نیتروژن دیاکسید (به انگلیسی: Nitrogen dioxide) با فرمول شیمیاییNO۲• یک ترکیب شیمیایی با شناسه پابکم ۳۰۳۲۵۵۲ است. که جرم مولی آن ۴۶٫۰۰۵۵ g/mol میباشد. این گاز در دمای معمولی زرد و در دماهای بالاتر به رنگ قهوهای سرخفام(خرمایی رنگ) است و سمی و بویی بسیار تند و زننده دارد.
دیاکسید نیتروژن از مهمترین آلایندههای هوا به شمار می رود. هر سال میلیونها تن از این گاز در اثر فعالیتهای انسانی به ویژه مصرف سوختهای فسیلی تولید میشود. دیاکسید نیتروژن در ترکیب با هوای مرطوب تولید اسید نیتریک میکند که موجب پوسیدگی شدید فلزات میشود. همچنین در غلظتهای بالا باعث ایجاد مهدود شده و میدان دید را به شدت کاهش میدهد و بر رشد گیاهان اثر منفی شدید دارد. این گاز از اثر گلخانهای نیز برخوردار است.
Nitrogen dioxide at -196°C, 0°C, 23°C, 35°C, 50°C (-321°F, 32°F, 73.4°F, 95°F, 122°F).
(NO 2) converts to the colorless dinitrogen tetroxide (N 2O 4) at low temperatures, and reverts to NO 2 at higher temperatures.
Nitrogen dioxide is a reddish-brown gas above 21.2 °C (70.2 °F; 294.3 K) with a pungent, acrid odor, becomes a yellowish-brown liquid below 21.2 °C (70.2 °F; 294.3 K), and converts to the colorless dinitrogen tetroxide (N 2O 4) below −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 groundelectronic 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 (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 O atom so formed to O2 results in ozone formation.
Preparation and reactions
Nitrogen dioxide typically arises via the oxidation of nitric oxide by oxygen in air:
The equilibrium is characterized by ΔH = −57.23 kJ/mol, which is exothermic. NO2 is favored at higher temperatures, while at lower temperatures, dinitrogen tetroxide (N2O4) predominates. Dinitrogen tetroxide (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.
The chemistry of nitrogen dioxide has been investigated extensively. At 150 °C, NO 2 decomposes with release of oxygen via an endothermic process (ΔH = 14 kJ/mol):
2 NO 2 → 2 NO + 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, with many compounds, such as hydrocarbons.
This reaction is one step 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.
Formation from decomposition of nitric acid
Nitric acid decomposes slowly to nitrogen dioxide by the overall reaction:
4 HNO 3 → 4 NO 2 + 2 H 2O + O 2
The nitrogen dioxide so formed confers the characteristic yellow color often exhibited by this acid.
Conversion to nitrates
NO 2 is used to generate anhydrous metal nitrates from the oxides:
MO + 3 NO 2 → M(NO 3) 2 + NO
Conversion to nitrites
Alkyl and metal iodides give the corresponding nitrites:
2 CH 3I + 2 NO 2 → 2 CH 3NO 2 + I 2
TiI 4 + 4 NO 2 → Ti(NO 2) 4 + 2 I 2
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.
Pathways indicated by a dotted line are those for which evidence is limited to findings from experimental animal studies, while evidence from controlled human exposure studies is available for pathways indicated by a solid line. Dashed lines indicate proposed links to the outcomes of asthma exacerbation and respiratory tract infections. Key events are subclinical effects, endpoints are effects that are generally measured in the clinic, and outcomes are health effects at the organism level. NO2 = nitrogen dioxide; ELF = epithelial lining fluid.:4–62
Nitrogen dioxide diffusion tube for air quality monitoring. Positioned in the City of London
Acute harm due to NO 2 exposure is only likely to arise in occupational settings. Direct exposure to the skin can cause irritations and burns. Only very high concentrations of the gaseous form cause immediate distress: 10–20 ppm can cause mild irritation of the nose and throat, 25–50 ppm can cause edema, leading to bronchitis or pneumonia, and levels above 100 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.
For the public, chronic exposure to NO 2 can cause respiratory effects including airway inflammation in healthy people and increased respiratory symptoms in people with asthma. NO 2 creates ozone which causes eye irritation and exacerbates respiratory conditions, leading to increased visits to emergency departments and hospital admissions for respiratory issues, especially asthma.
The effects of toxicity on health have been examined using questionnaires and inperson 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 from 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.
Avoiding NO 2 toxicity
While using a gas stove, it is advised to also use ventilation. Studies show that in homes with gas stoves, if ventilation is used while using gas stoves, then children have lower odds of asthma, wheezing and bronchitis as compared to children in homes that never used ventilation. If venting isn't possible, then replacing gas stoves with electric stove could be another option. Replacing gas stoves with electric ranges could greatly reduce the exposure to indoor NO2 and improve the respiratory function of children with asthma. It is important to keep gas stoves and heaters in good repair so they are not polluting extra NO2. 2015 International Residential Code that requires that vent hoods are used for all stoves and set standards for residential buildings. This requires that all range hoods have a vent that discharges outside. You can also prevent NO2 exposure by avoiding cigarette smoking and not idling your car whenever possible.
The U.S. EPA has set safety levels for environmental exposure to NO 2 at 100 ppb, averaged over one hour, and 53 ppb, averaged annually. As of February 2016, no area of the US was out of compliance with these limits and concentrations ranged between 10–20 ppb, and annual average ambient NO2 concentrations, as measured at area-wide monitors, have decreased by more than 40% since 1980.
However, NO 2 concentrations in vehicles and near roadways are appreciably higher than those measured at monitors in the current network. In fact, in-vehicle concentrations can be 2–3 times higher than measured at nearby area-wide monitors. Near-roadway (within about 50 metres (160 ft)) concentrations of NO2 have been measured to be approximately 30 to 100% higher than concentrations away from roadways. Individuals who spend time on or near major roadways can experience short-term NO2 exposures considerably higher than measured by the current network. Approximately 16% of U.S. housing units are located within 300 feet (91 m) of a major highway, railroad, or airport (approximately 48 million people). Studies show a connection between breathing elevated short-term NO2 concentrations, and increased visits to emergency departments and hospital admissions for respiratory issues, especially asthma. NO2 exposure concentrations near roadways are of particular concern for susceptible individuals, including asthmatics, children, and the elderly.
^Mendiara, S. N.; Sagedahl, A.; Perissinotti, L. J. (2001). "An electron paramagnetic resonance study of nitrogen dioxide dissolved in water, carbon tetrachloride and some organic compounds". Applied Magnetic Resonance. 20 (1–2): 275–287. doi:10.1007/BF03162326.
^ abcHolleman, A. F.; Wiberg, E. (2001) Inorganic Chemistry. Academic Press: San Diego. ISBN0-12-352651-5.
^Thiemann, Michael; Scheibler, Erich and Wiegand, Karl Wilhelm (2005). "Nitric Acid, Nitrous Acid, and Nitrogen Oxides". Ullmann's Encyclopedia of Industrial Chemistry. Ullmann’s Encyclopedia of Industrial Chemistry. Weinheim: Wiley-VCH. doi:10.1002/14356007.a17_293. ISBN978-3527306732.CS1 maint: uses authors parameter (link)
^Subcommittee on Emergency and Continuous Exposure Guidance Levels for Selected Submarine Contaminants; Committee on Toxicology; Board on Environmental Studies and Toxicology; Division on Earth and Life Studies; National Research Council. Chapter 12: Nitrogen Dioxide in Emergency and Continuous Exposure Guidance Levels for Selected Submarine Contaminants. National Academies Press, 2007. ISBN978-0-309-09225-8
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^ abGarrett, Maria H.; Hooper, Martin A.; Hooper, Beverley M.; Abramson, Michael J. (1998-09-01). "Respiratory Symptoms in Children and Indoor Exposure to Nitrogen Dioxide and Gas Stoves". American Journal of Respiratory and Critical Care Medicine. 158 (3): 891–895. doi:10.1164/ajrccm.158.3.9701084. PMID9731022.
^Chapman, Robert S.; Hadden, Wilbur C.; Perlin, Susan A. (2003-07-15). "Influences of asthma and household environment on lung function in children and adolescents: the third national health and nutrition examination survey". American Journal of Epidemiology. 158 (2): 175–189. doi:10.1093/aje/kwg129. PMID12851231.