Pyrethroid

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A pyrethroid is an organic compound similar to the natural pyrethrins, which are produced by the flowers of pyrethrums (Chrysanthemum cinerariaefolium and C. coccineum). Pyrethroids are used as commercial and household insecticides.[1]

In household concentrations pyrethroids are generally harmless to humans.[1] However, pyrethroids are toxic to beneficial insects such as bees, dragonflies, mayflies, gadflies, and some other invertebrates, including those that constitute the base of aquatic and terrestrial food webs.[2] Pyrethroids are toxic to aquatic organisms including fish.[3][4]

Mode of action[edit]

Pyrethroids are axonic excitotoxins, the toxic effects of which are mediated through preventing the closure of the voltage-gated sodium channels in the axonal membranes. The sodium channel is a membrane protein with a hydrophilic interior. This interior is shaped precisely to allow sodium ions to pass through the membrane, enter the axon, and propagate an action potential. When the toxin keeps the channels in their open state, the nerves cannot repolarize, leaving the axonal membrane permanently depolarized, thereby paralyzing the organism.[5] Pyrethroids can be combined with the synergist piperonyl butoxide, a known inhibitor of key microsomal cytochrome P450 enzymes from metabolizing the pyrethroid, which increases its efficacy (lethality).[6]

Chemistry and classification[edit]

(1R,3R)- or (+)-trans-chrysanthemic acid.

Pyrethroids are mostly defined as pyrethroids based on their biological action, as they do not have common chemical structures. They often contain some 2,2-dimethylcyclopropanecarboxylic acid derivative, like chrysanthemic acid, which is esterified with a large alcohol. Cyclopropyl does not occur in all pyrethroids. Fenvalerate, which was developed in 1972, is one such example and was the first pyrethroid without the cyclopropyl group. Fenvalerate also has an α-cyano group. Pyrethroids which lack this α-cyano group are often classified as type I pyrethroids and those with it are called type II pyrethroids. Some pyrethroids, like etofenprox, lack the ester bond found from most pyrethroids and have an ether bond in its place. Silafluofen is also classified as a pyrethroid and it has silicon atom in the place of an ester. Pyrethroids often have chiral centers and only certain stereoisomers work efficiently as insecticides.[7]

Examples[edit]

Environmental effects[edit]

Pyrethroids are toxic to beneficial insects such as bees, dragonflies, mayflies, gadflies, and some other invertebrates, including those that constitute the base of aquatic and terrestrial food webs.[2] They are toxic to aquatic organisms including fish.[3][4]

Biodegradation[edit]

Pyrethroids are usually broken apart by sunlight and the atmosphere in one or two days, however when associated with sediment they can persist for some time.[8]

Pyrethroids are unaffected by conventional secondary treatment systems at municipal wastewater treatment facilities. They appear in the effluent, usually at levels lethal to invertebrates.[9]

Safety[edit]

Humans[edit]

Pyrethroid absorption can happen via skin, inhalation or ingestion.[10] Pyrethroids often do not bind efficiently to mammalian sodium channels.[11] They also absorb poorly via skin and human liver is often able to metabolize them relatively efficiently. Pyrethroids are thus much less toxic to humans than to insects.[12]

It is not well established if chronic exposure to small amounts of pyrethroids is hazardous or not.[13] However, large doses can cause acute poisoning, which is rarely life threatening. Typical symptoms include facial paresthesia, itching, burning, dizziness, nausea, vomiting and more severe cases of muscle twitching. Severe poisoning is often caused by ingestion of pyrethroids and can result in a variety of symptoms like seizures, coma, bleeding or pulmonary edema.[10]

Other organisms[edit]

Pyrethroids are very toxic to cats, but not to dogs. Poisoning in cats can result in seizures, fever, ataxia and even death. Poisoning can occur if pyrethroid containing flea treatment products, which are intended for dogs, are used on cats. The livers of cats detoxify pyrethroids via glucuronidation more poorly than dogs, which is the cause of this difference.[14] Aside from cats, pyrethroids are typically not toxic to mammals or birds.[15] They are often toxic to fish, reptiles and amphibians.[16]

Resistance[edit]

Although bedbugs were almost eradicated in North America through the use of DDT and organophosphates, populations of bedbugs resistant to both have developed. The use of DDT for this purpose was banned, and its reintroduction would not offer a solution to the problem of bedbugs, due to resistance.[17] Pyrethroids became more commonly used against bedbugs, but resistant populations have now developed to them as well.[18][19][20][21] Diamondback moths are also resistant to pyrethroids.[22]

History[edit]

Pyrethroids were introduced by a team of Rothamsted Research scientists in the 1960s and 1970s following the elucidation of the structures of pyrethrin I and II by Hermann Staudinger and Leopold Ružička in the 1920s.[23] The pyrethroids represented a major advancement in the chemistry that would synthesize the analog of the natural version found in pyrethrum. Its insecticidal activity has relatively low mammalian toxicity and an unusually fast biodegradation. Their development coincided with the identification of problems with DDT use. Their work consisted firstly of identifying the most active components of pyrethrum, extracted from East African chrysanthemum flowers and long known to have insecticidal properties. Pyrethrum rapidly knocks down flying insects but has negligible persistence — which is good for the environment but gives poor efficacy when applied in the field. Pyrethroids are essentially chemically stabilized forms of natural pyrethrum and belong to IRAC MoA group 3 (they interfere with sodium transport in insect nerve cells).[24]

The first-generation pyrethroids, developed in the 1960s, include bioallethrin, tetramethrin, resmethrin, and bioresmethrin. They are more active than the natural pyrethrum but are unstable in sunlight. With the 91/414/EEC review,[25] many 1st-generation compounds have not been included on Annex 1, probably because the market is not big enough to warrant the costs of re-registration (rather than any special concerns about safety).

By 1974, the Rothamsted team had discovered a second generation of more persistent compounds notably: permethrin, cypermethrin and deltamethrin. They are substantially more resistant to degradation by light and air, thus making them suitable for use in agriculture, but they have significantly higher mammalian toxicities. Over the subsequent decades these derivatives were followed with other proprietary compounds such as fenvalerate, lambda-cyhalothrin and beta-cyfluthrin. Most patents have now expired, making these compounds cheap and therefore popular (although permethrin and fenvalerate have not been re-registered under the 91/414/EEC process).

References[edit]

  1. ^ a b Metcalf, Robert L (2000). Ullmann's Encyclopedia of Industrial Chemistry. Weinheim: Wiley-VCH. doi:10.1002/14356007.a14_263.
  2. ^ a b Zaveri, Mihir (February 4, 2010). "Study Links Pesticides to River Contamination". The Daily Californian. The Daily Californian. Retrieved 9 June 2012.
  3. ^ a b Thatheyus, A.J; Gnana Selvam, A.Deborah (2013). "Synthetic Pyrethroids: Toxicity and Biodegradation". Applied Ecology and Environmental Sciences. 1 (3): 33–6. doi:10.12691/aees-1-3-2.
  4. ^ a b Pyrethroids fact sheet from the Illinois Department of Public Health.
  5. ^ Soderlund, David M; Clark, John M; Sheets, Larry P; Mullin, Linda S; Piccirillo, Vincent J; Sargent, Dana; Stevens, James T; Weiner, Myra L (2002). "Mechanisms of pyrethroid neurotoxicity: Implications for cumulative risk assessment". Toxicology. 171 (1): 3–59. doi:10.1016/s0300-483x(01)00569-8. PMID 11812616.
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