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The Effects of Hydrocarbons on NOx Reduction over Fe-based SCR Catalyst Maruthi Devarakonda 1 , Russell Tonkyn 1 , Diana Tran 1 , Darrell Herling 1 , Jong Lee 1 , Josh Pihl 2 , Stuart Daw 2 1 Pacific Northwest National Laboratory 2 Oakridge National Laboratory Directions in Engine-Efficiency and Emissions Research Detroit, MI September 30 th , 2010
Transcript

The Effects of Hydrocarbons on NOxReduction over Fe-based SCR Catalyst

Maruthi Devarakonda1, Russell Tonkyn1, Diana Tran1, Darrell Herling1, Jong Lee1, Josh Pihl2, Stuart Daw2

1Pacific Northwest National Laboratory2Oakridge National Laboratory

Directions in Engine-Efficiency and Emissions ResearchDetroit, MI

September 30th, 2010

2

Motivation

• Selective Catalytic Reduction (SCR) effective over a wide range of temperatures.

• Higher NOx reduction performance required to meet more stringent emission standards

• Cooler exhaust temperatures due to advanced combustion technologies.

• Factors that can affect NOx conversion at low temperatures include: Inhibition of NH3 storage at low temperatures

Hydrocarbon slip from DOC/DPF during cold-start

3

Objectives

• Investigate the effects of hydrocarbons on various SCR reaction steps under controlled lab reactor conditions.

• Develop kinetic models to characterize competitive adsorption and inhibition, and to describe the impact on SCR performance quantitatively.

4

Outline

• Lab Reactor Experiments

• DRIFT Experiments

• Hydrocarbon Storage & Inhibition Modeling

• Conclusions & Future Work

5

Reactor Test Setup

Fe-zeolite catalyst400/6.5

160g/L washcoat loading

6

Test Conditions

7

NOx Reaction Pathways

In addition to NH3 adsorption and desorption on SCR catalyst surface,

NH3 oxidation: 2NH3 + 3/2O2 → N2 + 3H2O

NO oxidation: NO + 1/2O2 ↔ NO2

Standard SCR: 4NH3 + 4NO + O2 → 4N2 + 6H2O

NO2-SCR: 4NH3 + 3NO2 → 7/2N2 + 6H2O

Fast SCR: 2NH3 + NO + NO2 → 2N2 + 3H2O

8

20

40

60

80

100

200 300 400 500 600Temperature (oC)

Con

vers

ion

(%)

NOx (with Dodecane) NOx (w/o HC)NH3 (with Dodecane) NH3 (w/o HC)NOx (with Toluene) NH3 (with Toluene)

Feed Conditions

175 ppm NO

175 ppm NO2

350 ppm NH3

14% O2

2% H2O

50 ppm toluene (350 C1)

29 ppm dodecane (350 C1)

29k h-1

Effect of Hydrocarbon on NOx Reduction

• No effect of ethylene, propane

• Detrimental effects of toluene, dodecane

9

Feed Conditions

350 ppm NOx

350 ppm NH3

14% O2

2% H2O

50 ppm toluene (350 C1)

29k h-1

Effect of Toluene on NOx Reduction

• More pronounced effect on Standard SCR

• No effect on NO2-SCR

10

350 ppm NO, 14% O2, 25 ppm toluene, 2% H2O

• More pronounced inhibition effect during temp-up ramp

• Severe inhibition in the presence of H2O

Effect of Toluene on NO Oxidation

11

Feed Conditions

175 ppm NO

175 ppm NO2

350 ppm NH3

14% O2

2% H2O

29 ppm dodecane (350 C1)50

60

70

80

90

100

200 300 400 500 600Temperature (oC)

Con

vers

ion

(%)

NOx, w/o dodecaneNOx,w/ Dodecane

• Decreased NOx reduction during temp-down ramp

• More pronounced effect on Standard SCR

• No effect on NO2-SCR

Effect of Dodecane on NOx Reduction

12

Outline

• Lab Reactor Experiments

• DRIFT Experiments

• Hydrocarbon Storage & Inhibition Modeling

• Conclusions & Future Work

13

In Situ DRIFT Setup

• Diffuse reflectance IR FT spectroscopy (DRIFT) Adsorbates on the particle surfaces

under SCR reaction conditions

• Typical experiment: Under 14% O2, 5% CO2, 4.5% H2O:

o Heat to 500 C to clean surfaceo Cool to experiment temperatureo Take background spectrum

Turn on 350 ppm NOx Turn on 350 ppm NH3

Turn on 350 ppm [C1] HC Continue scanning after turning off HC

HeatElement

ParabolicMirror

Sample

GasIn

GasOut

HeatElement

ParabolicMirror

Sample

GasIn

GasOut

HeatElement

ParabolicMirror

Sample

GasIn

GasOut

HeatElement

ParabolicMirror

Sample

GasIn

GasOut

IR Beam

in situ DRIFTS reactor

14

NH3 Consumption by NOx

Exposure conditions: 350 ppm NO or NO2, 350 ppm NH3, 14% O2, 5% CO2, 4.5% H2O

• Surface NH3 continually consumed by SCR reactions

• NO more effective than NO2at decreasing adsorbed NH3

3800 3300 2800 2300 1800 13004300

wavenumber (cm-1)

abso

rban

ce

200°C

300°C

-0.15-0.1

-0.050

0.050.1

0.150.2

0.250.3

0.35

-0.1-0.08-0.06-0.04-0.02

00.020.040.060.08

0.1

NH3 NH3+NO NH3+NO2

15

Toluene Inhibition at 200°C

• Introduction of toluene generates new adsorbates‒ 1300-1800 cm-1: most likely

toluene and derivatives

• Increased NH3 on surface due to poisoned NO+NH3reaction

• No changes upon removal of toluene‒ Poisoning irreversible at 200 C

• Little effect on NO2-SCR

3800 3300 2800 2300 1800 13004300

wavenumber (cm-1)

abso

rban

ceab

sorb

ance

diff

eren

ce

-0.15-0.1

-0.050

0.050.1

0.150.2

0.250.3

0.35

[NH3][NH3+NO]

-0.1

-0.05

0

0.05

0.1

0.15

[NH3+NO+C6H5CH3]

[NH3+NO+C6H5CH3] - [NH3+NO]

[NH3+NO(-C6H5CH3)]

[NH3+NO(-C6H5CH3)] - [NH3+NO]

16

Reduced Inhibition at 300°C

• Toluene addition shifts spectrum considerably‒ Increased NH3 on the surface‒ Increased toluene-derived

species

• Some recovery upon removal of toluene‒ Increased NH3 consumption‒ Reduced toluene-derived species

3800 3300 2800 2300 1800 13004300

wavenumber (cm-1)

-0.1-0.08-0.06-0.04-0.02

00.020.040.060.08

0.1

[NH3][NH3+NO]

-0.08

-0.06

-0.04

-0.02

0

0.02

0.04

0.06

[NH3+NO+C6H5CH3]

[NH3+NO+C6H5CH3] - [NH3+NO]

[NH3+NO(-C6H5CH3)]

[NH3+NO(-C6H5CH3)] - [NH3+NO]

abso

rban

ceab

sorb

ance

diff

eren

ce

17

Outline

• Lab Reactor Experiments

• DRIFT Experiments

• Hydrocarbon Storage & Inhibition Modeling

• Conclusions & Future Work

18

Overview of PNNL 1-D SCR Model• Gas phase, surface phase concentrations and NH3 storage as states

• Coded as ‘C’ S-functions and developed in Matlab/Simulink

• Optimized and validated using steady state and thermal transient reactor data

19

Hydrocarbon Storage Model: Toluene

totalHCstotaleqst NcTKNn87,, )(

111+=

dtnnneqt

outHCinHCeqst )(0

,,, 8787∫ −=

Typical Adsorption Test

Langmuir Isotherms

Test Matrix

Storage rate parameters are obtained through approximation of Langmuir isotherms.

20

Single Site Kinetics Model for HC Storage

( )

( )

)(1

)1( ,,,,

,,,,

desadstol

jjiisiggi

is

isiggiigig

rrdt

d

rccAt

c

ccAx

cu

tc

−Ω

=

+−=∂

∂−

−−∂

∂−=

∑θ

βε

βεε

• Simulated using a variable step solver ode23tb, a TR-BDF2 algorithm

• Spatial derivative term approximated by a first order Euler integration scheme

• A total of 10 tanks (cells or axial increments) considered in series, each represented by a ‘C’ s-function and implemented in Matlab/Simulink

Validation at 150ppm, 100C

21

Modeling HC Inhibition of NO OxidationFeed: 350 ppm NO, 14% O2, 25 ppm toluene (175 C1)

Step Temperature Test

Arrhenius Plot for rate parameter (Ktol)

Model Validation on Temperature Ramps

Rate parameter (Ktol) for the inhibition model, follows Arrhenius dependency. It is calculated from steady state data and validated on temperature ramp tests.

tol

toltol

eq

NOoNOoxif

K

Kc

cckr

θθ−

+

=

11

)( 2

2

5.0,

22

Conclusions• Effects of hydrocarbons on NOx reduction pathways over

Fe-zeolite catalyst has been investigated.No effect of ethylene and propane on NOx reduction

Detrimental effects of toluene and n-dodecane on Standard SCR through suppressed NO oxidation

Increased surface NH3 due to suppressed SCR

HC poisoning irreversible at low temps

• 1-D model has been developed to describe the effects of hydrocarbons on SCR reaction kinetics.HC storage model developed using Langmuir isotherms

A single site kinetic model developed and validated to predict the effects of toluene & dodecane on NO oxidation and SCR reaction

23

Next Steps

• Investigate the competitive adsorption kinetics (NH3, H2O, HC) on Cu-zeolite SCR catalysts through experiments and modeling.

• Investigate the effects of catalyst aging on kinetic parameters and physicochemical properties of Cu-zeolite catalysts, and develop a catalyst aging model.

24

Acknowledgments

• Ken Howden and Gurpreet Singh, DOE-OVT

• CLEERS Team

• Kalyan Chakravarthy (ORNL)

• Umicore


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