Nitrogen dioxide poisoning
|Nitrogen dioxide poisoning|
|Classification and external resources|
Nitrogen dioxide poisoning is the illness resulting from the toxic effect of nitrogen dioxide (NO
2). It usually occurs after the inhalation of the gas beyond the threshold limit value. Nitrogen dioxide is reddish-brown with very harsh smell at high concentrations. It is colorless and odorless at lower concentration but still harmful. Nitrogen dioxide poisoning depends on the duration, frequency, and intensity of exposure. Nitrogen dioxide is an irritant of the mucous membrane linked with another air pollutant that causes pulmonary diseases such as OLD, asthma, chronic obstructive pulmonary disease and sometimes acute exacerbation of COPD and in fatal cases, deaths. Its poor solubility in water enhances its passage and its ability to pass through the moist oral mucosa of the respiratory tract. Like most toxic gases, the dose inhaled determines the toxicity on the respiratory tract. Occupational exposures constitute the highest risk of toxicity and domestic exposure is uncommon. Prolonged exposure to low concentration of the gas may have lethal effects, as can short-term exposure to high concentrations like chlorine gas poisoning. It is one of the major air pollutant capable of causing severe heath hazards such as coronary artery disease as well as stroke. Nitrogen dioxide is often released into the environment as a byproduct of fuel combustion but rarely released by spontaneous combustion. Known sources of nitrogen dioxide gas poisoning include automobile exhaust and power stations. The toxicity may also result from non-combustible sources such as the one released from anaerobic fermentation of food grains and anaerobic digestion of biodegradable waste. The World Health Organization (WHO) developed a global recommendation limiting exposures to less than 20 parts per billion for chronic exposure and value less 100 ppb for one hour for acute exposure, using nitrogen dioxide as a marker for other pollutants from fuel combustion. The standards also based on the concentration of nitrogen dioxide that show a significant and profound effects on the function of the pulmonary of asthmatic patients. Historically, some cities in the United States including Chicago and Los Angeles have high levels of nitrogen dioxide but the EPA set a standard values less than 100 ppb for a one-hour exposure and less than 53 ppb for chronic exposure.
Signs and symptoms
Nitrogen dioxide poisoning is not harmful to all forms of life just like "chlorine gas poisoning" and carbon monoxide poisoning. It is easily absorbed through the lungs and its inhalation result in heart failure and sometimes death in severe and cases. Individual and races may differ in nitrogen dioxide tolerance level and individual tolerance level for the gas may be altered by several factors, such as metabolic rate, barometric pressure, and hematological disorders but significant exposure may result in fatal conditions that could lead to shorter lifespan due to heart failure.
Exposure to high level of nitrogen dioxide may lead to inflammation of the mucous membrane and the lower and upper respiratory tracts. The symptoms of acute nitrogen dioxide poisoning is non-specific and have a semblance with ammonia gas poisoning, chlorine gas poisoning, and carbon monoxide poisoning. The symptoms also resembles that of pneumonia or viral infection and other inhalational injuries but common symptoms includes rhinitis wheezing or coughing, conjunctivitis, headache, throat irritation and dyspnea which may progress to nasal fissures, ulcerations, or perforation. The patient is usually ill-appearing and presents with hypoxemia coupled with shallow rapid breathing. Therapy is supportive and includes removal from further nitrogen dioxide exposure. Systemic symptoms include fever and anorexia. Electrocardiography and chest radiography can help in revealing diffuse, bilateral alveolar infiltrates.
Chest radiography may be used in diagnosis and the baseline could be established with pulmonary function testing. There is no specific laboratory diagnostic test for acute nitrogen dioxide poisoning but analysis of arterial blood gas level, methemoglobin level, complete blood count, glucose test, lactate threshold measurement and r peripheral blood smear may be helpful in the diagnosis of nitrogen dioxide poisoning. The determination of nitrogen dioxide in urine or tissue does not establish the diagnosis, and there are technical and interpretive problems with these tests.
Prolonged exposure to a very high level of nitrogen dioxide in micro meter-size range, may have an inflammatory effect that principally targets the respiratory tracts leading to chronic nitrogen dioxide poisoning which can occur within days or weeks after the threshold limit value is excessively exceeded.
This condition causes fever, rapid breathing coupled with rapid heart rate, and severe seizure of breath. Other effects include diaphoresis, chest pain, and persistent dry cough, all of which may result in weight loss, anorexia and may also lead to right-side heart enlargement and heart disease in advanced cases. Prolonged exposure to relatively low levels of nitrogen (II) oxide may cause persistent headaches and nausea. Like chlorine gas poisoning, symptoms usually resolve themselves upon removal from further nitrogen dioxide exposure, unless there had been an episode of severe acute poisoning. Treatment and management vary with symptoms. Patients are often observed for hypoxemia for a minimum of 12 hours if there are no initial symptoms and if the patient is hypoxemic, oxygen may be administered but high-dose steroids are recommended for patients with pulmonary manifestations. Patients may also be hospitalized for 12 to 24 hours or longer for observation if the gaseous exchange is impaired. In a case where gaseous exchange is impaired, mechanical ventilation and intubation may be necessary and if bronchiolitis obliterans develop within 2 to 6 weeks of nitrogen dioxide exposure, corticosteroid therapy such as anticholinergic may be required for 6 to 12 months to lower the body overreaction to nitrogen dioxide gas.
Occupational exposures constitute the highest risk of toxicity and it is often high for farmers especially those that deal with food grains. It is equally high for firefighters and military personnel, especially those officers that deal in explosives. The risk is also high for arc welders, traffic officers, aerospace staffs and miners as well as those people whose occupations are connected with the nitric acid. Silo-filler's disease is a consequence of exposure to nitrogen dioxide poisoning by farmers dealing with silos. Food grains such as corn and millet, as well as grasses such as alfalfa and some other plant material, produces nitrogen dioxide within hours due to anaerobic fermentation. The threshold concentrations of nitrogen dioxide are often attained within 1 to 2 days and begin to decline gradually after 10 to 14 days but if the silos is well sealed, the gas may remain in there for weeks. Heavily fertilized silage, particularly the ones produced from immature plants, generate a higher concentration of the gas within the silo. Nitrogen dioxide is about 1.5 times heavier than air and during silage storage, nitrogen dioxide remains in the silage material. Improper ventilation may result in exposure during the leveling of the silage.
Nitrogen dioxide is sparingly soluble in water and on inhalation, it diffuses into the lung and slowly hydrolyzes to nitrous and nitric acid which causes pulmonary edema and pneumonitis leading to the inflammation of the bronchioles and pulmonary alveolus resulting from lipid peroxidation and oxidative stress. Mucous membrane is primarily affected alongside with type I pneumocyte and the respiratory epithelium. The generation of free radicals from lipid peroxidation results in irritation of the bronchioles and alveoli that causes rapid destruction of the respiratory epithelial cells. The overall reaction results in the release of fluid that causes pulmonary edema.
Nitrogen dioxide poisoning may alter macrophage activity and immune function leading to susceptibility of the body to a wide range of infections, and overexposure to the gas may also lead to methemoglobinemia, a disorder characterized by a higher than normal level of methemoglobin (metHb, i.e., ferric [Fe3+] rather than ferrous [Fe2+] haemoglobin) in the blood.
Methemoglobinemia prevents the binding of oxygen to haemoglobin causing oxygen depletion that could lead to severe hypoxia.
If nitrogen dioxide poisoning is untreated, fibrous granulation tissue is likely to develop within the alveolar ducts, tiny ducts that connect the respiratory bronchioles to alveolar sacs, each of which contains a collection of alveoli (small mucus-lined pouches made of flattened epithelial cells). The overall reaction may cause an obstructive lung disease. Meanwhile, proliferative bronchiolitis is a secondary effect of nitrogen dioxide poisoning.
The EPA have some regulations and guidelines for monitoring nitrogen dioxide levels. Historically, some states in the U.S including Chicago, Northeast corridor and L.A have had high levels of nitrogen dioxide.
In 2006, the WHO estimated that over 2 million deaths result annually from air pollution in which nitrogen dioxide constitute one of the pollutants. While over 50% of the disease that results from these pollutants are common in developing countries and the effects in developed countries is also significant. An EPA survey in the U.S. suggests that 16 percent of United States' housing units are sited close to an airport, highway or railroad increasing in the United States the exposure risk of approximately 48 million people.
A feasibility study of the ozone formed from the oxidation of nitrogen dioxide in ambient air reported by the WHO suggested that daily deaths of 1 to 2% is attributed to exposure to ozone concentration above 47.3 ppb and exposure above 75.7ppb is attributed to 3 to 5% increase in daily mortality. A level of 114 ppb was attributed to 5 to 9% increase daily mortality.
Silo filler's disease is pervasive during the harvest seasons of food grains.
In May 2015, the National Green Tribunal directed Delhi and other states in India to ban diesel vehicles over 10 years old as a measure to reduce nitrogen dioxide emission that may result in nitrogen dioxide poisoning. In 2008, the report of United Kingdom committee on the medical effects of air pollutants (COMEAP) suggested that air pollution is the cause of about 29,000 deaths in UK. The WHO urban air quality database estimated Delhi's mean annual PM 10 levels in 2010 as 286 μg /m3 and London as 23 μg /m3. In 2014, the database estimated Delhi's annual mean PM 2.5 particulate matter levels in 2013 as 156 μg /m3 whereas, London have only 8 μg /m3 in 2010 but the nitrogen dioxide in London breach the European Union's standard. In 2013, the annual mean nitrogen dioxide level in London was estimated as 58 μg /m3 but the save and "threshold limit value" is 40 μg /m3. On March 2015, Brussels took the United Kingdom into court for breaching emissions limits of nitrogen dioxide at its coal-fired Aberthaw power stations in Wales. The plant operated under a permit allowing emissions of 0.0012 μg/m3, which is more than twice the 0.000 5μg /m3 limit specified in the EU's large combustion plant directive.
Generally, long-term prognosis is helpful to survival of initial exposure to nitrogen dioxide. Some cases of nitrogen dioxide poisoning resolves with no observable symptoms and patient may be determined by pulmonary function testing. If chronic exposure causes lung damage, it could take several days or months for the pulmonary function to improve. Meanwhile, permanent mild dysfunction may result from bronchiolitis obliterans and could manifest as abnormal flow at 50 to 70 percent of vital capacity. It may also manifest as mild hyperinflammation, airway obstruction and in that case, patient may be subject to steroid treatment to treat deconditioning. Complications from prolong exposure includes bronchiolitis obliterans and other secondary infections such as pneumonia due to injuries on the mucous membrane from pulmonary edema and inhibition of immune system by nitrogen dioxide. Nitrogen dioxide inhalation can result in short and long-term morbidity or death depending on the extent of exposure and inhaled concentration and the exposure time. Illness resulting from acute exposure is usually not fatal although some exposure may cause bronchiolitis obliterans, pulmonary edema as well as rapid asphyxiation. If the concentration of exposure is excessively high, the gas may displace oxygen resulting in fatal asphyxiation.
Generally, patients and workers should be educated by medical personnel on how to identify the signs and symptoms of Nitrogen dioxide poisoning. Farmers and other farm workers should be educated on the proper way of food grain storage to prevent silo filler's disease.
Chronic exposure to high level of nitrogen dioxide results in the allosteric inhibition of glutathione peroxidase and glutathione S-transferase, both of which are important enzymes found in the mucous membrane antioxidant defense system, that catalyse nucleophilic attack by reduced glutathione (GSH) on non-polar compounds that contain an electrophillic carbon and nitrogen. These inhibition mechanisms generates free radicals that causes peroxidation from the lipids in the mucous membrane leading to increased peroxidized eyrthrocyte lipids, a reaction that proceeds by a free radical chain reaction mechanism that result in oxidative stress. The oxidative stress on the mucous membrane causes the dissociation of the GSTp-JNK complex, oligomerization of GSTP and induction of the JNK pathway, resulting in apoptosis or inflammation of the bronchioles and pulmonary alveolus in mild cases. On migrating to the bloodstream, nitrogen dioxide poisoning results in an irreversible inhibition of the erythrocite membrane acetylcholinesterase which may lead to muscular paralysis, convulsions, bronchoconstriction, the narrowing of the airways in the lungs (bronchi and bronchioles) and death by asphyxiation. It also causes a decrease in glucose-6-phosphate dehydrogenase which may results in glucose-6-phosphate dehydrogenase deficiency known as favism, a condition that predisposes to hemolysis (spontaneous destruction of red blood cells). Acute and chronic exposure also reduces glutathione reductase, an enzyme that catalyzes the reduction of glutathione disulfide (GSSG) to the sulfhydryl form glutathione (GSH), which is a critical molecule in resisting oxidative stress and maintaining the reducing environment of the cell.
Exposure to nitrogen dioxide has a significant effect on the male reproductive system by inhibiting the production of Sertoli cell, a "nurse" cell of the testicles that is part of a seminiferous tubule and helps in the process of spermatogenesis. These effects consequently retard the production of sperm cell. The effects of nitrogen dioxide poisoning of female reproduction may be linked with the effects of oxidative stress in female reproduction. Nitrogen dioxide poisoning disrupts the balance of reactive oxygen species, ROS which results in OS and this has significant effects on female reproductive life span. ROS play a significant role in body physiology, from oocyte production, development and maturation to fertilization, development of embryo and pregnancy. Exposure to nitrogen dioxide causes an ovulation-induced oxidative damage to the DNA of ovarian epithelium. There is a growing literature on the pathological effects of ROS on female reproduction in relation to free radical-induced birth defect, abortion, hydatidiform mole and pathophysiogy of pre-eclampsia. ROS also play a significant role in etiopathogenesis of endometriosis, a disease in which tissue that normally grows inside the uterus grows outside the uterus. Oxidative stress causes defective placentation which is likely to lead to placental hypoxia, shortage of oxygen in the placental as well as reperfusion injury resulting from ischemia which may lead to endothelial cell dysfunction. Over-expression of oxidative stress caused by nitrogen dioxide poisoning may results in ovarian epithelium inflammation and sometime leads to cancer in severe cases.
- Krzyzanowski Michal (June 2008). "Update of WHO air quality guidelines". Air Quality, Atmosphere & Health. International Agency for Research on Cancer. 1 (1): 7–13. doi:10.1007/s11869-008-0008-9. Retrieved August 1, 2015.
- "Nitrogen dioxide". US EPA. Retrieved August 1, 2015.
- "Indoor Air". United States Environmental Protection Agency. Retrieved August 1, 2015.
- Ashok, Pandey (2014). Pretreatment of Biomass: Processes and Technologies. USA: Elsevier. p. 202. ISBN 0128003960. Retrieved August 1, 2015.
- "Nitrogen dioxide - WHO Guidelines for Indoor Air Quality: Selected". PubMed. Retrieved August 1, 2015.
- Belanger K, Gent JF, Triche EW, Bracken MB, Leaderer BP (February 1, 2006). "Association of indoor nitrogen dioxide exposure with respiratory symptoms in children with asthma". American Journal of Respiratory and Critical Care Medicine. 173 (3): 297–303. doi:10.1164/rccm.200408-1123OC. PMC 2662932. PMID 2662932.CS1 maint: Multiple names: authors list (link)
- "Nitrogen oxides limits: Chicago would fail to meet Obama's tougher". Chicargo Tribune. Retrieved August 1, 2015.
- "Nitrogen Dioxide". American Lung Association. Retrieved August 1, 2015.
- "Hazardous Substances Data Bank (HSDB) [online database]. Nitrogen dioxide". National Library of Medicine. Retrieved August 1, 2015.
- Arashidani K, Yoshikawa M, Kawamoto T, Matsuno K, Kayama F, Kodama Y (1996). "Indoor pollution from heating". Ind Health. 34 (3): 205–15. doi:10.2486/indhealth.34.205. PMID 8768665.CS1 maint: Multiple names: authors list (link)
- J I Levy, K Lee, Y Yanagisawa, P Hutchinson, and J D Spengler (1998). "Determinants of nitrogen dioxide concentrations in indoor ice skating rinks". American Journal of Public Health. 88 (12): 1781–6. doi:10.2105/ajph.88.12.1781. PMC 1509046.CS1 maint: Multiple names: authors list (link)
- Glorennec P; et al. (2008). "Is a quantitative risk assessment of air quality in underground parking garages possible?". Indoor Air. 18 (4): 283–92. doi:10.1111/j.1600-0668.2008.00529.x. PMID 18717983.CS1 maint: Explicit use of et al. (link)
- Leung R; et al. (1998). "Indoor environment of residential homes in Hong Kong – relevance to asthma and allergic disease". Clin Exp Allergy. 28 (5): 585–90. doi:10.1046/j.1365-2222.1998.00281.x. PMID 9645595.CS1 maint: Explicit use of et al. (link)
- Hagenbjork-Gustafsson A; et al. (1996). "Measurements of indoor and outdoor nitrogen dioxide concentrations using a diffusive sampler". Analyst. 12 (9): 1261–1264. Bibcode:1996Ana...121.1261H. doi:10.1039/an9962101261. PMID 8831283.CS1 maint: Explicit use of et al. (link)
- Levy JI; et al. (1998). "Impact of residential nitrogen dioxide exposure on personal exposure: an international study". J Air Waste Manag Assoc. 48 (6): 553–60. doi:10.1080/10473289.1998.10463704. PMID 9949739.CS1 maint: Explicit use of et al. (link)
- Lambert WE; et al. (1993). "Nitrogen dioxide and respiratory illness in children. Part II. Assessment of exposure to nitrogen dioxide". Res Rep Health Eff Inst. 58 (33–50): 51–80. PMID 8240759.CS1 maint: Explicit use of et al. (link)
- Simoni M; et al. (2002). "The Po River Delta (north Italy) indoor epidemiological study: effects of pollutant exposure on acute respiratory symptoms and respiratory function in adults". Arch Environ Health. 57 (2): 130–6. doi:10.1080/00039890209602928. PMID 12194158.CS1 maint: Explicit use of et al. (link)
- Garcia-Algar O; et al. (2003). "Sources and concentrations of indoor nitrogen dioxide in Barcelona, Spain". J Air Waste Manag Assoc. 53 (11): 1312–7. doi:10.1080/10473289.2003.10466297. PMID 14649750.CS1 maint: Explicit use of et al. (link)
- Kodama Y; et al. (2002). "Environmental NO2 concentration and exposure in daily life along main roads in Tokyo". Environ Res. 89 (3): 236–44. Bibcode:2002ER.....89..236K. doi:10.1006/enrs.2002.4350. PMID 12176007.CS1 maint: Explicit use of et al. (link)
- Nakai S, Nitta H, Maeda K. (1995). "Respiratory health associated with exposure to automobile exhaust. II. Personal NO2 exposure levels according to distance from the roadside". J Expo Anal Environ Epidemiol. 5 (2): 125–36. PMID 7492902.CS1 maint: Multiple names: authors list (link)
- Baxter LK; et al. (2007). "Predicting residential indoor concentrations of nitrogen dioxide, fine particulate matter, and elemental carbon using questionnaire and geographic information system based data". Atmos Environ. 41 (31): 6561–6571. Bibcode:2007AtmEn..41.6561B. doi:10.1016/j.atmosenv.2007.04.027. PMC 2760735. PMID 19830252.CS1 maint: Explicit use of et al. (link)
- Hansel N; et al. (2008). "A longitudinal study of indoor nitrogen dioxide levels and respiratory symptoms in inner-city children with asthma". Environ Health Perspect. 116 (10): 1428–32. doi:10.1289/ehp.11349. PMC 2569107. PMID 18941590.CS1 maint: Explicit use of et al. (link)
- Pilotto LS; et al. (1997). "Respiratory effects associated with indoor nitrogen dioxide exposure in children". Int J Epidemiol. 26 (4): 788–96. doi:10.1093/ije/26.4.788. PMID 9279611.CS1 maint: Explicit use of et al. (link)
- Lévesque B; et al. (2001). "Wood-burning appliances and indoor air quality". Sci Total Environ. 281 (1–3): 46–62. PMID 11778959.CS1 maint: Explicit use of et al. (link)
- Blondeau P; et al. (2005). "Relationship between outdoor and indoor air quality in eight French schools". Indoor Air. 15 (1): 2–12. doi:10.1111/j.1600-0668.2004.00263.x. PMID 15660564.CS1 maint: Explicit use of et al. (link)
- Weschler CJ, et. al (2006). "Workgroup report: indoor chemistry and health. Environmental Health Perspectives". Environ Health Perspect. 11 (3): 442–6. doi:10.1289/ehp.8271. PMC 1392240. PMID 16507469.
- Kattan M; et al. (2007). "Health effects of indoor nitrogen dioxide and passive smoking on urban asthmatic children". J Allergy Clin Immunol. 120 (3): 618–24. doi:10.1016/j.jaci.2007.05.014. PMID 17582483.CS1 maint: Explicit use of et al. (link)
- Baxter LK; et al. (2007). "Predictors of concentrations of nitrogen dioxide, fine particulate matter, and particle constituents inside of lower socioeconomic status urban homes". J Expo Sci Environ Epidemiol. 17 (5): 433–44. doi:10.1038/sj.jes.7500532. PMID 17051138.CS1 maint: Explicit use of et al. (link)
- Kumie A; et al. (2008). "lMagnitude of indoor NO2 from biomass fuels in rural settings of Ethiopia". Indoor Air. 19 (1): 14–21. doi:10.1111/j.1600-0668.2008.00555.x. PMID 19191924.CS1 maint: Explicit use of et al. (link)
- Lawrence AJ et. al. (2005). "Indoor/outdoor relationships of carbon monoxide and oxides of nitrogen in domestic homes with roadside, urban and rural locations in a central Indian region". Indoor Air. 15 (2): 76–82. doi:10.1111/j.1600-0668.2004.00311.x. PMID 15737150.
- "UK set for war on NO2 emissions". Times of India. Retrieved August 2, 2015.
- "London set to declare war on diesel". The Irish Times. Retrieved August 2, 2015.
- "Air pollution in London's Oxford Street has already breached the". Independent News. Retrieved August 2, 2015.
- "UK set for war on NO2 emissions". India Environment Portal. Retrieved August 2, 2015.
- "UK faces European court over coal plant emissions". The Guardian News. Retrieved August 2, 2015.
- Garrett MH, Hooper MA, Hooper BM (1996). "Nitrogen dioxide in Australian homes: levels and sources". J Air Waste Manag Assoc. 49 (1): 76–81. PMID 9951416.CS1 maint: Multiple names: authors list (link)
- Zota A; et al. (2005). "Ventilation in public housing: implications for indoor nitrogen dioxide concentrations". Indoor Air. 15 (6): 393–401. doi:10.1111/j.1600-0668.2005.00375.x. PMID 16268829.CS1 maint: Explicit use of et al. (link)
- Dennekamp M; et al. (2001). "Ultrafine particles and nitrogen oxides generated by gas and electric cooking". Occup Environ Med. 58 (8): 511–6. doi:10.1136/oem.58.8.511. PMC 1740176. PMID 11452045.CS1 maint: Explicit use of et al. (link)
- Lee K; et al. (2002). "Nitrous acid, nitrogen dioxide, and ozone concentrations in residential environments". Environ Health Perspect. 110 (2): 145–50. doi:10.1289/ehp.02110145. PMC 1240728. PMID 11836142.CS1 maint: Explicit use of et al. (link)
- "Nitrogen dioxide toxicity". medscape.com. Retrieved August 1, 2015.
- Spannhake EW; et al. (2002). "Synergism between rhinovirus infection and oxidant pollutant exposure enhances airway epithelial cell cytokine production". Environ Health Perspect. 110 (7): 665-170. doi:10.1289/ehp.02110665. PMC 1240912. PMID 12117643.CS1 maint: Explicit use of et al. (link)
- Sanga M, ichinose T (1991). "Biochemical effects of combined gases of nitrogen dioxide". Toxicology. 66 (2): 121–32. doi:10.1016/0300-483x(91)90213-k. PMID 2014515.
- Persinger RL et. al (2002). "Molecular mechanisms of nitrogen dioxide induced epithelial injury". Mol Cell Biochem. 234–235 (1–2): 71–80. PMID 12162462.
- "National Pesticide Information Center-Diazinon Technical Fact Sheet" (PDF). Retrieved 24 February 2012.
- Drachman, D.B.; Isselbacher, K.J., Braunwald, E., Wilson, J.D., Martin, J.B., Fauci, A.S. Kasper, D.L., eds (1998). Harrison's Principles of Internal Medicine (14 ed.). The McCraw-Hill Companies. pp. 2469–2472. ISBN 978-0-07-020291-7.CS1 maint: Multiple names: authors list (link) CS1 maint: Extra text: authors list (link)
- Raffe, RB. Autonomic and Somatic Nervous Systems in Netter's Illustrated Pharmacology. Elsevier Health Science. p. 43. ISBN 978-1-929007-60-8.
- Sagai M. et. al (1984). "Studies on the biochemical effects of nitrogen dioxide. IV. Relation. Relation between the changes of lipid peroxidation and the antioxidative protective system in Rat lungs upon life span exposure to low levels of Nitrogen dioxide". Toxicol Appl Pharmacol. 73 (3): 444–56. PMID 6719462.
- Meister A (November 1988). "Glutathione metabolism and its selective modification". J. Biol. Chem. 263 (33): 17205–8. PMID 3053703.
- Mannervik B (August 1987). "The enzymes of glutathione metabolism: an overview". Biochem. Soc. Trans. 15 (4): 717–8. PMID 3315772.
- Patel JM, Block ER (1987). "Biochemical and metabolic response to nitrogen dioxide-induced enthothelia injury". Res Rep Health Eff Inst. 9 (3): 3–20. PMID 2478162.
- Ashok Agawa et. al (2005). "Role of oxidative stress in female reproduction". Reprod. Biol. Endocrinol. 3 (28): 3–28. doi:10.1186/1477-7827-3-28. PMC 1215514. PMID 16018814.
- Ashok Agarwal et. al. (2005). "Role of oxidative stress in female reproduction". Reproductive Biology and Endocrinology. 3 (28): 1477-7827. doi:10.1186/1477-7827-3-28. PMC 1215514. PMID 16018814.
- Ashok Agawa et. al (2012). "The effects of oxidative stress on female reproduction: a review". Reprod. Biol. Endocrinol. 10 (49): 1477-7827. doi:10.1186/1477-7827-10-49. PMC 3527168. PMID 22748101.
- Gupta S et. al (2007). "The role of oxidative stress in spontaneous abortion and recurrent". Obstet Gynecol Surv. 62 (5): 335–47. doi:10.1097/01.ogx.0000261644.89300.df. PMID 17425812.
- Monis Bilial Shamsi et. al. (2011). "Sperm DNA damage & oxidative stress in recurrent spontaneous". Indian J. Med. Res. 133 (5): 550–551. PMC 3121290. PMID 21623044.
- "Role of oxidative stress in female reproduction". Cleaveland Clinic. Retrieved August 3, 2015.