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Tetramethrin


Tetramethrin is a synthetic developed in during the , valued for its rapid knockdown effect on household pests including flies, , , and wasps by disrupting their nervous systems. It exists as a white to colorless crystalline solid with the molecular formula C₁₉H₂₅NO₄ and a of 331.4 g/mol, offering improved stability over natural pyrethrins derived from flowers. Commonly formulated in aerosols, emulsifiable concentrates, and mosquito coils for indoor use, tetramethrin targets pests in residential settings, gardens, and on companion animals, though its application is limited to avoid environmental persistence due to rapid degradation in light and air. While exhibiting low to mammals (LD₅₀ >5000 mg/kg orally in rats), it poses risks to aquatic life and honey bees, necessitating careful handling to mitigate ecological impacts.

Chemical Properties

Structure and Physical Characteristics

Tetramethrin is a synthetic with the molecular formula C₁₉H₂₅NO₄ and molecular weight of 331.41 g/mol. Its structure features a carboxylic acid derived from 2,2-dimethyl-3-(2-methylprop-1-enyl)-1-carboxylic acid and (3,4,5,6-tetrahydro-1,3-dioxo-1H-isoindol-5-yl), forming a derivative. The ring introduces , resulting in and stereoisomers; commercial tetramethrin typically comprises a with 75–85% isomers. Physically, tetramethrin manifests as colorless crystals exhibiting a slight . It possesses a between 65 and 80 °C. The boiling point occurs at 180–190 °C under reduced (0.1 mm ). Density measures approximately 1.11 g/cm³ at ambient conditions. Tetramethrin demonstrates low solubility, rendering it practically insoluble (<0.002 g/100 mL), while exhibiting good in organic solvents like acetone and ethanol. Vapor pressure remains negligible at 20 °C, contributing to its stability in formulations.

Stability and Formulation

Tetramethrin demonstrates thermal stability, remaining intact after exposure to 50 °C for six months in technical grade form. However, it is unstable to light, air, and alkaline conditions, undergoing photodegradation and hydrolysis that limit its persistence in outdoor environments. The compound is stable in weakly acidic and neutral media but degrades via base-catalyzed hydrolysis in alkaline settings and shows sensitivity to strong acids, producing metabolites such as (1RS)-cis-chrysanthemic acid. Relative to natural pyrethrins, tetramethrin offers improved resistance to light and heat, though early pyrethroids like it remain more prone to photodegradation than later type II variants. These properties necessitate storage in opaque, airtight containers and avoidance of alkaline processing to maintain efficacy. In commercial formulations, tetramethrin is typically diluted to concentrations of 0.5–2% active ingredient and incorporated into aerosols, emulsifiable concentrates (ECs), and mosquito coils or mats for vaporization, targeting indoor pests where photodegradation risks are minimized. It is frequently synergized with to counteract insect metabolic resistance, enhancing knockdown and mortality rates while reducing recovery in target species. Compatibility with common solvents, emulsifiers, and other actives—such as in EC blends—allows versatile mixing without precipitation or loss of stability under neutral pH conditions. Formulations often include stabilizers like antioxidants to further protect against oxidative degradation during storage, ensuring a shelf life of up to two years when unopened. These designs prioritize rapid dispersion and low environmental persistence, aligning with its use in household and space-spray applications rather than persistent agricultural residues.

History and Development

Discovery and Synthesis

Tetramethrin was first synthesized in 1964 by Takeaki Kato, Kenzo Ueda, and Keimei Fujimoto at in Japan, marking it as the inaugural synthetic with potent knockdown activity against household pests such as flies and mosquitoes. This development stemmed from systematic efforts to create stable analogues of natural , derived from flowers, which suffered from rapid degradation by light and air, limiting their practical utility. Ueda's initial pursuit of an amide derivative from chrysanthemic acid derivatives unexpectedly led to explorations of N-hydroxymethyl-type structures, culminating in tetramethrin's identification after testing numerous candidates for insecticidal efficacy. The synthesis of tetramethrin involves esterification of racemic (1RS, cis,trans)-2,2-dimethyl-3-(2,2-dichlorovinyl)cyclopropanecarboxylic acid (a halomethylated analogue) with N-(3,4,5,6-tetrahydrophthalimido)methanol. This multi-step process typically begins with cyclopropane ring formation via carbene addition to alkenes, followed by side-chain modifications to introduce the dichlorovinyl group, and concludes with the key ester linkage to the phthalimide-derived alcohol, yielding the active compound as a mixture of stereoisomers. The resulting structure retains the ester motif essential for bioactivity while enhancing stability and knockdown speed compared to natural precursors.

Commercial Introduction and Evolution

Tetramethrin was developed by researchers at , as a synthetic emphasizing rapid knockdown effects against household pests. It was first registered for commercial use in Japan in 1964, marking an early advancement in pyrethroid insecticides following predecessors like . In the United States, the granted initial registration in 1968, enabling its deployment as a broad-spectrum, non-systemic insecticide for non-agricultural applications. Early commercial formulations focused on aerosols, emulsifiable concentrates, and mosquito coils for indoor pest management, targeting species such as flies, cockroaches, , and wasps. Its efficacy led to widespread adoption in household products, often synergized with other pyrethroids like to prolong residual activity and overcome insect resistance. Over subsequent decades, applications expanded to include veterinary shampoos for ectoparasite control, such as , while maintaining emphasis on low mammalian toxicity relative to earlier insecticides. Regulatory evolution reflected growing scrutiny of pyrethroid environmental persistence and non-target impacts; tetramethrin was withdrawn from the European Union market in 2010 amid reevaluations of synthetic insecticides. Despite this, it remains registered in regions like the United States for targeted uses in space sprays, crack-and-crevice treatments, and institutional settings, with formulations adapted for minimal drift and volatility. Ongoing research has explored stereoisomer-specific variants to optimize potency while addressing resistance in pest populations.

Mechanism of Action

Insecticidal Effects

Tetramethrin exhibits potent insecticidal activity characterized by rapid knockdown, a phenomenon where insects lose coordinated locomotion and become immobilized shortly after exposure. This effect occurs at low concentrations, often within seconds to minutes, particularly against flying insects such as houseflies (Musca domestica) and mosquitoes (Culex spp.), as well as crawling pests like cockroaches (Blattella germanica). The compound disrupts normal nerve signaling, leading to initial hyperexcitation manifested as tremors, spasms, and uncoordinated movements, followed by paralysis that prevents feeding, reproduction, or escape. While tetramethrin alone provides exceptional knockdown, its lethal efficacy is often augmented by synergists such as , which inhibit insect detoxifying enzymes, thereby prolonging exposure and increasing mortality rates. The spectrum of activity encompasses a broad range of household and public health pests, including wasps, ants, and stored-product insects, with formulations targeting both adults and larvae. In laboratory assays, tetramethrin demonstrates superior knockdown compared to natural pyrethrins, outperforming them in oil-based aerosols against resistant strains when combined with other pyrethroids like resmethrin. Its effects are species-dependent, with higher potency against dipterans and lepidopterans due to differences in nerve sensitivity and metabolic rates, though repeated exposure can select for resistance via enhanced cytochrome P450 activity. Overall, tetramethrin's fast-acting paralysis minimizes pest dispersal, making it suitable for space sprays and coils where immediate control is prioritized over residual persistence.

Mode of Toxicity

Tetramethrin, classified as a Type I , primarily induces toxicity by binding to voltage-gated sodium channels in neuronal membranes, thereby modifying their gating kinetics. This interaction prolongs the open state of the channels during depolarization, slowing their closure and generating persistent sodium tail currents without altering single-channel conductance or ion selectivity. The result is repetitive nerve firing and after-discharges, leading to neuronal hyperexcitation and disruption of normal impulse transmission. In insects, the target organisms, this mechanism manifests as rapid knockdown paralysis, with low concentrations (e.g., 3 × 10⁻¹³ mol/liter in cockroach sensory nerves) sufficient to elicit prolonged repetitive activity in axons and muscles. Tetramethrin modifies channels in resting, open, or inactivated states, but its effects are more pronounced on closed-state channels, contributing to selective insecticidal potency through differences in sodium channel isoforms and slower detoxification compared to mammals. In mammals, the mode of toxicity parallels that in insects, producing the characteristic "T-syndrome" of fine tremors, hyperexcitability, and choreoathetosis via central and peripheral nerve hyperexcitation. However, mammalian toxicity is limited by rapid enzymatic hydrolysis of the ester linkage by carboxylesterases and cytochrome P450 oxidation, resulting in transient effects and low overall acute toxicity (e.g., rat oral LD50 >5000 mg/kg).

Uses and Applications

Indoor Pest Control

Tetramethrin serves as a key in indoor formulations, including and trigger sprays, as well as total release foggers, applied via direct broadcast, spot treatments, or crack-and-crevice methods in residential and institutional environments such as homes, hotels, and restaurants. These products leverage its rapid knockdown properties to target urban and nuisance pests, including , flies, , wasps, and mosquitoes. The compound's efficacy stems from its action as a type I , disrupting insect nervous systems to induce quick and death, effective against a range of orders such as Diptera (flies and mosquitoes), Coleoptera (beetles), (), and others. It is often combined with synergists like to amplify insecticidal performance while maintaining low persistence indoors, as tetramethrin degrades relatively rapidly, reducing residual exposure risks. When applied as recommended, indoor aerial concentrations remain low, supporting its suitability for enclosed spaces. Tetramethrin's profile of low mammalian toxicity facilitates safe indoor deployment, with no identified risks to residential handlers under labeled conditions, though users must avoid drain disposal to prevent unintended environmental release. Its primary role emphasizes immediate control over long-term residual effects, making it complementary to strategies that incorporate sanitation and exclusion.

Outdoor and Agricultural Applications

Tetramethrin finds application in non-agricultural outdoor , including treatments for residential yards, gardens, and ornamental plants, where it targets flying and crawling such as mosquitoes, flies, and via foggers, sprays, or formulations. These uses emphasize urban and domestic settings rather than broad-scale field applications, with products often combined with synergists like to enhance against household and garden pests. Horticultural applications typically involve foliar sprays or fogging on non-food plants, avoiding direct contact with edible crops to prevent residue concerns. In agricultural contexts, tetramethrin lacks registration for direct use on food-bearing crops , with no established tolerances for residues in raw agricultural commodities, reflecting its classification as a non-food-use . While limited historical data indicate minimal application volumes in regions like as of 2007—primarily for non-crop pest management—its instability under sunlight and preference for indoor formulations restrict widespread outdoor agricultural adoption compared to more photostable pyrethroids. Regulatory assessments confirm no registered wide-area or crop treatments, prioritizing instead contained outdoor scenarios to minimize environmental drift and non-target exposure.

Human Health and Toxicology

Acute and Short-Term Effects

Tetramethrin exhibits low to mammals, with oral and dermal LD50 values in rats exceeding 2000 mg/kg, classifying it as Toxicity Category III or IV by these routes according to U.S. Environmental Protection Agency assessments. Dermal exposure primarily causes transient —a tingling or numbing sensation on the skin—along with mild and potential rash, effects typical of Type I pyrethroids due to sodium channel modulation in sensory nerves. results in , including redness and discomfort, but without permanent in standard tests. Inhalation of tetramethrin aerosols or vapors at high concentrations (e.g., above 87 mg/m³ in animal studies) can induce respiratory irregularities, salivation, hyperexcitability, and mild systemic symptoms such as or , though human exposure thresholds for such effects remain low under typical use. Short-term occupational or accidental exposures, as documented in case reports, have reported symptoms including (up to 60.6% of exposed workers), (44.5%), (26%), and increased salivation (20%), resolving without sequelae upon cessation. Gastrointestinal effects from oral are limited to transient or , with no evidence of severe poisoning in humans despite widespread commercial use since the . No fatalities or hospitalizations from acute tetramethrin exposure have been reported in peer-reviewed or toxicological profiles, underscoring its favorable safety margin for humans compared to target insects. Short-term repeated exposures do not appear to exacerbate acute effects beyond additive , based on intermediate-duration studies in showing no cumulative at doses below 100 mg/kg/day.

Long-Term Exposure Risks

No cases of adverse health effects from long-term tetramethrin have been reported in humans, despite decades of widespread use in and insecticides. Tetramethrin exhibits low mammalian , attributed to rapid and , resulting in minimal accumulation. Regulatory assessments, including those by the U.S. EPA, have concluded that chronic dietary or residential s pose negligible risks when used as directed, with margins of exposure exceeding 100-fold based on no-observed-adverse-effect levels (NOAELs) from . In chronic oral toxicity studies, rats fed tetramethrin for 104 weeks showed a NOEL of 1000 mg/kg diet, with reduced body weight and increased liver weights observed only at doses ≥3000 mg/kg diet; these hepatic changes were deemed adaptive rather than adverse. Mice exposed for 104 weeks had a NOEL of 12 mg/kg diet, with no treatment-related tumors or significant histopathological effects up to 1500 mg/kg diet. was noted in rats at 76 mg/kg body weight/day orally, but insufficient for classification as repeated-dose target organ toxicity. Tetramethrin has not been classified as carcinogenic by recent assessments, though the U.S. EPA's 1989 designated it a Group C possible human carcinogen based on increased tumors in male rats at 180–230 mg/kg body weight/day; these were considered species-specific, non-genotoxic, and hormonally mediated, with low relevance to humans due to absence of supporting epidemiological data. No evidence of mutagenicity was found across and assays. Reproductive and developmental toxicity studies in rats and rabbits showed no effects at doses up to 300 mg/kg body weight/day (parental and fetal NOEL), with minor skeletal anomalies in rabbits only secondary to maternal toxicity at 500 mg/kg body weight/day. Overall, long-term risks remain low for typical human exposures, which are far below thresholds eliciting effects in sensitive animal models.

Safety Measures and Exposure Mitigation

Tetramethrin poses low risk to human health when applied according to label instructions, with no reported cases of or adverse effects despite decades of use in indoor . The U.S. Environmental Protection Agency (EPA) has determined that residential and occupational handler exposures result in margins of exposure exceeding 30, indicating no concern, following the 2020 interim registration review that incorporated label amendments for safer use. Acceptable operator exposure limits are set at 0.045 mg/kg body weight per day, with atmospheric concentrations recommended not to exceed 0.5 mg/m³ during application. Personal protective equipment (PPE) for professional handlers includes gloves, ® or equivalent impermeable clothing, tight-fitting safety glasses, and NIOSH-approved respirators with organic vapor cartridges for high-exposure scenarios, though consumer products require no PPE. Safe handling mandates use in well-ventilated areas, avoidance of and eye contact, and immediate washing of exposed areas with soap and water; workers must not eat, drink, or smoke during application and should follow good practices to minimize absorption through or . Local exhaust ventilation is advised to control airborne particles, and spills should be covered to prevent spreading while avoiding dust generation. First aid measures emphasize rapid response: flush eyes with water for 15 minutes, wash with and water while removing contaminated clothing, and remove individuals from exposure for cases, providing or medical attention if symptoms like or occur. Storage requires tightly closed containers in cool, dry, well-ventilated areas away from ignition sources, strong oxidizers, acids, bases, , and ultraviolet light to prevent or accidental release. Disposal follows local regulations, prohibiting drain disposal, with EPA labels updated to direct users to waste agencies for proper handling. These measures, combined with restricted perimeter applications (limited to 7 feet from structures), effectively mitigate exposure risks.

Environmental Impact

Fate in the Environment

Tetramethrin exhibits low environmental persistence, primarily degrading through and . In air, it undergoes rapid photolysis with an estimated of 30 minutes. In aqueous environments, tetramethrin dissipates quickly via photolysis ( less than 1 day) and pH-dependent , with reported of 16-20 days at 5, approximately 1 day at 7, and less than 21 minutes at 9 (25°C). under sunlight yields products such as epoxides (14%), derivatives (19%), caronaldehyde (6%), and allylic hydroperoxides (6%), involving pathways like epoxidation of the double bond, oxidation of methyl groups to hydroxymethyl, , or forms, and cleavage. In , aerobic yields a of 32.7-33.3 days, classifying it as moderately persistent with primary degradation in about 13 days and ultimate mineralization of 33.3-57.6% after 30-122 days, increasing to 65-69.8% after 365 days. dissipation is faster, with DT50 values of 3 hours in soils and less than 1 hour in soils. The cis-isomer degrades slightly more slowly than the trans-isomer, while d-tetramethrin shows half-lives of 2.5-7.6 days. Tetramethrin displays low to slight mobility in soil, with Koc values ranging from 1,249 to 2,939, favoring adsorption to organic-rich matrices over leaching in low-organic soils.

Ecotoxicological Effects

Tetramethrin demonstrates high acute toxicity to aquatic organisms, with 96-hour LC50 values for fish species ranging from 0.0037 mg/L (rainbow trout, Oncorhynchus mykiss) to 21 µg/L (rainbow trout) and 19 µg/L (bluegill sunfish, Lepomis macrochirus). These endpoints classify tetramethrin as GHS Category 1 for acute aquatic toxicity, with a multiplication factor of 100 indicating substantial hazard potential. Acute toxicity to aquatic invertebrates is similarly elevated, evidenced by a 48-hour EC50 of 0.045 mg/L for Daphnia magna. Chronic exposure risks to aquatic life are also significant, warranting GHS Category 1 classification based on extrapolated data from acute fish toxicity studies. Tetramethrin shows potential for and is not rapidly biodegradable in aquatic environments, which may prolong localized impacts despite its overall low environmental persistence due to . Among terrestrial non-target species, tetramethrin is highly toxic to pollinators, with a 48-hour contact LD50 of 0.155 μg/bee for honeybees (Apis mellifera), classifying it as hazardous to terrestrial invertebrates. In contrast, avian toxicity is low, as indicated by an acute oral LD50 exceeding 2250 mg/kg in bobwhite quail (Colinus virginianus). These profiles underscore tetramethrin's selective ecotoxicological profile, posing greater risks to aquatic ecosystems and beneficial insects than to birds.

Mitigation and Alternatives

To mitigate the environmental release and ecotoxicological effects of tetramethrin, regulatory measures emphasize preventing runoff into aquatic systems and improper disposal. The U.S. Environmental Protection Agency (EPA) requires labeling on tetramethrin products to prohibit pouring down drains or sewers, with prominent disposal instructions directing users to local solid waste agencies, and includes a drain pictogram on consumer products to visually reinforce these restrictions. Application guidelines limit perimeter treatments around buildings to 7 feet on pervious surfaces, restrict spot treatments to no more than 2 square feet, and mandate 25-foot buffers from water bodies for soil or foliar uses, alongside prohibitions on applications during rain or when is forecast within 4 hours to minimize contamination. Wind speeds are capped at 15 mph for certain outdoor applications to reduce drift. Integrated pest management (IPM) practices further reduce tetramethrin's environmental footprint by minimizing overall applications through monitoring, cultural controls, and biological agents before resorting to chemical interventions. Studies demonstrate that IPM can cut use by up to 95% while sustaining yields or efficacy, including reduced reliance in urban settings by 75% via targeted scouting and non-chemical thresholds. For like tetramethrin, IPM incorporates resistance management by rotating modes of action and integrating habitat modifications, such as sanitation and exclusion, to limit broad-spectrum spraying. Alternatives to tetramethrin include lower-persistence biological and botanical options for household and agricultural pests. Microbial insecticides like Bacillus thuringiensis (Bt) target specific lepidopteran larvae with minimal non-target effects and rapid biodegradation, serving as substitutes in integrated programs for flying insects. Spinosad, derived from soil bacteria, offers effective control against ants, cockroaches, and flies with lower aquatic toxicity than pyrethroids, though it requires careful application to avoid bee exposure. Non-pyrethroid chemicals such as indoxacarb or abamectin provide ant and cockroach control with reduced environmental mobility, while insecticidal soaps, horticultural oils, and diatomaceous earth enable mechanical disruption of pests like aphids and soft-bodied insects without synthetic residues. Pyrethrins from chrysanthemum extracts mimic tetramethrin's action but degrade faster in sunlight (half-life of 1-2 days), posing a biodegradable option despite similar acute toxicity profiles. These alternatives prioritize specificity and shorter persistence but may necessitate more frequent applications compared to tetramethrin's residual effects.

Regulatory Framework

Approvals and Assessments

The U.S. Environmental Protection Agency (EPA) issued a Reregistration Eligibility Decision (RED) for tetramethrin in July 2008, determining it eligible for continued registration for non-agricultural uses such as indoor space sprays and pet collars, with requirements for labeling to mitigate risks from and dermal . The EPA confirmed no direct applications to food crops and established tolerances for residues in or on food only from indirect contamination, such as from treated premises. In September 2020, the EPA released an Interim Registration Review Decision, affirming low human health risks under labeled use conditions while requiring further data on ecological effects and confirming no concerns necessitating additional mitigation at that stage. The Joint FAO/WHO Meeting on Pesticide Residues (JMPR) has not established an (ADI) or acute reference dose for tetramethrin due to its lack of registered agricultural uses, but the International Programme on Chemical Safety (IPCS), under WHO, evaluated its toxicology in Environmental Health Criteria 98 (1990), classifying it as having low acute oral, dermal, and inhalational toxicity in mammals (LD50 >2,000 mg/kg in rats) while noting rapid metabolism and excretion, with potential for transient neurotoxic symptoms like tremors at high doses. An earlier WHO Health and Safety Guide (HSG 31, 1989) recommended precautions for handling, including protective equipment, based on its irritancy to eyes and skin in animal studies. In the , tetramethrin is regulated primarily under biocidal product frameworks rather than plant protection products, with no specific EFSA peer-reviewed for agricultural residues identified, reflecting its primary indoor applications; national approvals vary, often aligning with low mammalian profiles similar to EPA evaluations.

Restrictions and Global Variations

In the United States, the Environmental Protection Agency (EPA) determined tetramethrin eligible for reregistration in 2008, concluding that the supporting database was substantially complete and that registered products met safety standards with appropriate labeling and use restrictions. An interim registration review decision issued on September 29, 2020, confirmed continued eligibility while requiring mitigations for ecological risks, particularly to aquatic invertebrates, such as prohibiting direct application to water bodies and limiting outdoor uses. In the , tetramethrin was not approved under Directive 91/414/EEC (repealed by Regulation (EC) No 1107/2009) following review in 2002, and it remains unapproved as a under Biocidal Products Regulation (EU) No 528/2012, with ongoing applications for limited insecticide uses under evaluation as of recent assessments. Post-Brexit, the classified tetramethrin as a category 2 (suspected ) effective March 2020, mandating updated safety labeling for products containing it, though indoor uses persist under controlled conditions. Canada's Pest Management Regulatory Agency proposed label amendments in 2016 to restrict tetramethrin applications near water, enhance requirements, and prohibit certain broadcast uses, reflecting re-evaluation findings on environmental persistence and toxicity. In , tetramethrin holds Hazardous Substances and New Organisms (HSNO) approval (HSR003266) with controls limiting exposure and environmental discharge, permitting its use in indoor products. Global variations emphasize protections against aquatic ecotoxicity, with approvals in jurisdictions like the , , and confined primarily to non-agricultural, indoor applications, while the EU's non-approval effectively restricts for plant protection products. No comprehensive bans exist in major economies, but formulations combining tetramethrin with synergists like face scrutiny in some regions for amplified risks.