nitrogen oxides (no x )

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

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Nitrogen Oxides (NO x ). Chapter 12 Page 147-168. NO x emissions include:. Nitric oxide, NO, and Nitrogen dioxide, NO 2 , are normally categorized as NO x Nitrous oxide, N 2 O, is a green house gas (GHG) and receives special attention. Smog precursors:. - PowerPoint PPT Presentation

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Page 1: Nitrogen Oxides (NO x )

Nitrogen Oxides (NOx)

Chapter 12

Page 147-168

Page 2: Nitrogen Oxides (NO x )

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: Nitrogen Oxides (NO x )

Smog precursors:

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

smog calphotochemi O VOCs NOozone level Ground

3Sunlight

x

Page 4: Nitrogen Oxides (NO x )

“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: Nitrogen Oxides (NO x )

NOx reaction mechanisms:

NO O 2

1 N

2

122

• highly endothermic with hf = +90.4 kJ/mol

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

Page 6: Nitrogen Oxides (NO x )

Zeldovich mechanism (1946):

N NO O N

1-

1

k

k

2

O NO O N

2-

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: Nitrogen Oxides (NO x )

N NO O N

1-

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: Nitrogen Oxides (NO x )

Combine Zeldovich mechanism with

H O OH O 2

4-k

4k

To obtain

]OH[k ]O[k

]NO[k 1

]O[k

]NO[kk - ]N[k

[O] 2 dt

d[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: Nitrogen Oxides (NO x )

“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: Nitrogen Oxides (NO x )

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: Nitrogen Oxides (NO x )

Example of proposed reaction pathway for fuel-rich hydrocarbon flames

Page 12: Nitrogen Oxides (NO x )

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: Nitrogen Oxides (NO x )

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: Nitrogen Oxides (NO x )

SCR process:

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

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

Page 15: Nitrogen Oxides (NO x )

SNCR process:

4 NH3 + 6 NO 5 N2 + 6 H2O

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

Page 16: Nitrogen Oxides (NO x )

Low NOX burners:

Dilute combustion technology

Page 17: Nitrogen Oxides (NO x )

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: Nitrogen Oxides (NO x )

• 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: Nitrogen Oxides (NO x )

A conventional burner

Lance Air

FuelGas

Combustion Air

Page 20: Nitrogen Oxides (NO x )

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: Nitrogen Oxides (NO x )

Strong-jet/Weak-jet Aerodynamics

•Strong jet = oxidant

•Weak jet = fuel

Page 22: Nitrogen Oxides (NO x )

Strong-jet/Weak-jet aerodynamics

Page 23: Nitrogen Oxides (NO x )

CGRI burner

Pilot burner portUV scanner port

Fuel nozzle

Air/oxidant nozzle

Page 24: Nitrogen Oxides (NO x )

• 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: Nitrogen Oxides (NO x )

Queen’s test facility

Page 26: Nitrogen Oxides (NO x )

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: Nitrogen Oxides (NO x )

CGRI burner in operation at 1100OC

Page 28: Nitrogen Oxides (NO x )

CFD rendering of the fuel flow pattern

Page 29: Nitrogen Oxides (NO x )

CGRI burner performance (1100OC)

Page 30: Nitrogen Oxides (NO x )

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: Nitrogen Oxides (NO x )

NOx emissions as a function of oxygen enrichment

2

2

2 2

OO

O O A

m 100

m + m

Page 32: Nitrogen Oxides (NO x )

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

Page 33: Nitrogen Oxides (NO x )

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: Nitrogen Oxides (NO x )

NOx emissions as a function of furnace N2 concentration

Page 35: Nitrogen Oxides (NO x )

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: Nitrogen Oxides (NO x )

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: Nitrogen Oxides (NO x )

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