Chlordane is a chemical compound and also part of a similarly named pesticide mixture resulting from synthesis (main components- heptachlor, chlordane, and nonachlor). These highly chlorinated cyclodienes were classified as organic pollutants hazardous for human health. They are both resistant to degradation in the environment and in humans/animals and readily accumulate in lipids (fats) of human/animals. Exposure to these compounds has been linked to cancers and many other diseases.
|Systematic IUPAC name
Chlordan; Chlordano; Ortho; Octachloro-4,7-methanohydroindane
|Molar mass||g·mol−1 409.76|
|Appearance||Colorless, viscous liquid|
|Odor||Slightly pungent, chlorine-like|
|Melting point||102–106 °C (216–223 °F; 375–379 K) |
Refractive index (nD)
|Main hazards||potential occupational carcinogen|
|Flash point||107 °C (225 °F; 380 K) (open cup)|
|Lethal dose or concentration (LD, LC):|
LD50 (median dose)
|590 mg/kg (rat, oral)|
100 mg/kg (rabbit, oral)
430 mg/kg (mouse, oral)
300 mg/kg (rabbit, oral)
145 mg/kg (mouse, oral)
1720 mg/kg (hamster, oral)
200 mg/kg (rat, oral)
|US health exposure limits (NIOSH):|
|TWA 0.5 mg/m3 [skin]|
|Ca TWA 0.5 mg/m3 [skin]|
IDLH (Immediate danger)
Except where otherwise noted, data are given for materials in their standard state (at 25 °C [77 °F], 100 kPa).
|what is ?)(|
In the United States, chlordane was used for termite-treatment of approximately 30 million homes until it was banned in 1988. Chlordane was banned 10 years earlier for food crops like corn and citrus, and on lawns and domestic gardens.
Production, composition and usesEdit
Technical chlordane development was by chance by Julius Hyman in 1948, during a search for possible uses of a by-product of synthetic rubber manufacturing. By chlorinating this by-product, persistent and potent insecticides were easily and cheaply produced. The chlorine atoms, 7 in the case of heptachlor and 8 in chlordane, and 9 in the case of nonachlor, surround and stabilize the cyclodiene ring and thus these compounds are referred to as cyclodienes. Other members of the cyclodiene family of organochorine insecticides are aldrin and its epoxide, dieldrin, as well as endrin, which is a stereoisomer of dieldrin. Cyclodiene derives its name from hexachlorocyclopentadiene a precursor in its production.
Hexachlorocyclopentadiene forms a Diels-Alder adduct with cyclopentadiene to give Chlordene intermediate [3734-48-3]; chlorination of this adduct gives predominantly two chlordane isomers, α and β, in addition to other products such as trans-nonachlor and heptachlor. The β-isomer is popularly known as gamma and is more bioactive. The mixture that is composed of 147 components is called technical chlordane.
Chlordane appears as a white or off-white crystals when synthesized, but it was more commonly sold in various formulations as oil solutions, emulsions, sprays, dusts, and powders. These products were sold in the United States from 1948 to 1988.
Because of concern for harm to human health and to the environment, the United States Environmental Protection Agency (EPA) banned all uses of chlordane in 1983, except termite control in wooden structures (e.g. houses). After many reports of chlordane in the indoor air of treated homes, EPA banned the remaining use of chlordane in 1988. The EPA recommends that children should not drink water with more than 60 parts of chlordane per billion parts of drinking water (60 ppb) for longer than 1 day. EPA has set a limit in drinking water of 2 ppb.
Chlordane is very persistent in the environment because it does not break down easily. Tests of the air in the residence of U.S. government housing, 32 years after chlordane treatment, showed levels of chlordane and heptachlor 10-15 times the Minimal Risk Levels (20 nanograms/cubic meter of air) published by the Centers for Disease Control. It has an environmental half-life of 10 to 20 years.
Origin, pathways of exposure, and processes of excretionEdit
In the years 1948–1988 chlordane was a common pesticide for corn and citrus crops, as well as a method of home termite control. Pathways of exposure to chlordane include ingestion of crops grown in chlordane-contaminated soil, inhalation of air in chlordane-treated homes and from landfills, and ingestion of high-fat foods such as meat, fish, and dairy, as chlordane builds up in fatty tissue. The United States Environmental Protection Agency reported that over 30 million homes were treated with technical chlordane or technical chlordane with heptachlor. Depending on the site of home treatment, the indoor air levels of chlordane can still exceed the Minimal Risks Levels (MRLs) for both cancer and chronic disease by orders of magnitude. Chlordane is excreted slowly through feces, urine elimination, and through breast milk in nursing mothers. It is able to cross the placenta and become absorbed by developing fetuses in pregnant women. A breakdown product of chlordane, the metabolite oxychlordane, accumulates in blood and adipose tissue with age.
The examples and perspective in this article deal primarily with the United States and do not represent a worldwide view of the subject. (January 2017) (Learn how and when to remove this template message)
Being hydrophobic, chlordane adheres to soil particles and enters groundwater only slowly, owing to its low solubility (0.009 ppm). It requires many years to degrade. Chlordane bioaccumulates in animals. It is highly toxic to fish, with an LD50 of 0.022–0.095 mg/kg (oral).
Oxychlordane (C10H4Cl8O), the primary metabolite of chlordane, and heptachlor epoxide, the primary metabolite of heptachlor, along with the two other main components of the chlordane mixture, cis-nonachlor and trans-nonachlor, are the main bioaccumulating constituents. trans-Nonachlor is more toxic than technical chlordane and cis-nonachlor is less toxic.
Chlordane and heptachlor are known as persistent organic pollutants (POP), classified among the "dirty dozen" and banned by the 2001 Stockholm Convention on Persistent Organic Pollutants.
Exposure to chlordane/heptachlor and/or its metabolites (oxychlordane, heptachlor epoxide) are risk factors for type-2 diabetes, for lymphoma, for prostate cancer, for obesity, for testicular cancer, for breast cancer.
An epidemiological study conducted by the National Cancer Institute reported that higher levels of chlordane in dust on the floors of homes were associated with higher rates of non-Hodgkin lymphoma in occupants. Breathing chlordane in indoor air is the main route of exposure for these levels in human tissues. Currently, EPA has defined a concentration of 24 nanogram per cubic meter of air (ng/M3) for chlordane compounds over a 20-year exposure period as the concentration that will increase the probability of cancer by 1 in 1,000,000 persons. This probability of developing cancer increases to 10 in 1,000,000 persons with an exposure of 100 ng/m3 and 100 in 1,000,000 with an exposure of 1000 ng/m3.
The non-cancer health effects of chlordane compounds, which include diabetes, insulin resistance, migraines, respiratory infections, immune-system activation, anxiety, depression, blurry vision, confusion, intractable seizures as well as permanent neurological damage, probably affects more people than cancer. Trans-nonachlor and oxychlordane in serum of mothers during gestation has been linked with behaviors associated with autism in offspring at age 4-5. The Agency for Toxic Substances and Disease Registry (ATSDR) has defined a concentration of chlordane compounds of 20 ng/m3 as the Minimal Risk Level (MRLs). ATSDR defines Minimal Risk Level as an estimate of daily human exposure to a dose of a chemical that is likely to be without an appreciable risk of adverse non-cancerous effects over a specific duration of exposure.
Chlordane was applied under the home/building during treatment for termites and the half-life can be up to 30 years. Chlordane has a low vapor pressure and volatilizes slowly into the air of home/building above. To remove chlordane from indoor air requires either ventilation (Heat Exchange Ventilation) or activated carbon filtration. Chemical remediation of chlordane in soils was attempted by the US Army Corps of Engineers by mixing chlordane with aqueous lime and persulfate. In a phytoremediation study, Kentucky bluegrass and Perennial ryegrass were found to be minimally affected by chlordane, and both were found to take it up into their roots and shoots. Mycoremediation of chlordane in soil have found that contamination levels were reduced. The fungus Phanerochaete chrysosporium has been found to reduce concentrations by 21% in water in 30 days and in solids in 60 days.
- "NIOSH Pocket Guide to Chemical Hazards #0112". National Institute for Occupational Safety and Health (NIOSH).
- "Chlordane". Immediately Dangerous to Life and Health Concentrations (IDLH). National Institute for Occupational Safety and Health (NIOSH).
- Agency for Toxic Substances & Disease Registry (ATSDR). Toxic Substances Portal: Chlordane. Last updated September, 2010 [online]. Available at URL: http://www.atsdr.cdc.gov/substances/toxsubstance.asp?toxid=62
- Toxicological Profile for Chlordane, U.S. Department Of Health and Human Services, Agency for Toxic Substances and Disease Registry
- Robert L. Metcalf "Insect Control" in Ullmann’s Encyclopedia of Industrial Chemistry, Wiley-VCH, Weinheim, 2002. doi:10.1002/14356007.a14_263
- Dearth Mark A.; Hites Ronald A. (1991). "Complete analysis of technical chlordane using negative ionization mass spectrometry". Environ. Sci. Technol. 25 (2): 245–254. doi:10.1021/es00014a005.
- Bondy, G. S.; Newsome, WH; Armstrong, CL; Suzuki, CA; Doucet, J; Fernie, S; Hierlihy, SL; Feeley, MM; Barker, MG (2000). "Trans-Nonachlor and cis-Nonachlor Toxicity in Sprague-Dawley Rats: Comparison with Technical Chlordane". Toxicological Sciences. 58 (2): 386–98. doi:10.1093/toxsci/58.2.386. PMID 11099650.
- Liu W.; Ye J.; Jin M. (2009). "Enantioselective phytoeffects of chiral pesticides". J Agric Food Chem. 57 (6): 2087–2095. doi:10.1021/jf900079y. PMID 19292458.
- Pesticides and Breast Cancer Risk: Chlordane Archived 2012-06-14 at the Wayback Machine, Fact Sheet #11, March 1998, Program on Breast Cancer and Environmental Risk Factors Cornell University
- Bennett, G. W.; Ballee, D. L.; Hall, R. C.; Fahey, J. F.; Butts, W. L. & Osmun, J. V. (1974). "Persistence and distribution of chlordane and dieldrin applied as termiticides". Bull. Environ. Contam. Toxicol. 11 (1): 64–9. doi:10.1007/BF01685030. PMID 4433785.
- Agency for Toxic Substances & Disease Registry (ATSDR). ToxFaqs: September, 1995. Available at URL: http://www.atsdr.cdc.gov/toxfaqs/tfacts31.pdf
- Whitmore R. W.; et al. (1994). "Non-occupational exposures to pesticides for residents of two U.S. cities". Archives of Environmental Contamination and Toxicology. 26 (1): 47–59. doi:10.1007/bf00212793. PMID 8110023.
- Center for Disease Control and Prevention (CDC). National Report on Human Exposure to Environmental Chemicals: Chemical Information: Chlordane. Last updated November, 2010 [online].
- Lee D.; et al. (2007). "Association between serum concentrations of persistent organic pollutants and insulin resistance among nondiabetic adults: Results from the National Health and Nutrition Examination Survey". Diabetes Care. 30 (3): 622–628. doi:10.2337/dc06-2190. PMID 17327331.
- Kavita Singh, Wim J.M. Hegeman, Remi W.P.M. Laane, Hing Man Chan (2016). "Review and evaluation of a chiral enrichment model for chlordane enantiomers in the environment". Environmental Reviews. 24 (4): 363–376. doi:10.1139/er-2016-0015.CS1 maint: Multiple names: authors list (link)
- The 12 initial POPs under the Stockholm Convention
- Evangelou, E; et al. (2016). "Exposure to pesticides and diabetes: A systematic review and meta-analysis". Environment International. 91: 60–68. doi:10.1016/j.envint.2016.02.013. PMID 26909814.
- Luo, Dan; et al. (2005). "Exposure to organochlorine pesticides and non-Hodgkin lymphoma: a meta-analysis of observational studies". Scientific Reports. 6: 25768. doi:10.1038/srep25768. PMC 4869027. PMID 27185567.
- Lim, J.E.; et al. (2015). "Body concentrations of persistent organic pollutants and prostate cancer". Environmental Science Pullution Research International. 22 (15): 11275–84. doi:10.1007/s11356-015-4315-z. PMID 25797015.
- Tang-Peronard, J. L.; et al. (2011). "Endocrine-disrupting chemicals and obesity development in humans: a review". Obesity Reviews. 12 (8): 622–36. doi:10.1111/j.1467-789x.2011.00871.x. PMID 21457182.
- Cook, Michael B; et al. (2011). "Organochlorine compounds and testicular dygensis syndrome:human data". International Journal of Andrology. 34 (4): e68–e85. doi:10.1111/j1365-2605.2011.01171.x (inactive 2018-08-28).
- Khanjani, Narges; et al. (2007). "Systematic review and meta-analysis of cylodiene insecticides and breast cancer". Journal of Environmental Science and Health Part C. 25 (1): 23–52. doi:10.1080/10590500701201711. PMID 17365341.
- Colt Joanna S.; et al. (2006). "Residential Insecticde Use and Risk of non-Hodgkin's lymphoma". Cancer Epidemiology, Biomarkers & Prevention. 15 (2): 251–257. doi:10.1158/1055-9965-EPI-05-0556 (inactive 2018-08-28). PMID 16492912.
- Chlordane (Technical) (CASRN 12789-03-6) | IRIS | US EPA
- ATSDR - Medical Management Guidelines (MMGs): Chlordane
- J. M. Braun (2014). "Gestational Exposure to Endocrine-Disrupting Chemicals and Reciprocal Social, Repetitive, and Stereotypic Behaviors in 4-and 5-Year-Old Children:The HOME Study". Environmental Health Perspectives. 122: 513–520. doi:10.1289/ehp130761 (inactive 2018-08-28).
- ATSDR - Redirect - Toxicological Profile: Chlordane
- Medina, Victor F.; Scott A. Waisner; Agnes B. Morrow; Afrachanna D. Butler; David R. Johnson; Allyson Harrison; Catherine C. Nestler. "Legacy Chlordane in Soils from Housing Areas Treated with Organochlorine Pesticides" (PDF). US Army Corps of Engineers. Retrieved 10 October 2012.
- Kennedy, D.W.; S. D. Aust; J. A. Bumpus (1990). "Comparative biodegradation of alkyl halide insecticides by the White Rot fungus, Phanerochaete chrysosporium". Appl. Environ. Microbiol. 56:2347–2353.