18 th month meeting, Paris, May INGAS INtegrated GAS Powertrain 1 Politecnico di Milano Dipartimento di Energia Research Activities Nov.
INGAS “24 Months Meeting ”, “Brussels, Belgium”, “27-28 October 2010” INGAS INtegrated GAS Powertrain 1 INGAS 24 months meeting Brussels - Belgium 27 -
INGAS 6 month meeting, Prague, May 2009 INGAS INtegrated GAS Powertrain 1 Politecnico di Milano Dipartimento di Energia Research activity from Nov.
NOx formation in ultra-low-NOx gas burners Zoran M. Djurisic, Eric G. Eddings University of Utah.
Shaping the Future Exhaust After Treatment Systems.
Shaping the Future Emissions Formation and Control.
Chemical Reactions Vocabulary. catalyst A ___ is used to start or speed up a reaction.
Noble Metals as Catalysts Oxidation of Methanol at the anode of a DMFC Zach Cater-Cyker 4/20/2006 MS&E 410.
1Korea University of Technology and Education 2 Generation Common Rail VGT Variable Swirl 32Bit Computer Elec. Controlled EGR Flap C P F Electronically.
Catalytic production of methane from CO 2 and H 2 at low temperature: Insight on the reaction mechanism A review by Shujin Jiang 3/17/2015.
AQ Data Collection and Monitoring Emissions. Learning Objectives After this activity, you should be able to: List the products of complete and incomplete.
Lee Roberts and Charlotte Stead
ENTRAINED FLOW GASIFICATION OF WOOD PYROLYSIS OIL
ALTERNATE FUELS Alcohols , Vegetable oils and bio-diesel, Bio-gas, Natural Gas, Liquefied Petroleum Gas, Hydrogen, Properties, Suitability, Engine Modifications,
1 Hom Sharma Ashish Mhadeshwar
P M V Subbarao Professor Mechanical Engineering Department
A Review by: Ritwik Athalye April 28th, 2015
ENZYMES and Activation Energy
S2 Chemistry Materials from the Earth
POLLUTION IN IC ENGINES
STEP 1 Low-Temperature Oxidation
Fischer-Tropsch Reaction Kinetics
Microkinetic Study of CO Adsorption and Dissociation on Fe Catalysts
Date of download: 11/6/2017 Copyright © ASME. All rights reserved.
Sorption-enhanced hydrogen production for pre-combustion CO2 capture
Maryam Abdolrahmani, Kuizhi Chen and Jeffery L. White*
Reactions of unsaturated oxygenates on metal surfaces
Diesel Engine Catalyst Deactivation/Ageing
CH EN 5253 – Process Design II Dealing with Impurities in Processes and Process Simulators February 09, 2018.
KEY CONCEPT Life depends on chemical reactions.
On the activation mechanism of Sn to the EER of ethanol: decomposition of H2O and ethanol over PtnM clusters Yixuan Wang, Albany State University, Albany,
Selective removal of oxygen by carbon monoxide instead of
AFTERTREATMENT PROTOCOLS FOR CATALYST CHARACTERIZATION
A Systematic And Mechanistic Analysis Of The Water-Gas Shift Reaction Kinetics On Low And High Temperature Shift Catalysts CA Callaghan, I Fishtik, and.
Chemical Reactions.
NOTES 9 – Chemical Reactions
Complex Anode Kinetics Chronocoulometry Evidence
Volume 1, Issue 1, Pages (September 2017)
Lifetime impact of SO2-poisoning of Cu-CHA catalysts for NH3-SCR
Chemical Reactions and Enzymes
Burning fuels: three sources of pollution
CONTROL OF NITROGEN OXIDES
Volume 4, Issue 4, Pages (April 2018)
Catalyst Modification to Reduce Product Inhibition During High Temperature Water-Gas Shift, C. Lund (PI) DFT models of unpromoted and Cu-promoted sites.
Andrew P. Wong, Qiuli Liu, John R. Regalbuto
Andrew Wong, Todd J. Toops*, and John R. Regalbuto
15% H2 or 1% CO in N2 balance at 500 – 900 ℃
Affect of Biodiesel Blends on DPF and SCR Systems
Integrated Aftertreatment System Modeling Using GT-POWER
Presentation transcript:

Coupled NO and C3H6 Trapping, Release and Conversion on Pd-BEA Sam Malamis, Mugdha Ambast, Michael P. Harold, William S. Epling1 Department of Chemical and Biomolecular Engineering, University of Houston, Houston, TX 77204 1Department of Chemical Engineering University of Virginia, Charlottesville, VA Motivation Proposed Mechanism NO + C3H6 Co-adsorption PdO  Pd2+ Distribution PdO + 2H+Z- ↔ Z-Pd2+Z- + H2O Complete Storage/Release Profile NO: 60 μmol/g-cat HC: 830 μmol/g-cat Stringent requirements on fuel economy and emission standards are challenging to meet for both gasoline and diesel engine vehicles A number of technologies including low temperature diesel combustion are in development for improving fuel economy, but produce higher amounts of NOx Typical systems (TWC, LNT, SCR) are ineffective below ~200°C Increased emissions during cold start NOx/N2O Desorption C3H6 inhibits NO adsorption (63% reduction) NOx desorption peak shifts to the right Fraction desorbing above 200°C increases from 52% to 86% NO2 formed during ads./des. reduced by C3H6, also forms N2O Product distribution depends on both acid site and Pd-catalyzed interactions Multiple CO2 peaks caused by variations in light-off bahavior of HCs formed during adsorption Objectives Pd2+  Pd+ Oxidation - Reduction 2[PdOH]+Z- + NO ↔ 2Pd+Z- + NO2 + H2O Z-[Pd-O-Pd]2+Z- + NO ↔ NO2 + 2Pd+Z- Z-Pd2+Z-+ NO ↔ Z-Pd+(NO)+Z- H2O + ½ O2 + 2Pd+Z- ↔ 2[PdOH]+Z- C3H6 Adsorption and Oligomerization H+Z- + C3H6 ↔ [H3C(CH)+CH3]+Z- n[H3C(CH)+CH3]+Z- ↔ [H3C(CH)+(CH3)]n+Z- Investigate a multifunctional catalyst with the following behavior Trap NO and HC at temperatures below 200°C Release NO and HC upon warm-up Oxidize HC/CO to CO2 Further understanding of combined NO/HC trapping/release effectiveness Develop mechanistic understanding of NO/HC storage and their inhibitive behavior Evaluate the impact of water and investigate methods to improve storage Formulate working model that can predict storage, release and oxidation behavior of PNA catalyst Global Pd-Catalyzed Reactions NO + ½ O2 ↔ NO2 2 NO  0.5 O2 + N2O C3H6 + 9 NO  3 CO2 + 3 H2O + 4.5 N2 C3H6 + 4.5 O2 ↔ 3 CO2 + 3 H2O C3H6 + 3 O2 ↔ 3 CO + 3 H2O C3H6 + 4 NO2 ↔ 3 CO + 3 H2O + 2N2O C3H6 + 4.5 NO2 ↔ 3 CO2 + 3 H2O + 2.25 N2 NO Adsorption and Other Reactions Pd+Z- + NO ↔ NOPd+Z- NO + ½ O2 + H+Z- ↔ [NO2 H] +Z- [NO2 H] +Z- + ½ O2 ↔ [NO3 H] +Z- 2NO2 ↔ N2O4 ↔ NO+ + NO3- H+Z- + NO+ + NO3-↔ NO+Z- + HNO3 Water Effects NOx Adsorption C3H6 Adsorption Experimental Setup H2O inhibits NO and C3H6 adsorption Oxytreatment: 10% O2,bal. Ar at 750°C for 2hr [4] C3H6 Adsorption, Desorption and Light-Off Catalyst 2wt% Pd-BEA (SAR 38) 1.5g/in3 monolith (0.31g total) 400 cpsi 2500 sccm (32k hr-1) Feed Conditions All feeds contain 2% O2, bal. Ar Adsorption Profile Desorption Profile Conditions: 400ppm NO or 800ppm C3H6 , 2% O2, 0 or 5% H2O, 80°C ads. Ads. Temp. (°C) Storage Time NOin (ppm) C3H6,in (ppm) 50°C, 80°C, 150°C 5 min 400 ppm 0 ppm 800 ppm Conclusions & Future Work Mechanism developed consistent with adsorption, desorption and reaction data Significant findings include: NO stores on both Pd and BEA acid sites through a number of interactions C3H6 forms coupled products during adsorption, leads to the release of a complex distribution of hydrocarbons NO and C3H6 uptake are mutually inhibitive due to competition for adsorption on Brønsted acid sites C3H6 delays NO desorption to higher temperatures High-temperature oxidation pretreatment improves NO uptake in presence of H2O Upon warmup, PNA aids in oxidation of HC to CO2 Future work includes development of predictive kinetic model for Pd/BEA system Future experimental work includes steady state and oxidation studies to evaluate kinetic parameters Model development can be used to predict behavior of other Pd-based zeolites 80 NOx Storage Conditions: 800ppm C3H6, 2% O2, 50-150°C ads., 20°C/min des. Desorption profile provides evidence for C3H6 coupling NO uptake decreases with temperature NO2 formation during uptake suggests NO oxidation Key step in NO storage Multi-peak desorption indicates formation of various storage complexes NO on BEA (low Temp.) NO on Pd (high Temp.) Adsorption Profile Desorption Profile C3H6 Light-Off Behavior T50 vs. Feed C3H6 400ppm 800ppm 1200ppm 1600ppm 1800ppm References Acknowledgements Y. Murata, T. Morita, K. Wada, H. Ohno, SAE Int. J. Fuels Lubr. 8 (2015) p.1. H.-Y. Chen, J.E. Collier, D. Liu, L. Mantarosie, D. Durán-Martín, V. Novák, R.R. Rajaram, D. Thompsett, Catal. Letters. 146 (2016) p.1706. Y. Zheng, L. Kovarik, M.H. Engelhard, Y. Wang, Y. Wang, F. Gao, J. Szanyi, J. Phys. Chem. C. 121 (2017) p.15793. Y.S. Ryou, J. Lee, S.J. Cho, H. Lee, C.H. Kim, D.H. Kim, Appl. Catal. B Environ. 212 (2017) p.140. Funding provided by: FCA, Inc. US DOE-EERE Vehicle Technologies Program Conditions: 400ppm NO, 2% O2, 80°C ads., 20°C/min des. Conditions: 400-1800ppm C3H6, 2% O2, 5°C/min