| |||
NO
2 converts to the colorless dinitrogen tetroxide (N 2O 4) at low temperatures and reverts to NO 2 at higher temperatures. | |||
| Names | |||
|---|---|---|---|
|
IUPAC name
Nitrogen dioxide
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| Other names
Nitrogen(IV) oxide, deutoxide of nitrogen
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| Identifiers | |||
|
3D model (JSmol)
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| ChEBI | |||
| ChemSpider | |||
| ECHA InfoCard | 100.030.234 | ||
| EC Number |
|
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| 976 | |||
|
PubChem CID
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| RTECS number |
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| UNII | |||
| UN number | 1067 | ||
|
CompTox Dashboard (EPA)
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| Properties | |||
| NO• 2 |
|||
| Molar mass | 46.006 g/mol | ||
| Appearance | Brown gas | ||
| Odor | Chlorine-like | ||
| Density | 1.880 g/L | ||
| Melting point | −9.3 °C (15.3 °F; 263.8 K) | ||
| Boiling point | 21.15 °C (70.07 °F; 294.30 K) | ||
| Hydrolyses | |||
| Solubility | Soluble in CCl 4, nitric acid,chloroform |
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| Vapor pressure | 98.80 kPa (at 20 °C) | ||
| +150.0·10−6 cm3/mol | |||
|
Refractive index (nD)
|
1.449 (at 20 °C) | ||
| Structure | |||
| C2v | |||
| Bent | |||
| Thermochemistry | |||
|
Heat capacity (C)
|
37.2 J/(mol·K) | ||
|
Std molar
entropy (S⦵298) |
240.1 J/(mol·K) | ||
|
Std enthalpy of
formation (ΔfH⦵298) |
+33.2 kJ/mol | ||
| Hazards | |||
| Occupational safety and health (OHS/OSH): | |||
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Main hazards
|
Poison, oxidizer | ||
| GHS labelling: | |||
    
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| Danger | |||
| H270, H314, H330 | |||
| P220, P260, P280, P284, P305+P351+P338, P310 | |||
| NFPA 704 (fire diamond) | |||
| Lethal dose or concentration (LD, LC): | |||
|
LC50 (median concentration)
|
30 ppm (guinea pig, 1 h) 315 ppm (rabbit, 15 min) 68 ppm (rat, 4 h) 138 ppm (rat, 30 min) 1000 ppm (mouse, 10 min) |
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LCLo (lowest published)
|
64 ppm (dog, 8 h) 64 ppm (monkey, 8 h) |
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| NIOSH (US health exposure limits): | |||
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PEL (Permissible)
|
C 5 ppm (9 mg/m3) | ||
|
REL (Recommended)
|
ST 1 ppm (1.8 mg/m3) | ||
|
IDLH (Immediate danger)
|
13 ppm | ||
| Safety data sheet (SDS) | ICSC 0930 | ||
| Related compounds | |||
|
Related nitrogen oxides
|
Dinitrogen pentoxide Dinitrogen tetroxide |
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Related compounds
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Chlorine dioxide Carbon dioxide |
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Except where otherwise noted, data are given for materials in their standard state (at 25 °C [77 °F], 100 kPa).
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Nitrogen dioxide is a chemical compound with the formula NO
2. It is one of several nitrogen oxides. NO
2 is an intermediate in the industrial synthesis of nitric acid, millions of tons of which are produced each year for use primarily in the production of fertilizers. At higher temperatures it is a reddish-brown gas. It can be fatal if inhaled in large quantities. Nitrogen dioxide is a paramagnetic, bent molecule with C2vpoint group symmetry.
It is included in the NOx family of atmospheric pollutants.
Properties
Nitrogen dioxide is a reddish-brown gas with a pungent, acrid odor above 21.2 °C (70.2 °F; 294.3 K) and becomes a yellowish-brown liquid below 21.2 °C (70.2 °F; 294.3 K). It forms an equilibrium with its dimer, dinitrogen tetroxide (N
2O
4), and converts almost entirely to N
2O
4below −11.2 °C (11.8 °F; 261.9 K).
The bond length between the nitrogen atom and the oxygen atom is 119.7 pm. This bond length is consistent with a bond order between one and two.
Unlike ozone, O3, the ground electronic state of nitrogen dioxide is a doublet state, since nitrogen has one unpaired electron, which decreases the alpha effect compared with nitrite and creates a weak bonding interaction with the oxygen lone pairs. The lone electron in NO
2 also means that this compound is a free radical, so the formula for nitrogen dioxide is often written as •NO
2.
The reddish-brown color is a consequence of preferential absorption of light in the blue region of the spectrum (400 – 500 nm), although the absorption extends throughout the visible (at shorter wavelengths) and into the infrared (at longer wavelengths). Absorption of light at wavelengths shorter than about 400 nm results in photolysis (to form NO + O, atomic oxygen); in the atmosphere the addition of the oxygen atom so formed to O2 results in ozone.
Preparation
Nitrogen dioxide typically arises via the oxidation of nitric oxide by oxygen in air (e.g. as result of corona discharge):
- NO + 1⁄2 O
2 → NO
2
Nitrogen dioxide is formed in most combustion processes using air as the oxidant. At elevated temperatures nitrogen combines with oxygen to form nitrogen dioxide:
-
1⁄2 N
2 + O
2 → NO
2
In the laboratory, NO
2 can be prepared in a two-step procedure where dehydration of nitric acid produces dinitrogen pentoxide:
- 2 HNO3 → N2O5 + H2O
- 6 HNO
3 + 1⁄2 P
4O
10 → 3 N
2O
5 + 2 H
3PO
4
which subsequently undergoes thermal decomposition:
-
N
2O
5 → 2 NO
2 + 1⁄2 O
2
The thermal decomposition of some metal nitrates also generates NO
2:
-
Pb(NO
3)
2 → PbO + 2 NO
2 + 1⁄2 O
2
NO
2 is generated by the reduction of concentrated nitric acid with a metal (such as copper):
- 4 HNO3 + Cu → Cu(NO3)2 + 2 NO2 + 2 H2O
Formation from decomposition of nitric acid
Nitric acid decomposes slowly to nitrogen dioxide by the overall reaction:
-
2 HNO3 → 2 NO2 + H2O + 1⁄2 O
2
The nitrogen dioxide so formed confers the characteristic yellow color often exhibited by this acid.
Selected reactions
Thermal properties
NO
2 exists in equilibrium with the colourless gas dinitrogen tetroxide (N
2O
4):
- 2 NO
2 ⇌ N
2O
4
The equilibrium is characterized by ΔH = −57.23 kJ/mol, which is exothermic. NO2 is favored at higher temperatures, while at lower temperatures, N2O4 predominates. N
2O
4 can be obtained as a white solid with melting point −11.2 °C. NO2 is paramagnetic due to its unpaired electron, while N2O4 is diamagnetic.
At 150 °C, NO
2 decomposes with release of oxygen via an endothermic process (ΔH = 14 kJ/mol):
-
NO
2 → NO + 1⁄2 O
2
As an oxidizer
As suggested by the weakness of the N–O bond, NO
2 is a good oxidizer. Consequently, it will combust, sometimes explosively, in the presence of hydrocarbons.
Hydrolysis
NO2reacts with water to give nitric acid and nitrous acid:
- 2 NO2 + H2O → HNO2 + HNO3
This reaction is one of the steps in the Ostwald process for the industrial production of nitric acid from ammonia. This reaction is negligibly slow at low concentrations of NO2 characteristic of the ambient atmosphere, although it does proceed upon NO2 uptake to surfaces. Such surface reaction is thought to produce gaseous HNO2 (often written as HONO) in outdoor and indoor environments.
Conversion to nitrates
NO
2 is used to generate anhydrous metal nitrates from the oxides:
- MO + 3 NO
2 → M(NO
3)
2 + NO
Alkyl and metal iodides give the corresponding nitrates:
- TiI4 + 8 NO2 → Ti(NO3)4 + 4 NO + 2 I2
Ecology
NO
2 is introduced into the environment by natural causes, including entry from the stratosphere, bacterial respiration, volcanos, and lightning. These sources make NO
2 a trace gas in the atmosphere of Earth, where it plays a role in absorbing sunlight and regulating the chemistry of the troposphere, especially in determining ozone concentrations.
Uses
NO
2 is used as an intermediate in the manufacturing of nitric acid, as a nitrating agent in the manufacturing of chemical explosives, as a polymerization inhibitor for acrylates, as a flour bleaching agent, and as a room temperature sterilization agent. It is also used as an oxidizer in rocket fuel, for example in red fuming nitric acid; it was used in the Titan rockets, to launch Project Gemini, in the maneuvering thrusters of the Space Shuttle, and in uncrewed space probes sent to various planets.
Human-caused sources and exposure
For the general public, the most prominent sources of NO
2 are internal combustion engines, as combustion temperatures are high enough to thermally combine some of the nitrogen and oxygen in the air to form NO
2. Outdoors, NO
2 can be a result of traffic from motor vehicles.
Indoors, exposure arises from cigarette smoke, and butane and kerosene heaters and stoves.
Workers in industries where NO
2 is used are also exposed and are at risk for occupational lung diseases, and NIOSH has set exposure limits and safety standards. Workers in high voltage areas especially those with spark or plasma creation are at risk.Agricultural workers can be exposed to NO
2 arising from grain decomposing in silos; chronic exposure can lead to lung damage in a condition called "silo-filler's disease".
Toxicity
NO
2 diffuses into the epithelial lining fluid (ELF) of the respiratory epithelium and dissolves. There, it chemically reacts with antioxidant and lipid molecules in the ELF. The health effects of NO
2 are caused by the reaction products or their metabolites, which are reactive nitrogen species and reactive oxygen species that can drive bronchoconstriction, inflammation, reduced immune response, and may have effects on the heart.
Acute harm due to NO
2 exposure is rare. 100–200 ppm can cause mild irritation of the nose and throat, 250–500 ppm can cause edema, leading to bronchitis or pneumonia, and levels above 1000 ppm can cause death due to asphyxiation from fluid in the lungs. There are often no symptoms at the time of exposure other than transient cough, fatigue or nausea, but over hours inflammation in the lungs causes edema.
For skin or eye exposure, the affected area is flushed with saline. For inhalation, oxygen is administered, bronchodilators may be administered, and if there are signs of methemoglobinemia, a condition that arises when nitrogen-based compounds affect the hemoglobin in red blood cells, methylene blue may be administered.
It is classified as an extremely hazardous substance in the United States as defined in Section 302 of the U.S. Emergency Planning and Community Right-to-Know Act (42 U.S.C. 11002), and it is subject to strict reporting requirements by facilities which produce, store, or use it in significant quantities.
Health effects of NO
2 exposure
Even small day-to-day variations in NO
2 can cause changes in lung function.
Chronic exposure to NO
2 can cause respiratory effects including airway inflammation in healthy people and increased respiratory symptoms in people with asthma.
The effects of toxicity on health have been examined using questionnaires and in-person interviews in an effort to understand the relationship between NO
2 and asthma. The influence of indoor air pollutants on health is important because the majority of people in the world spend more than 80% of their time indoors. The amount of time spent indoors depends upon on several factors including geographical region, job activities, and gender among other variables. Additionally, because home insulation is improving, this can result in greater retention of indoor air pollutants, such as NO
2. With respect to geographic region, the prevalence of asthma has ranged from 2 to 20% with no clear indication as to what's driving the difference. This may be a result of the "hygiene hypothesis" or "western lifestyle" that captures the notions of homes that are well insulated and with fewer inhabitants. Another study examined the relationship between nitrogen exposure in the home and respiratory symptoms and found a statistically significant odds ratio of 2.23 (95% CI: 1.06, 4.72) among those with a medical diagnosis of asthma and gas stove exposure.
A major source of indoor exposure to NO
2 is the use of gas stoves for cooking or heating in homes. According to the 2000 census, over half of US households use gas stoves and indoor exposure levels of NO
2 are, on average, at least three times higher in homes with gas stoves compared to electric stoves with the highest levels being in multifamily homes. Exposure to NO
2 is especially harmful for children with asthma. Research has shown that children with asthma who live in homes with gas stoves have greater risk of respiratory symptoms such as wheezing, cough and chest tightness. Additionally, gas stove use was associated with reduced lung function in girls with asthma, although this association was not found in boys. Using ventilation when operating gas stoves may reduce the risk of respiratory symptoms in children with asthma.
In a cohort study with inner-city minority African American Baltimore children to determine if there was a relationship between NO
2 and asthma for children aged 2 to 6 years old, with an existing medical diagnosis of asthma, and one asthma related visit, families of lower socioeconomic status were more likely to have gas stoves in their homes. The study concluded that higher levels of NO
2 within a home were linked to a greater level of respiratory symptoms among the study population. This further exemplifies that NO
2 toxicity is dangerous for children.
Environmental effects
Interaction of NO
2 and other NO
x with water, oxygen and other chemicals in the atmosphere can form acid rain which harms sensitive ecosystems such as lakes and forests. Elevated levels of NO
2 can also harm vegetation, decreasing growth, and reduce crop yields.
See also
- Dinitrogen tetroxide
-
Nitric oxide (NO) – pollutant that is short lived because it converts to NO
2 in the presence of ozone - Nitrite
-
Nitrous oxide (N
2O) – "laughing gas", a linear molecule, isoelectronic with CO
2 but with a nonsymmetric arrangement of atoms (NNO) - Nitryl
Cited sources
- Haynes, William M., ed. (2011). CRC Handbook of Chemistry and Physics (92nd ed.). CRC Press. ISBN 978-1439855119.
External links
- International Chemical Safety Card 0930
- National Pollutant Inventory – Oxides of nitrogen fact sheet
- NIOSH Pocket Guide to Chemical Hazards
- WHO-Europe reports: Health Aspects of Air Pollution (2003) (PDF) and "Answer to follow-up questions from CAFE (2004) (PDF)
- Nitrogen Dioxide Air Pollution
- Current global map of nitrogen dioxide distribution
- A review of the acute and long term impacts of exposure to nitrogen dioxide in the United Kingdom IOM Research Report TM/04/03