Any of several carcinogenic or teratogenic heterocyclic hydrocarbons that occur as impurities in petroleum-derived herbicides.
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Any of several carcinogenic or teratogenic heterocyclic hydrocarbons that occur as impurities in petroleum-derived herbicides.
Dioxins are a class of halogenated aryl hydrocarbons, formed during chemical synthesis when chlorophenols are used in the starting material. The three most widely studied sources of dioxins are the manufacturing of the herbicide Agent Orange, the manufacturing of the microbicide hexachlorphene, and the chlorine bleaching of wood pulp. Other sources include combustion of wastes that contain chlorine residues in plastics, and combustion in engines where a chlorinated product has been used as a fuel additive.
2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is the prototype for the toxicity of this chemical class, which also includes chlorinated dibenzofurans. TCDD is one of the most highly toxic chemicals tested in several laboratory animal species. The acute LD50 (the lethal dose that will kill 50 percent of test animals) in guinea pigs (the most susceptible species) is in the microgram per kilogram range; the toxicity in rodents varies by species and strain of animal. The reason for this variation is that TCDD operates through a specific protein called the aryl hydrocarbon receptor (AhR), and the level of this protein and its ancillary proteins varies across species. TCDD is teratogenic in mice and carcinogenic in rats and mice, and is classified as a probable human carcinogen based on animal data and epidemiological studies. The most common human finding observed in high level occupational and accidental exposures is chloracne, a skin disorder. Several epidemiology studies have been conducted in worker cohorts, and in veterans and residents of Vietnam, with inconsistent results. However, it is generally accepted that TCDD has the potential to be a human carcinogen and teratogen, and exposures should be reduced to an absolute minimum.
The controversy surrounding this class of compounds stems from five areas. First, TCDD is highly toxic having carcinogenic, teratogenic, immunotoxic, and endocrine modulation properties. Second, there are over 200 analogs and congeners of the dioxins and benzofurans, with varying qualitative and/or qualitative toxicity. Toxic Equivalent Factors (TEFs) have been developed based on the ability of the analogs and congeners to bind to the AhR and induce a family of enzymes in a manner similar to TCDD. Third, TCDD is very persistent in soil and in animal tissues (including humans). Half-life estimates range from months to several years. Dioxins also bioaccumulate in the food chain. Hence, the potential is there for the compounds to accumulate in human tissue. Fourth, the extent of toxicity in humans has not been well defined. Fifth, dioxins are produced as combustion products when chlorine is available in the burning process. This area is of particular importance because of the incineration of municipal waste that contains bottles made from chlorinated plastics.
A great deal of research has gone into the generation and control of dioxin emissions from incinerators. One confounding factor is that incinerators may not be the only point source for dioxins, and fewer chemical plants are using starting materials that will lead to major releases of dioxins as in the past. Wood pulp and paper bleaching in the United States and Canada has minimized or eliminated the use of chlorine bleaches, but the contamination that exists is very persistent. The search for other sources of dioxins continues.
Some polychlorinated biphenyls (PCBs), another class of chlorinated hydrocarbons, mimic the biological activity of dioxins.
(SEE ALSO: Carcinogen; Carcinogenesis; Endocrine Disrupters; PCBs; Persistent Organic Pollutants [POPs]; Pollution; Toxicology)
— MICHAEL GALLO
n.a highly toxic compound produced as a by-product in some manufacturing processes, notably herbicide production (especially Agent Orange) and paper bleaching. It is a serious and persistent environmental pollutant.
See the Introduction, Abbreviations and Pronunciation for further details.
For more information on dioxin, visit Britannica.com.
Endocrine disruptor. Causes birth defects, developmental problems, and cancer.
A group of pollutants created as by-products in many industrial processes. Dioxins accumulate in human tissue and affect human
A highly toxic and teratogenic chlorinated hydrocarbon that is a trace contaminant in the herbicide 2,4,5-T. Acute poisoning causes vomiting, abortion, anestrus. Chronic poisoning causes liver damage, especially in dogs. Congenital defects caused include cranio-facial deformity and anasarca. It is excreted in the milk.
Dioxin in its original usage denoted the organochemical heterocyclic compound with the general chemical formula C4H4O2 in which two CH groups of a benzene ring were replaced (endocyclic substitution) by oxygen atoms, of which two isomers were possible, the ortho (o) and the para (p) variety: 1,2-dioxin and 1,4-dioxin. This name then extended to the family of compounds derivable from the parent compounds by exocyclic substitution, and especially to the dibenzo substitution of the para variety.
Dioxin in current usage is the common name for the group of compounds classified as polychlorinated dibenzodioxins (PCDDs). PCDDs, which are members of the family of halogenated organic compounds, have been shown to bioaccumulate in humans and wildlife due to their lipophilic properties, and are known teratogens, mutagens, and suspected human carcinogens.
The basic structure of PCDDs comprises two benzene rings joined by a double oxygen bridge. Chlorine atoms are attached to the basic structure at any of 8 different places on the molecule, positions 1–4 and 6–9. There are 75 different types of PCDD congeners (herein, a congener means a related dioxin compound). The toxicity of PCDDs depends on the number and position of the chlorine atoms; only congeners that have chlorines in the 2, 3, 7, and 8 positions have been found to be significantly toxic. Out of the 75 PCDD compounds, only 7 congeners have chlorine atoms in the relevant positions to be considered toxic by the NATO Committee on the Challenges to Modern Society (NATO/CCMS) international toxic equivalent (I-TEQ) scheme.
Concentrations of dioxins in nature prior to industrialization, due to natural combustion and geological processes, were generally about three times lower than today [1] [2]. The first intentional synthesis of chlorinated dibenzodioxin dates back to 1872. Today, concentrations of dioxins are found in all humans, with higher levels commonly found in persons living in more industrialized countries. The most toxic dioxin, 2,3,7,8 tetrachlorodibenzo-p-dioxin (TCDD), became well known as a contaminant of Agent Orange, a herbicide used in the Vietnam War[3]. Later, dioxins were found in Times Beach, Missouri, USA [4] and Love Canal, New York, USA [5] and Seveso, Italy [6]. More recently, dioxin has been in the news with the poisoning of President Viktor Yushchenko of Ukraine, 2004 [7].
The United States Environmental Protection Agency
Dioxin Reassessment Report is possibly the most comprehensive review of
dioxin, but other countries now have substantial research. Australia,
Occupational exposure is an issue for some in the chemical industry, or in the application of chemicals, notably herbicides. Inhalation has been a problem for people living near substantial point sources where emissions are not adequately controlled. In many developed nations there are now emissions regulations which have alleviated some concerns, although the lack of constant sampling of dioxin emissions causes concern about the understatement of emissions. In Belgium, through the introduction of a process called AMESA, constant sampling showed that periodic sampling understated emissions by a factor of 30 to 50 times. Few facilities have constant sampling.
Most controversial is the United States Environmental Protection Agency assessment's (draft) finding that any reference dose that were to be set would be far below current average intakes.
Children are passed substantial body burdens by their mothers, and breastfeeding increases the child's body burden[citation needed]. Children's body burdens are often many times above the amount implied by tolerable intakes which are based on body weight. Breast fed children usually have substantially higher dioxin body burdens than non breast fed children until they are about 8 to 10 years old. The WHO still recommends breast feeding for its other benefits.
Dioxins are produced in small concentrations when organic material is burned in the presence of chlorine, whether the chlorine is present as chloride ions or as organochlorine compounds, so they are widely produced in many contexts. According to the most recent US EPA data the major sources of dioxin are:
These sources together account for nearly 80% of dioxin emissions.
When the original US EPA inventory of dioxin sources was done in 1987, incineration represented over 80% of known dioxin sources. As a result, US EPA implemented new emissions requirements. These regulations have been very successful in reducing dioxin stack emissions from incinerators. Incineration of municipal solid waste, medical waste, sewage sludge, and hazardous waste together now produce less than 3% of all dioxin emissions.
In incineration, dioxins can also reform in the atmosphere above the stack as the exhaust gases cool through a temperature window of 600 to 200°C. The most common method of reducing dioxins reforming or forming de novo is through rapid (30 millisecond) quenching of the exhaust gases through that 400°C window [9]. Incinerator emissions of dioxins have been reduced by over 90% as a result of new emissions control requirements. Incineration is now a very minor contributor to dioxin emissions.
Dioxins are also generated in reactions that do not involve burning — such as bleaching fibers for paper or textiles, and in the manufacture of chlorinated phenols, particularly when reaction temperature is not well controlled. Affected compounds include the wood preservative pentachlorophenol, and also herbicides such as 2,4-dichlorophenoxyacetic acid (or 2,4-D) and 2,4,5-trichlorophenoxyacetic acid (2,4,5-T). Higher levels of chlorination require higher reaction temperatures and greater dioxin production. See Agent Orange for more on contamination problems in the 1960s. Dioxins may also be formed during the photochemical breakdown of the common antimicrobial compound triclosan [10].
Dioxins are also in typical cigarette smoke[citation needed]. Dioxin in cigarette smoke was noted as "understudied" by the US EPA in its "Re-Evaluating Dioxin" (1995). In that same document, the US EPA acknowledged that dioxin in cigarettes is "anthropogenic" (man-made, "not likely in nature"). Nevertheless, the use of chlorine-containing tobacco pesticides and chlorine-bleached cigarette papers remains legal[citation needed].
Dioxins are present in minuscule amounts in a wide range of materials used by humans — including practically all substances manufactured using plastics, resins, or bleaches.[citation needed] Such materials include tampons, and a wide variety of food packaging substances[citation needed]. The use of these materials means that all Western humans receive at least a very small daily dose of dioxin[citation needed]—however, it is disputed whether such exceptionally tiny exposures have any clinical relevance[citation needed]. It is even controversially discussed whether dioxins might have a non-linear dose-response curve with beneficial health effects in a certain lower dose range, a phenomenon called hormesis[citation needed].
Dietary sources of dioxin in the United States have been analyzed by the EPA and scientists from other organizations.
Dioxins are absorbed primarily through dietary intake of fat, as this is where they accumulate in animals and humans. In humans, the highly chlorinated dioxins are stored in fatty tissues and are neither readily metabolized nor excreted. The estimated elimination half-life for highly clorinated dioxins (4-8 chlorine atoms) in humans ranges from 7.8 to 132 years [11].
The persistence of a particular dioxin congener in an animal is thought to be a consequence of its structure. It is believed that dioxins with few chlorines, which thus contain hydrogen atoms on adjacent pairs of carbons, can more readily be oxidized by cytochromes P450.[citation needed] The oxidized dioxins can then be more readily excreted rather than stored for long time.[citation needed]
2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) is the most toxic of the congeners. Other dioxin congeners (or mixtures thereof) are given a toxicity rating from 0 to 1, where TCDD = 1. This toxicity rating is called the Toxic Equivalence Factor, or TEF. TEFs are consensus values and, because of the strong species dependence for toxicity, are listed separately for mammals, fish, and birds. TEFs for mammalian species are generally applicable to human risk calculations. The TEFs have been developed from detailed assessment of literature data to facilitate both risk assessment and regulatory control [12]. Many other compounds may also have dioxin-like properties, particularly non-ortho PCBs, some of which can have TEFs as high as 0.1.
The total dioxin toxic equivalence (TEQ) value expresses the toxicity as if the mixture were pure TCDD. The TEQ approach and current TEFs have been adopted internationally as the most appropriate way to estimate the potential health risks of mixture of dioxins. Recent data suggest that this type of linear scaling factor may not be the most appropriate treatment for complex mixtures of dioxins; further research into non-linear toxicity models is required to substantiate this hypothesis.
Dioxins and other persistent organic pollutants (POPs) are subject to the Stockholm Convention. The treaty obliges signatories to take measures to eliminate where possible, and minimize where not possible to eliminate, all sources of dioxin.
Dioxins build up primarily in fatty tissues over time (bioaccumulate), so even small exposures may eventually reach dangerous levels. In 1994, EPA reported that dioxin is a probable carcinogen, but notes that non-cancer effects (reproduction and sexual development, immune system) may pose an even greater threat to human health. TCDD, the most toxic of the dibenzodioxins, has a half-life of approximately 8 years in humans, but at high concentrations, the elimination rate is enhanced by metabolism [13]. The health effects of dioxins are mediated by their action on a cellular receptor, the aryl hydrocarbon receptor (AhR) [14].
Dioxins also accumulate in food chains in a fashion similar to other chlorinated compounds (bioaccumulate). This means that even small concentrations in contaminated water can be concentrated up a food chain to dangerous levels due to the long biological half life and low solubility of dioxins.
Exposure to high levels of dioxin in humans causes a severe form of persistent acne, known as chloracne [15]. Other effects in humans may include:
Recent studies have shown that exposure to dioxin changes the ratio of male to female births among a population such that more females are born than males.[23]
While it has been difficult to prove that dioxins cause specific health effects in humans due to the lack of controlled dose experiments, studies in animals have shown that dioxin causes a wide variety of toxic effects. In particular, TCDD has been shown to be teratogenic, mutagenic, carcinogenic, immunotoxic, and hepatotoxic. Furthermore, alterations in multiple endocrine and growth factor systems have been reported. The most sensitive effects, observed in multiple species, appear to be developmental, including effects on the developing immune, nervous, and reproductive systems [24]. These effects are caused at body burdens close to those reported in humans.
Among the animals for which TCDD toxicity has been studied, there is strong evidence for the following effects:
US veterans' groups and Vietnamese groups, including the Vietnamese government, have convened scientific studies to explore their belief that dioxins were responsible for a host of disorders, including tens of thousands of birth defects in children, amongst Vietnam veterans as well as an estimated one million Vietnamese, through their exposure to Agent Orange during the Vietnam War, which was found to be highly contaminated with TCDD. Several exposure studies showed that some US Vietnam Veterans who were exposed to Agent Orange had serum TCDD levels up to 600 ppt (parts per trillion) many years after they left Vietnam, compared to general population levels of approximately 1 to 2 ppt of TCDD. In Vietnam, TCDD levels up to 1,000,000 ppt have been found in soil and sediments from Agent Orange contaminated areas 3 to 4 decades after spraying. In addition, elevated levels have been measured in food and wildlife in Vietnam [37].
The most recent study, paid for by the National Academy of Sciences, was released in an April 2003 report. This report is currently (March 2007) being revised for release again later in 2007.
The Centers for Disease Control found that dioxin levels in Vietnam veterans [38] were in no way atypical when compared against the rest of the population. The only exception existed for those who directly handled Agent Orange. These were members of Operation Ranch Hand. Long-term studies of the members of Ranch Hand have thus far uncovered a possibility of elevated risks of diabetes.
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Français (French)
n. - dioxine
Deutsch (German)
n. - (chem.) Dioxin
Ελληνική (Greek)
n. - (χημ.) διοξίνη
Português (Portuguese)
n. - dioxina (f) (Quím.)
Русский (Russian)
разлагающее вещество в гербициде
Español (Spanish)
n. - dioxina
中文(简体) (Chinese (Simplified))
戴奥辛
中文(繁體) (Chinese (Traditional))
n. - 戴奧辛
العربيه (Arabic)
(الاسم) مادة ملوثه و سامه
עברית (Hebrew)
n. - דיוקסין (כימיקל)
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