(Redirected from NOx)
The term 'nitrogen oxide' is used to refer to any of these
oxygen compounds of
nitrogen, or to a mixture of them:
★
Nitric oxide (NO), nitrogen(II) oxide
★
Nitrogen dioxide (NO
2), nitrogen(IV) oxide
★
Nitrous oxide (N
2O)
★
Dinitrogen trioxide (N
2O
3), nitrogen(II, IV) oxide
★
Dinitrogen tetroxide (N
2O
4), nitrogen(IV) oxide
★
Dinitrogen pentoxide (N
2O
5), nitrogen(V) oxide
(Note that the last three are unstable.)
Chemical reactions that produce nitrogen oxides often produce several, the proportions depending on the specific reaction and conditions. This is one reason why
domestic production of N
2O is undesirable; the other two stable oxides — which are extremely toxic — are liable to be produced.
NOx
'NO
x' is a generic term for mono-nitrogen oxides (NO and NO
2). These oxides are produced during
combustion, and are of interest as air pollution. They are believed to aggravate
asthmatic conditions, and are involved in
tropospheric production of
ozone.
[1] They eventually form
nitric acid when dissolved in atmospheric moisture, forming a component of
acid rain.
If
nitric oxide (NO) is in the presence of excess
oxygen (O
2) then it will be converted to
nitrogen dioxide (NO
2) depending on the concentration of air as shown below:
| NO concentration in air(ppm) | Time required for half NOto be oxidized to NO2 (min) |
|---|
| 10,000 | 0.175 |
| 20,000 | 0.35 |
| 1,000 | 3.5 |
| 100 | 35 |
| 10 | 350 |
| 1 | 3500 |
[2]
The following chemical reaction occurs when nitrogen dioxide reacts with water:
2NO
2 + H
2O → HNO
2 + HNO
3
Nitrogen dioxide + water → nitrous acid + nitric acid
Nitrous acid then decomposes as follows:
HNO
2 → HNO
3 + 2NO + H
2
Nitrous acid → nitric acid + nitrogen oxide + water
Where
nitric oxide will
oxidize to form nitrogen dioxide again reacting with water ultimately forming
nitric acid 4NO + 3O
2 + 2H
2O → 4HNO
3, nitric oxide + oxygen + water → nitric acid
[3]
In an
internal combustion engine, a mixture of air and fuel is burned. When the mixture is tuned so as to consume every molecule of
reactant (in this case fuel and
oxygen) it is said to be "running at
stoichiometry". When this burns, combustion temperatures reach a high enough level to drive endothermic reactions between
nitrogen and
oxygen in the flame, yielding various
oxides of
nitrogen, the results of which can be seen over major cities such as
Los Angeles,
California in the summer in the form of brown clouds of
smog.
Not to be confused with the term NOS which is used to refer to
nitrous oxide in the context of its use as a booster for internal combustion engines.
Definition of NOx and NOy in atmospheric chemistry
In
atmospheric chemistry the term NO
x is used to mean the total concentration of
NO plus
NO2. During daylight NO and NO
2 are in equilibrium with the ratio NO/NO
2 determined by the intensity of sunshine (which converts NO
2 to NO) and ozone (which reacts with NO to give back NO
2). NO and NO
2 are also central to the formation of
tropospheric ozone. This definition excludes other oxides of nitrogen such as Nitrous Oxide. NO
y (reactive odd nitrogen) is defined as the sum of NO
x plus the compounds produced from the oxidation of NO
x which include
nitric acid,
peroxyacetyl nitrate. In this context nitrous oxide and
ammonia are not considered as reactive nitrogen compounds.
Industrial sources of NOx
The three primary sources of NO
x in
combustion processes:
★ thermal NO
x
★ fuel NO
x
★ prompt NO
x
Thermal NO
x formation, which is highly temperature dependent, is recognized as the most relevant source when combusting natural gas. Fuel NO
x tends to dominate during the combustion of fuels, such as coal, which have a significant nitrogen content, particularly when burned in combustors designed to minimise thermal NO
x. The contribution of prompt NO
x is normally considered negligible. A fourth source, called ''feed NO
x'' is associated with the combustion of nitrogen present in the feed material of cement rotary kilns, at between 300° and 800°C, where it is also a minor contributor.
Thermal NOx
Thermal NO
x refers to NO
x formed through high temperature oxidation of the diatomic nitrogen found in combustion air. The formation rate is primarily a function of temperature and the
residence time of nitrogen at that temperature. At high temperatures, usually above 1600°C (2900°F), molecular nitrogen (N
2) and oxygen (O
2) in the combustion air disassociate into their atomic states and participate in a series of reactions.
The three principal reactions producing thermal NO
x are:
(Extended
Zeldovich Mechanism)
★ 'N
2 + O → NO + N'
★ 'N + O
2 → NO + O'
★ 'N + OH → NO + H'
all 3 reactions are reversible. Zeldovich was the first to suggest the importance of the first two reactions. The last reaction of atomic Nitrogen with Hydroxyl radical, OH, was added by Lavovie, Heywood and Keck to the mechanism and makes a significiant contribution to the formation of thermal NO
x.
Fuel NOx
The major source of NO
x production from nitrogen-bearing fuels such as certain coals and oil, is the conversion of fuel bound nitrogen to NO
x during combustion. During combustion, the nitrogen bound in the fuel is released as a
free radical and ultimately forms free N
2, or NO. Fuel NO
x can contribute as much as 50% of total emissions when combusting oil and as much as 80% when combusting coal.
Although the complete mechanism is not fully understood, there are two primary paths of formation. The first involves the oxidation of volatile nitrogen species during the initial stages of combustion. During the release and prior to the oxidation of the volatiles, nitrogen reacts to form several intermediaries which are then oxidized into NO. If the volatiles evolve into a reducing atmosphere, the nitrogen evolved can readily be made to form nitrogen gas, rather than NO
x. The second path involves the combustion of nitrogen contained in the char matrix during the combustion of the
char portion of the fuels. This reaction occurs much more slowly than the volatile phase. Only around 20% of the char nitrogen is ultimately emitted as NO
x, since much of the NO
x that forms during this process is reduced to nitrogen by the char, which is nearly pure carbon.
Prompt NOx
This third source is attributed to the reaction of atmospheric nitrogen, N
2, with radicals such as C, CH, and CH
2 fragments derived from fuel, where this cannot be explained by either the aforementioned thermal or fuel processes. Occurring in the earliest stage of combustion, this results in the formation of fixed species of nitrogen such as NH (
nitrogen monohydride), HCN (
hydrogen cyanide), H
2CN (
dihydrogen cyanide) and CN- (
cyano radical) which can oxidize to NO. In fuels that contain nitrogen, the incidence of prompt NO
x is especially minimal and it is generally only of interest for the most exacting emission targets.
Regulation and emission control technologies
The
United States Environmental Protection Agency (EPA) regulates and enforces NO
x emission limits in the U.S. in accordance to legislation passed by the
United States Congress. The
Kyoto Protocol, ratified by 54 nations in 1997, calls for a substantial world wide reduction of
greenhouse gases including nitrous oxide.
Technologies such as
flameless oxidation (
FLOX®) and
staged combustion significantly reduce thermal NO
x in industrial processes.
Bowin low NOx technology is a hybrid of staged-premixed-radiant combustion technology with a major surface combustion preceded by a minor radiant combustion. In the
Bowin burner, air and fuel gas are premixed at a ratio greater than or equal to the stoichiometric combustion requirement.
[4] Water Injection technology, wherby water is introduced into the combustion chamber, is also becoming an important means of NO
x reduction through increased efficiency in the overall combustion process. Alternatively, the water (e.g. 10 to 50%) is emulsified into the fuel oil prior to the injection and combustion. This emulsification can either be made in-line (unstabilized) just before the injection or as a drop-in fuel with chemical additives for long term emulsion stability (stabilized). Other technologies, such as
selective catalytic reduction (SCR) and
selective non-catalytic reduction (SNCR) reduce post combustion NOx. Of particular importance is the introduction of
catalytic converters which have significantly
reduced emissions from motor vehicles.
Biogenic sources
Agricultural fertilization and the use of
nitrogen fixing plants have also contributed to increases in atmospheric NO
''x'' through promoting
nitrogen fixation by microorganisms.
[5][6]
References
1.
The atmospheric budget of oxidized nitrogen and its role in ozone formation and deposition, D. Fowler, ''et al.'', , , New Phytologist, 1998
2. Nox
3. Process Design Technical Note
4. Bob Joynt & Stephen Wu, ''Nitrogen oxides emissions standards for domestic gas appliances background study'' Combustion Engineering Consultant; February 2000
5.
Nitrogen cycles: past, present, and future, J.N. Galloway, ''et al.'', , , Biogeochemistry, 2004
6.
A global inventory of nitric oxide emissions from soils, E.A. Davidson & W. Kingerlee, , , Nutrient Cycling in Agroecosystems, 1997
★
Fire and ICE: Revving Up for H2, Adrian Cho, , , Science, 2004
★ Seinfeld, John H.; Pandis, Spyros N (1998). Atmospheric Chemistry and Physics - From Air Pollution to Climate Change. John Wiley and Sons, Inc. ISBN 0-471-17816-0
★
NOx Formation Literature Review and Research Project, Jack Ponton; Department of Chemical Engineering; School of Engineering and Electronics; Edinburgh, UK
★
FACT SHEET #2; NOx Formation and Control in Cement Rotary Kilns (html) (
MS Word doc), Southern Illinois University at Edwardsville
★
Prompt NOx definition, boiler glossary, McKenzie Corporation
See also
★
Criteria air contaminants
External links
★
Australia's Nitrogen oxides emissions standards for domestic gas appliances - background study
★
Australia's National Pollutant Inventory - Oxides of nitrogen Fact Sheet
★
in-line emulsification of water with oil for NOx reduction
★
NASA report on non combustion NOx in atmosphere