nitrogenoxides nox emissions

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Nitrogen Oxides (NO x ) Chapter 12 Page 147-168

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Page 1: NitrogenOxides NOx Emissions

Nitrogen Oxides (NOx)

Chapter 12Page 147-168

Page 2: NitrogenOxides NOx Emissions

NOx emissions include:

• Nitric oxide, NO, and Nitrogen dioxide, NO2, are normally categorized as NOx

• Nitrous oxide, N2O, is a green house gas (GHG) and receives special attention

Page 3: NitrogenOxides NOx Emissions

Smog precursors:

• NOx, SO2, particulate matter (PM2.5) and volatile organic compounds (VOC).

smog calphotochemi O VOCs NOozone level Ground

3Sunlight

x

Page 4: NitrogenOxides NOx Emissions

“Developing NOx and SOx Emission Limits” – December 2002, Ontario’s Clean Air Plan for Industry

Broad base of sources with close to 50% from the Electricity sector in 1999

Page 5: NitrogenOxides NOx Emissions

NOx reaction mechanisms:

NO O 21 N

21

22

• highly endothermic with hf = +90.4 kJ/mol

• NO formation favoured by the high temperatures encountered in combustion processes

Page 6: NitrogenOxides NOx Emissions

Zeldovich mechanism (1946):

N NO O N1-

1

k

k

2

O NO O N2-

2

k

k

2

H NO OH N3-k

3k

k+1 = 1.8 108 exp{-38,370/T}k-1 = 3.8 107 exp{-425/T}

k+2 = 1.8 104 T exp{-4680/T}k-2 = 3.8 103 T exp{-20,820/T}

k+3 = 7.1 107 exp{-450/T}k-3 = 1.7 108 exp{-24,560/T}

Page 7: NitrogenOxides NOx Emissions

N NO O N1-

1

k

k

2

k+1 = 1.8 108 exp{-38,370/T}k-1 = 3.8 107 exp{-425/T}

Rate-limiting step in the process

K+1 is highly temperature dependent

Page 8: NitrogenOxides NOx Emissions

Combine Zeldovich mechanism with

H O OH O 24-k

4k

To obtain

]OH[k ]O[k]NO[k

1

]O[k]NO[kk

- ]N[k [O] 2

dtd[NO]

322

1-

22

22-1-

21

]N[ [O]k 2 dt

d[NO]2 1If the initial concentrations of [NO]

and [OH] are low and only the forward reaction rates are significant

Modelling NOx emissions is difficult because of the competition for the [O] species in combustion processes

Page 9: NitrogenOxides NOx Emissions

“Prompt” NO mechanism (1971):

N HCN N CH 2

H NO OH N

O NO O N 2

N CO NO O HCN 2

This scheme occurs at lower temperature, fuel-rich conditions and short residence times

Page 10: NitrogenOxides NOx Emissions

Fuel NOx

Organic, fuel bound nitrogen compounds in solid fuels

C-N bond is much weaker than the N-N bond increasing the likelihood of NOx formation

Page 11: NitrogenOxides NOx Emissions

Example of proposed reaction pathway for fuel-rich hydrocarbon flames

Page 12: NitrogenOxides NOx Emissions

NOx control strategies:

• Reduce peak temperatures• Reduce residence time in

peak temperature zones• Reduce O2 content in

primary flame zone

• Low excess air• Staged combustion• Flue gas recirculation• Reduce air preheat• Reduce firing rates• Water injection

Combustion Modification Modified Operating Conditions

Page 13: NitrogenOxides NOx Emissions

Control strategies:

• Reburning – injection of hydrocarbon fuel downstream of the primary combustion zone to provide a fuel-rich region, converting NO to HCN.

• Post-combustion treatment include selective catalytic reduction (SCR) with ammonia injection, or selective noncatalytic reduction (SNCR) with urea or ammonia-based chemical chemical injection to convert NOx to N2.

Page 14: NitrogenOxides NOx Emissions

SCR process:

4 NO + 4 NH3 + O2 4 N2 + 6 H2O

2 NO2 + 4 NH3 + O2 3 N2 + 6 H2O

Page 15: NitrogenOxides NOx Emissions

SNCR process:

4 NH3 + 6 NO 5 N2 + 6 H2O

CO(NH3)2 + 2 NO ½ O2 2 N2 + CO2 + 2 H2O

Page 16: NitrogenOxides NOx Emissions

Low NOX burners:

Dilute combustion technology

Page 17: NitrogenOxides NOx Emissions

Industrial furnace combustion:• Natural gas is arguably “cleanest” fuel – perhaps not

the cheapest.• Independent injection of fuel and oxidant streams

(“non-premixed”). Industrial furnaces have multi-burner operation.

• Traditional thinking has been that a rapid mixing of fuel and oxidant ensures best operation.

• This approach gives high local temperatures in the flame zone with low HC but high NOx emissions.

• Heat transfer to a load in the furnace (radiatively dominated) must be controlled by adjustment of burners.

Page 18: NitrogenOxides NOx Emissions

• High intensity combustion with rapid mixing of fuel and oxidant• High temperature flame zones with low HC but high NOx• Furnace efficiency increased by preheating the oxidant stream

Page 19: NitrogenOxides NOx Emissions

A conventional burner

Lance Air

FuelGas

Combustion Air

Page 20: NitrogenOxides NOx Emissions

Dilute oxygen combustion:• An extreme case of staged-combustion.• Fuel and oxidant streams supplied as separate

injections to the furnace.• Initial mixing of fuel and oxidant with hot combustion

products within the furnace (fuel-rich/fuel-lean jets).• Lower flame temperature (but same heat release)

and more uniform furnace temperature (good heat transfer).

• Low NOx emissions – “single digit ppm levels”

Page 21: NitrogenOxides NOx Emissions

Strong-jet/Weak-jet Aerodynamics

•Strong jet = oxidant

•Weak jet = fuel

Page 22: NitrogenOxides NOx Emissions

Strong-jet/Weak-jet aerodynamics

Page 23: NitrogenOxides NOx Emissions

CGRI burner

Pilot burner portUV scanner port

Fuel nozzle

Air/oxidant nozzle

Page 24: NitrogenOxides NOx Emissions

• Dilute oxygen combustion operation with staged mixing of fuel and oxidant• No visible flame (“flameless” combustion)• More uniform temperature throughout flame and furnace• Low HC and NOx emissions

Page 25: NitrogenOxides NOx Emissions

Queen’s test facility

Page 26: NitrogenOxides NOx Emissions

Queen’s test facility

2750-362 0 750 1750 54624500 5100

1362z

0

1000

500

3000

3362

y

x

-362

0

B2B1 B3

Water-cooled floor panels

SideView

Plenum Wall

FurnaceExhaust

TopView

Page 27: NitrogenOxides NOx Emissions

CGRI burner in operation at 1100OC

Page 28: NitrogenOxides NOx Emissions

CFD rendering of the fuel flow pattern

Page 29: NitrogenOxides NOx Emissions

CGRI burner performance (1100OC)

Page 30: NitrogenOxides NOx Emissions

Oxygen-enriched combustion:

• Oxidant stream supplied with high concentrations of oxygen.

• Nitrogen “ballast” component in the oxidant stream is reduced – less energy requirements and less NOx reactant.

• Conventional oxy-fuel combustion leads to high efficiency combustion but high temperatures and high NOx levels.

• Higher efficiency combustion leads to lower fuel requirements and corresponding reduction in CO2 emissions.

• Does this work with dilute oxygen combustion???

Page 31: NitrogenOxides NOx Emissions

NOx emissions as a function of oxygen enrichment

2

2

2 2

OO

O O A

m 100

m + m

Page 32: NitrogenOxides NOx Emissions

Firing rate as a function of oxygen-enrichment level required to maintain 1100oC furnace temperature

Page 33: NitrogenOxides NOx Emissions

Is oxygen-enrichment a NOx reduction strategy?

• NOx emissions are reduced at high oxygen-enrichment levels … but …

• Only at quite significant enrichment levels, and• With no air infiltration (a source of N2).

Page 34: NitrogenOxides NOx Emissions

NOx emissions as a function of furnace N2 concentration

Page 35: NitrogenOxides NOx Emissions

Capabilities of oxygen-enriched combustion:

• Dilute oxygen combustion systems can work with oxygen-enriched combustion.

• NOx emissions are comparable to air-oxidant operation and NOx reductions are limited by air infiltration.

• NOx emissions also limited by N2 content of the fuel.• Primary benefit is energy conservation (reduced fuel

consumption) and associated CO2 reduction.

Page 36: NitrogenOxides NOx Emissions

Limitations of oxygen-enrichment:

• This is not a totally new technology !!!• Cost of oxygen – high purity O2 is expensive, lower

purity is more feasible in some situations.• Infrastructure costs – oxygen supply and handling.• Furnace modifications – burners, gas handling, etc.

Page 37: NitrogenOxides NOx Emissions

Final Examination• Tuesday, April 22, 1900h• 3rd Floor Ellis Hall• Open book, open notes• Red or gold calculator

CHEE 481 Tutorial Session• Saturday, April 19, 0900h

• Dupuis Hall 217