A new transient CLEERS SCR protocol

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A new transient CLEERS SCR protocol Josh Pihl, Todd Toops, Stuart Daw Oak Ridge National Laboratory presented to: 2010 DOE Crosscut Workshop on Lean Emissions Reduction Simulation Dearborn, MI April 20, 2010

Acknowledgments Funding sponsors: Ken Howden & Gurpreet Singh U.S. DOE Office of Vehicle Technologies CRADA partners for development of protocol predecessor: Vadim Strots, Ed Derybowski Navistar, Inc. Gordon Parker Michigan Technological University Providers of feedback during early stages: John Lee, Maruthi Devarakonda Pacific Northwest National Laboratory Kalyan Chakravarthy Oak Ridge National Laboratory 2

Motivation Existing CLEERS protocol for urea SCR is a collection of steady state points It does not measure NH 3 storage and release or the reactivity of stored NH3, which are crucial to accurate device simulations A new transient protocol would: generate well-defined data sets that could be used for parameter estimation and model validation help minimize time and expense required to generate such data sets (enable rapid adaptation to changing catalyst formulations) facilitate comparison of catalyst properties and kinetic data between organizations avoid expense and hassle for others to build a protocol from scratch held ensure the experiments we run are relevant to the needs of the aftertreatment modeling and development community 3 Goal: Create a general methodology for running SCR experiments that extracts necessary model parameters (reaction kinetics, storage capacities) with minimal time and expense

Approach Define time sequence of inlet compositions and catalyst temperatures Leave most operating parameters variable to allow users to customize protocol based on application requirements temperatures space velocities step times (depend on temperatures, space velocities, catalyst formulation) instead of prescribed times, allow each step to come to a steady state current definition of steady state: 0.1% change in concentration per minute concentrations of O 2, H 2 O, CO 2, and total NOx NH 3, NO, and NO 2 concentrations defined relative to total NOx in protocol Provide a set of suggested operating parameters 4

Scope of proposed protocol Processes included in current scope: NH 3 storage capacity NH 3 desorption NH 3 oxidation NO oxidation NO only SCR kinetics, including NH 3 /NO ratio impact NO + NO 2 SCR kinetics decomposition of surface species formed under low temperature SCR conditions Not currently included: impact of O 2, H 2 O, and CO 2 concentrations dynamic (pulsed input) experiments urea thermolysis/hydrolysis poisons (HCs, sulfur) 5

Proposed CLEERS transient SCR protocol Step Description NH 3 NO NO 2 O 2 H 2 O CO 2 T 0(a) Pretreat 0 0 0 [O 2 ] [H 2 O] [CO 2 ] Tn+50 0(b) T change 0 0 0 [O 2 ] [H 2 O] [CO 2 ] Tn+50 ->T0 0(c) NH 3 adsorption [NOx] 0 0 0 [H 2 O] [CO 2 ] T0 0(d) NH 3 TPD (10 C/min) 0 0 0 0 [H 2 O] [CO 2 ] T0 >Tn+50 0(e) Pretreat 0 0 0 [O 2 ] [H 2 O] [CO 2 ] Tn+50 1(a) T change 0 0 0 [O 2 ] [H 2 O] [CO 2 ] Tn+50 > Tn 1(b) NH 3 storage [NOx] 0 0 0 [H 2 O] [CO 2 ] Tn 1(c) NH 3 oxidation [NOx] 0 0 [O 2 ] [H 2 O] [CO 2 ] Tn 1(d) NO+NO2 SCR α = 1.0 [NOx] 0.5[NOx] 0.5[NOx] [O 2 ] [H 2 O] [CO 2 ] Tn 1(e) NO SCR α = 1.0 [NOx] [NOx] 0 [O 2 ] [H 2 O] [CO 2 ] Tn 1(f) NO SCR α = 0.9 0.9[NOx] [NOx] 0 [O 2 ] [H 2 O] [CO 2 ] Tn 1(g) NO SCR α = 1.1 1.1[NOx] [NOx] 0 [O 2 ] [H 2 O] [CO 2 ] Tn 1(h) NO oxidation, NH 3 storage 0 [NOx] 0 [O 2 ] [H 2 O] [CO 2 ] Tn 2(a) T change 0 0 0 [O 2 ] [H 2 O] [CO 2 ] Tn > T(n-1) Repeat a-h for all temperatures T(n-1) T0 n(h) NH 3 storage, NO oxidation 0 [NOx] 0 [O 2 ] [H 2 O] [CO 2 ] T0 6 n+1(a) TPD (10 C/min) 0 0 0 [O 2 ] [H 2 O] [CO 2 ] T0 > Tn+50

Example operating parameters for transient CLEERS SCR protocol operating temperatures: 150, 200, 250, 300, 350, 500, 450, 500, 550 C n = 9 T0 = 150 C Tn = T9 = 550 C Tn+50 = 600 C concentrations (from steady state CLEERS SCR protocol): [NOx] = 350 ppm [O 2 ] = 14% [H 2 O] = 4.5% [CO 2 ] = 5% 7

Example CLEERS transient SCR protocol 8 Step Description NH 3 (ppm) NO (ppm) NO 2 (ppm) 0(a) Pretreat 0 0 0 14 4.5 5 600 0(b) T change 0 0 0 14 4.5 5 600->150 0(c) NH 3 adsorption 350 0 0 0 4.5 5 150 0(d) NH 3 TPD (10 C/min) 0 0 0 0 4.5 5 150 >600 0(e) Pretreat 0 0 0 14 4.5 5 600 1(a) T change 0 0 0 14 4.5 5 600 > 550 1(b) NH 3 storage 350 0 0 0 4.5 5 550 1(c) NH 3 oxidation 350 0 0 14 4.5 5 550 1(d) NO+NO2 SCR α = 1.0 350 175 175 14 4.5 5 550 1(e) NO SCR α = 1.0 350 350 0 14 4.5 5 550 1(f) NO SCR α = 0.9 315 350 0 14 4.5 5 550 1(g) NO SCR α = 1.1 385 350 0 14 4.5 5 550 1(h) NO oxidation, NH 3 storage 0 350 0 14 4.5 5 550 2(a) T change 0 0 0 14 4.5 5 550 > 450 Repeat a-h for all temperatures O 2 (%) H 2 O (%) CO 2 (%) T ( C) 450 150 9(h) NH 3 storage, NO oxidation 0 175 0 14 4.5 5 150 10(a) TPD (10 C/min) 0 0 0 14 4.5 5 150 > 600

Example CLEERS transient SCR protocol plot of temperatures and gas compositions NH 3 ads/tpd isothermal feed gas transients repeated at each T TPD 9

CLEERS Transient SCR Protocol isothermal feed gas transients at each T T change NH 3 uptake NH 3 oxid. NO+NO 2 NO SCR SCR α = 1.0 0.9 1.1 NO oxid. T change 10

Other operating details Ran on automated flow reactor Used Cu zeolite core sample (1.9 cm D x 5 cm L) SV = 60,000 hr -1 Total run time for protocol: 21 hours 11

Sample data: outlet composition at 300 C NH 3 uptake NH 3 oxid. NO+NO 2 NO SCR SCR α = 1.0 0.9 1.1 NO oxid. 12

Sample results: steady state conversions NOx conversion NH 3 conversion NH 3 /NOx NO 2 /NOx 13

Sample results: SCR stoichiometry and oxidation conversion 14

Sample results: NH 3 storage from NH 3 uptake and NOx converted by stored NH 3 NH3 uptake NOx after NH 3 removed NH3 released (during NO oxid) 15

Sample results: TPDs 16

Questions to ponder Have we missed anything critical? Have we included anything unnecessary? Are either of the previous two answers dependent on the type of model the data will be used to calibrate? If so, do we need more than one protocol, or perhaps a separate group of experiments to include in the protocol just for more detailed models? Are there any problems with the way the protocol is constructed (order of steps, variable parameters)? Fire Away! pihlja@ornl.gov 17