Urea Decomposition and SCR Performance at Low … · •It appears that urea decomposition kinetics...

22
1 OAK RIDGE NATIONAL LABORATORY U. S. DEPARTMENT OF ENERGY Urea Decomposition and SCR Performance at Low Temperature Scott Sluder, John Storey, Sam Lewis, Linda Lewis, Oak Ridge National Laboratory 10 th Annual DEER Workshop Coronado, CA September 2, 2004 Sponsors: DOE-OFCVT, Steve Goguen and Kevin Stork

Transcript of Urea Decomposition and SCR Performance at Low … · •It appears that urea decomposition kinetics...

1

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Urea Decomposition and SCR Performance at Low Temperature

Scott Sluder, John Storey, Sam Lewis, Linda Lewis,

Oak Ridge National Laboratory

10th Annual DEER WorkshopCoronado, CA

September 2, 2004

Sponsors: DOE-OFCVT, Steve Goguen and Kevin Stork

2

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Why study urea decomposition?

• Under light-duty conditions (< 250 °C), there is negligible urea decomposition in the gas phase. Current models assume NH3 as input to catalyst.

• It appears that urea decomposition kinetics on catalyst surfaces has to be understood. This will affect the length of the catalyst that is used for urea decomposition.

3

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Urea/SCR Chemistry

Ideally, injected urea decomposes to NH3

2 NH3 + NO + NO2 ⇔ 2 N2 + 3 H2O

O

NH 2 N H 2

HeatNH3 +

H2O, O2

OH C Nisocyanic acid

OH C Nisocyanic acid

Heat

H2ONH3 + CO2

then reacts with NOX to form N2.

4

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Unusual things can happen, such as ammonium nitrate formation and decomposition at T < 200 °C.

2NH3 + 2NO2 →NH4NO3 + N2 + 3 H2O

NH4NO3 ⇔ NH3 + HNO3

2HNO3 + NO → 3 NO2 + H2O

M. Koebel et al. in Ind.Eng.Chem.Res.:39,p. 4120; 40, p. 52; 41, p.4008; 42, p.2093Also in Catal.Today, 73, p.239

5

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Experimental Approach• Use engine controls to:

− Vary temperature − Keep constant: NOX and exhaust flow.

• Investigate urea decomposition (if any)upstream of SCR catalyst.

• Analyze exhaust products exiting undersized monoliths to elucidate urea decomposition− 3” and 6” monoliths = space velocities of 25K and 50K − const. urea residence time in the exhaust stream. (~0.1

sec)− From clean condition, begin injecting urea:Wait 20 minutes (3” monolith) or,40 minutes (6” monolith), Then collect data and samples.

6

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Experiments conducted at NTRC cell 4 using Mercedes engine and BP15 fuel.

Urea

Injector

Oxidation catalyst (beneath engine)

Engine

SCR catalyst

To exhaust stack

7

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Experiments conducted at NTRC using Mercedes engine and BP15 fuel.

Urea

Injector

Oxidation catalyst (beneath engine)

Engine

SCR catalyst

To exhaust stack

3” monolith

8

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Experiments conducted at NTRC cell 4 using Mercedes engine and BP15 fuel.

Urea

Injector

Oxidation catalyst (beneath engine)

Engine

SCR catalyst

To exhaust stack

6” monolith

9

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Measurement of actual NH3 in the presence of urea and isocyanic acid is difficult.

• Problematic if making measurements of urea decomposition products.

• Short experiments showed that urea decomposed (to ammonia) on instrument filter at T as low as 80 °C.

• Filters are required for sampling PM-laden exhaust gas.

• Instrument filter T is typically > 100 °C to prevent condensation and loss of water soluble NH3

• Using 60 °C filter allows measurement of NH3 without decomposition of precursors, but precludes same stream from being used for HC measurements.

10

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Higher T decrease in NOX conversion (for 3”brick) implies competing processes….

0102030405060708090

100

150 170 190 210 230 250 270SCR inlet T (C)

App

aren

t Con

vers

ion

(%)

3 inch SCR6 inch SCR

11

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

The lower conversion of NOX is due at high temperature is due to lower NO2 conversion.

0102030405060708090

100

150 170 190 210 230 250 270SCR inlet T (C)

App

aren

t Con

vers

ion

(%)

3 inch SCR6 inch SCR

12

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Undersized SCRs slipped some NH3 at all conditions, indicating ample reductant available for

NOX reduction.

0

10

20

30

40

50

60

150 170 190 210 230 250 270SCR inlet T (C)

Con

cent

ratio

n (P

PM)

3 inch SCR6 inch SCR

13

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

N2O slip indicates incomplete reduction in the shorter catalyst

05

101520253035404550

150 170 190 210 230 250 270SCR inlet T (C)

Con

cent

ratio

n (P

PM)

3 inch SCR6 inch SCR

14

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

HCN was also formed as an intermediate at low concentrations at the temperatures studied.

0

1

2

3

4

5

6

7

8

9

150 170 190 210 230 250 270SCR inlet T (C)

Con

cent

ratio

n (P

PM)

3 inch SCR6 inch SCR

15

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Steady-state data suggest urea decomposition competes with NOX reduction processes.

• NO2 not converted as efficiently at high temperatures with the 3” SCR.

• High concentration of intermediate N2O in the 3”SCR could account for most NOX disappearance.

• Concentrations of intermediates drop with longer catalyst.

• NH3 slip indicates available reductant.• Temperature gradients associated with urea

decomposition and NOX reduction were too small to measure.

16

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Results from onset of injection

17

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

NO, NO2 disappearance at 250 °C using urea and ammonia as reductants suggests similarity of

reduction processes.

0

20

40

60

80

100

120

140

0 200 400 600 800 1000 1200Time (s)

Con

cent

ratio

n (p

pm)

NO w/ Urea NO2 w/ Urea

NO with NH3 NO2 w/ NH3Injection Starts

18

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Onset of N2O slip and NH3 slip at 250 °C is due to competition of urea decomposition process

0

2

4

6

8

10

12

14

0 200 400 600 800 1000 1200Time (s)

Con

cent

ratio

n (p

pm)

N2O w/Urea NH3 w/UreaN2O w/NH3 NH3 w/NH3

Injection Starts

19

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

NO and NO2 disappearance similar at 180 °C when using urea and ammonia as reductants.

0

40

80

120

160

0 200 400 600 800 1000 1200Time (s)

Con

cent

ratio

n (p

pm)

NO w/ Urea NO2 w/ UreaNO with NH3 NO2 w/ NH3

Injection Starts

20

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Large NH3 slip again occurs much sooner with urea injection than with ammonia injection.

0

5

10

15

0 200 400 600 800 1000 1200Time (s)

Con

cent

ratio

n (p

pm)

N2O w/Urea NH3 w/UreaN2O w/NH3 NH3 w/NH3

Injection Starts

21

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Urea decomposition hampers NOX reduction in at least the first 3” of SCR catalyst.

• Steady state data showed presence of NH3, intermediates downstream of 3” and 6” SCR.

• Transient data showed that NO, NO2 disappearance were similar using both NH3 and urea as reductants.

• Ammonia injection data showed intermediates (HCN, N2O) at ~1/3 of concentration vs. urea

• Ammonia injection data showed longer NH3 storage times before slip (~2X) than when urea was used.

22

OAK RIDGE NATIONAL LABORATORYU. S. DEPARTMENT OF ENERGY

Further investigation of the dynamics of urea decomposition is planned.

• Confirmatory, direct measurements of urea, isocyanic acid downstream of SCR are forthcoming.

• Study 3”+6” SCRs together (as a 9”) to determine whether same trends are observed in rear 3” of 6” monolith.

• Comparisons of urea and ammonia injection at other conditions to confirm