Fact-checked by Grok 2 weeks ago

Cyfluthrin

Cyfluthrin is a synthetic with the molecular formula C₂₂H₁₈Cl₂FNO₃ and a molecular weight of 434.3 g/. Developed as a broad-spectrum contact and stomach poison, it targets the nervous systems of by disrupting sodium channels, leading to hyperexcitation, , and death. First registered for use in the United States by the Environmental Protection Agency in 1987, it appears in over 150 commercial products, including emulsifiable concentrates, granules, aerosols, and foggers. Cyfluthrin is applied in agricultural settings to protect crops such as , corn, soybeans, fruits, , and from pests including cutworms, , , and weevils, with typical application rates ranging from 0.0125 to 0.05 pounds per acre. In non-agricultural uses, it controls household and structural pests like , , , fleas, mosquitoes, and flies in homes, yards, livestock facilities, and programs, often via aerial spraying or ear tags. Its low solubility (approximately 0.003 mg/L at 20°C) and moderate persistence in (half-life of 2–56 days) contribute to its effectiveness, though it degrades faster in sunlight-exposed environments or high-organic soils. While less toxic to mammals due to rapid metabolism and excretion (98% within 1–2 days), cyfluthrin can cause moderate acute toxicity in humans, including nausea, headaches, and skin or eye irritation upon exposure, classifying it as EPA Toxicity Category II for most formulations. It poses significant ecological risks, being highly toxic to bees, fish, and aquatic invertebrates, with regulatory mitigations such as 25-foot vegetative buffer strips required to reduce runoff and drift. The EPA's 2020 interim registration review confirmed no unacceptable human health risks after refinements but mandated label updates for pollinator and aquatic protection.

Introduction

Definition and Classification

Cyfluthrin is a synthetic belonging to the type II subclass, designed as an analog of the naturally occurring pyrethrins extracted from flowers. Pyrethroids, including cyfluthrin, replicate the neurotoxic effects of pyrethrins on nervous systems while providing improved environmental and persistence. As a non-systemic , cyfluthrin operates primarily through contact and stomach action, targeting the to disrupt function in pests, resulting in rapid knockdown and prolonged residual activity. It is recognized as a broad-spectrum effective against a diverse array of , including those in agricultural, structural, and settings. The distinction between type I and type II pyrethroids lies in the presence of an alpha-cyano group in the latter, such as cyfluthrin, which enhances potency—particularly via —compared to type I variants that lack this structural feature and primarily induce repetitive nerve firing. Commercially, cyfluthrin is supplied as 10–25% liquid concentrates, which are diluted for application in formulations.

History and Development

Cyfluthrin emerged as part of the broader evolution of synthetic pyrethroids, which originated from natural pyrethrins isolated from flowers in the 19th century. Building on post-World War II advancements, such as the 1949 invention of allethrin by the U.S. Department of Agriculture, researchers in the sought to develop photostable analogs with enhanced insecticidal potency and residual activity compared to natural pyrethrins. In 1977, Bayer AG developed cyfluthrin through targeted modifications to existing structures, incorporating an alpha-cyano group at the 3-phenoxybenzyl moiety to increase against a range of pests while improving environmental stability. This innovation addressed limitations of earlier non-cyano pyrethroids like , resulting in a type II pyrethroid with prolonged sodium channel disruption in nerves for greater potency. The compound's key patent, DE 2709264, was filed on March 3, 1977, by inventors Rainer Fuchs, Ingeborg Hammann, Wolfgang Behrenz, and others, assigning rights to Bayer AG and describing its arthropodicidal esters. Cyfluthrin was introduced commercially in 1981 as a under the trade name Baythroid, marking its market entry for agricultural applications. Initial testing demonstrated its efficacy against key cotton pests through and . This launch positioned cyfluthrin as a significant advancement in chemistry, influencing subsequent formulations and enrichments like beta-cyfluthrin.

Chemical Properties

Molecular Structure and Formula

Cyfluthrin is a synthetic with the molecular \ce{C22H18Cl2FNO3}. Its molecular weight is 434.29 g/. The molecule consists of an linkage between 3-(2,2-dichlorovinyl)-2,2-dimethylcarboxylic acid and cyano(4-fluoro-3-phenoxyphenyl), forming the core pyrethroid skeleton characteristic of type II pyrethroids, which includes a ring substituted with a dichlorovinyl group and methyl groups, connected via the to a derivative bearing a cyano group at the alpha position and a phenoxy substituent ortho to the fluoro group on the ring. This structure mimics natural pyrethrins found in flowers but incorporates synthetic modifications for enhanced stability. Cyfluthrin possesses three chiral centers—two on the ring (leading to cis-trans isomerism) and one at the benzylic carbon bearing the cyano group—resulting in eight possible stereoisomers that form four diastereomeric pairs, typically denoted as isomers I through IV based on chromatographic retention times. In the technical-grade product, these diastereoisomers are present in specific proportions: 23-27% isomer I, 17-21% isomer II, 32-36% isomer III, and 21-25% isomer IV.

Physical and Chemical Characteristics

Cyfluthrin appears as a viscous to brown or partly crystalline oil, though it may present as brown crystals with a characteristic depending on purity and composition. Its is 60°C (140°F), above which it transitions from a solid to a . Cyfluthrin exhibits very low in , approximately 2–3 μg/L at 20°C and 7, rendering it practically insoluble and limiting its mobility in aqueous environments. In contrast, it is highly soluble in solvents, such as acetone (>250 g/L at 20°C), n-hexane (10 g/L at 20°C), and (200 g/L at 20°C), facilitating its formulation and application. The compound remains stable under neutral and acidic conditions but undergoes in alkaline media, with a of 33–42 hours at 9 and 20°C. It is photostable under normal conditions yet degrades gradually upon extended exposure to . Cyfluthrin has a low of approximately 3 × 10^{-7} at 20°C, signifying minimal and reduced risk of airborne dispersion during handling. Its is log K_{ow} = 6.0 at 20°C and 7, reflecting high that enhances partitioning into phases. This property contributes to its potential for in fatty tissues.

Production

Synthesis Methods

Cyfluthrin is synthesized through a multi-step process typical of pyrethroid esters, involving the coupling of a cyclopropanecarboxylic acid derivative with a fluorinated benzyl cyanohydrin alcohol. The primary reaction is esterification, where 3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylic acid (or its acid chloride) is reacted with 2-hydroxy-2-(4-fluoro-3-phenoxyphenyl)acetonitrile under acidic conditions, often in a hydrocarbon solvent like toluene at reflux temperatures of 75–115°C, to form the ester linkage. This step proceeds without an acid acceptor to minimize epimerization and preserve the stereochemistry of the starting materials, yielding 87–99% based on the limiting reactant. Key preparatory steps focus on constructing the acid and components. For the acid moiety, introduces the dichlorovinyl group via of 4,6,6,6-tetrahalo-2,2-dimethylhexanoates or stereoselective followed by Wittig olefination with dichloromethylenetriphenylphosphorane, starting from chrysanthemic acid analogs. The alcohol component involves fluorination of the ring at the 4-position, typically from 2-fluoro-5-nitrophenol etherified with phenylboronic acid derivatives, followed by reduction to the and diazotization, then cyano group addition via condensation of the resulting 4-fluoro-3-phenoxybenzaldehyde with or in the presence of , forming the . Standard synthesis employs dehalogenation precursors for the , while labeled variants (e.g., for research) use catalysts like for deuteration or incorporation during selective reductions. A major challenge is controlling across the three chiral centers—the ring and the carbon—resulting in eight possible isomers; this is achieved by using enantiopure or diastereomer-enriched precursors, such as (1R,3R)-acid chlorides, to favor bioactive cis/trans ratios like 51.8:48.2. Purification typically involves washing with aqueous base (e.g., ) to remove impurities, followed by solvent evaporation and to isolate desired diastereomers, with overall yields for multi-step routes ranging from 52–87% depending on .

Commercial Formulations and Isomers

Cyfluthrin is commercially available as a technical-grade with a minimum purity of 920 g/kg, consisting of a of four diastereoisomers in specified proportions to ensure consistent . The diastereoisomer includes 23-27% diastereoisomer I, 17-21% diastereoisomer II, 32-36% diastereoisomer III, and 21-25% diastereoisomer IV, as defined by FAO specifications to meet regulatory standards for quality and performance. These proportions are verified through methods such as normal-phase (HPLC) to confirm the material's identity and isomer balance in both technical and formulated products. A key variant, beta-cyfluthrin, is an enriched form of cyfluthrin with a higher concentration of the biologically more active diastereoisomers II and IV, achieving a technical-grade purity of at least 965 g/kg. In beta-cyfluthrin, diastereoisomer II comprises 30-40% and diastereoisomer IV 57-67%, while isomers I and III are minimized to ≤2-3%, enhancing potency against target pests compared to the full isomer mix in standard cyfluthrin. This enrichment, analyzed via HPLC, allows for lower application rates while maintaining or improving insecticidal effectiveness, and beta-cyfluthrin is treated as a distinct compound in regulatory evaluations. Commercial formulations of cyfluthrin and beta-cyfluthrin are designed for diverse applications, including emulsifiable concentrates () typically containing 10-25% , wettable powders (WPs), suspension concentrates (), emulsion in water (EW), ultra-low volume () liquids, granules, and aerosols. Notable examples include Baythroid XL, an EC formulation of beta-cyfluthrin (12.7% ) used in crop protection, and SC , an SC with 11.8% beta-cyfluthrin for structural . These formulations must adhere to FAO tolerances, such as ±10-15% for declared content and stability tests under storage conditions like 0°C and 54°C, ensuring emulsification and suspensibility for practical use. Isomer-specific activity varies, with diastereoisomers II and IV in beta-cyfluthrin demonstrating the highest potency against a broad spectrum of insects, including lepidopterans and sucking pests, due to their enhanced binding to sodium channels in neuronal membranes. Regulatory specifications, such as those from the FAO, mandate the 23-27% proportion for isomer I in technical cyfluthrin to balance overall efficacy and minimize less active components, while beta-cyfluthrin formulations prioritize the enriched active isomers for optimized performance. Global production of cyfluthrin, originally developed by Bayer, is now supplemented by generic manufacturers, with output scaled to meet regional demands for pest management in agriculture and public health, contributing to a market valued at approximately USD 343 million in 2024.

Applications

Agricultural Uses

Cyfluthrin is widely used in agriculture as a broad-spectrum pyrethroid insecticide for foliar applications to protect various crops from chewing and sucking pests. Primary crops include cotton, corn, soybeans, vegetables such as tomatoes and peppers, fruits like citrus and grapes, and grains like wheat and sunflowers. In cotton production, it effectively targets bollworms, tobacco budworms, plant bugs, and stink bugs, while in vegetables, it controls caterpillars, aphids, and leafhoppers. For fruits and tree nuts, applications address mites, beetles, and lygus bugs, and in grains, it manages weevils, armyworms, and grasshoppers. Application rates typically range from 0.01 to 0.05 kg per , often delivered as emulsifiable concentrates via ground, aerial, or chemigation methods for contact and stomach action. For example, in corn, rates of 0.8–2.8 fl oz/acre (approximately 0.007–0.025 kg ai/ha) control European corn borers and cutworms, with similar dosages used for aphids and weevils in respective crops. Pre-harvest intervals are generally short, ranging from 0 to 7 days for many and , allowing flexibility in harvest scheduling, though longer intervals like 21–45 days apply to grains and s. Cyfluthrin provides rapid knockdown of pests within hours through nerve paralysis, offering immediate protection during vulnerable crop stages. It delivers residual control on treated foliage for up to 7 days, reducing the need for frequent reapplication while supporting resistance management when rotated with other classes. Its compatibility with (IPM) programs stems from targeted efficacy against key pests like tobacco budworms in tobacco and weevils in stored grains, minimizing disruption to beneficial when applied with proper timing and drift mitigation.

Household and Public Health Uses

Cyfluthrin is employed in household pest management to control a range of indoor insects, including , , , fleas, and bed bugs, through targeted applications that minimize exposure in living spaces. Common methods include crack-and-crevice treatments and sprays, which deliver the directly to pest harborages such as baseboards, voids, and entry points. Ready-to-use liquid formulations, typically at 0.05% , allow for spot treatments on surfaces like floors and walls, providing residual efficacy against crawling pests for several weeks. In structural protection, cyfluthrin targets and other wood-infesting around homes via perimeter barrier sprays applied to foundations and soil, creating a protective zone up to 7 feet wide. Reapplication is recommended every 3 to 6 months to maintain residual activity, depending on environmental factors and pressure. For applications, cyfluthrin serves in programs to manage mosquitoes, flies, and ticks that transmit , often through outdoor barrier sprays around residential and public structures. districts apply ultra-low volume (ULV) formulations via aerial or ground methods, exempt from certain buffer zones to facilitate rapid response in disease outbreaks. It demonstrates against houseflies at WHO-recommended doses of 0.03 g per square meter, achieving high mortality rates in resistance monitoring. In malaria-endemic areas, pyrethroids like cyfluthrin contribute to integrated vector management, including indoor residual spraying and space treatments, though resistance patterns necessitate rotation with other classes. products, such as controlled-release microencapsulated sprays, ensure knockdown of flying within 24 to 48 hours while providing extended protection.

Mechanism of Action

Insecticidal Effects

Cyfluthrin exhibits rapid knockdown effects on target , inducing through overstimulation of the , often within minutes to hours of exposure. This initial response manifests as constant muscle spasms, leading to immobilization that prevents feeding and movement. The compound's and stomach poison action facilitates quick penetration, making it particularly effective against both chewing pests, such as and caterpillars, and sucking pests, like and mosquitoes. Following knockdown, lethal effects result in insect death as paralysis progresses to starvation or direct neurotoxic failure. This process is observed in various studies on stored-product and agricultural pests. Cyfluthrin's efficacy ties briefly to its disruption of sodium channels in insect nerves, amplifying the overstimulation that culminates in fatality. The demonstrates a broad spectrum of activity, with high efficacy against orders such as (e.g., moths and ), Coleoptera (e.g., beetles and weevils), and Diptera (e.g., flies and mosquitoes). It controls a range of pests in field and structural settings, though effectiveness may be reduced in strains exhibiting due to repeated exposure. Residual persistence on treated surfaces varies by and environmental factors, generally lasting several days to weeks and allowing sustained control against reinfestation.

Biochemical Interactions

Cyfluthrin, a synthetic , primarily targets voltage-gated sodium channels (VGSCs) in the nerve axons of , binding to specific receptor sites on the alpha subunit of these channels. This modifies the gating of the VGSCs, preventing their from the open to the inactivated and thereby prolonging sodium influx during membrane depolarization. As a result, the channels remain open longer than normal, leading to repetitive nerve firing and eventual disruption of nerve impulse transmission, which causes hyperexcitation and in the target . As a Type II , cyfluthrin possesses an alpha-cyano group attached to the alpha-carbon of the moiety, which distinguishes it from Type I pyrethroids and enhances its binding affinity to VGSCs. This structural feature increases the potency of the by stabilizing the open state of the channel more effectively, producing a characteristic prolonged sodium tail current and promoting greater through sustained without initial repetitive discharges. The alpha-cyano group also slows the rate of , further contributing to its prolonged action on nervous systems. The selectivity of cyfluthrin for over mammals arises partly from differences in ; possess less efficient carboxylesterases and enzymes, which results in slower of the bond in pyrethroids compared to mammals, where rapid hepatic converts cyfluthrin to inactive, water-soluble metabolites. Additionally, VGSCs exhibit higher sensitivity to pyrethroids due to subtle amino acid differences, such as at position 918 versus in mammals, making channels approximately 10 to 100 times more susceptible to modification. Resistance to cyfluthrin in populations often develops through knock-on in the voltage-gated genes, such as the knockdown resistance (kdr) mutation L1014F or the super-kdr mutation M918T (also known as M918L), which alter the 's structure and reduce the binding affinity of the . These point , particularly in the S6 segments of domains and III, sterically hinder access to the , thereby decreasing the prolongation of opening and conferring varying levels of resistance across species like mosquitoes and agricultural pests.

Toxicology and Safety

Human Health Effects

Cyfluthrin exposure in humans primarily occurs through dermal or during occupational handling of formulations, with rare instances of oral from accidental . Due to its rapid in mammals, systemic effects are uncommon, as the compound is quickly hydrolyzed in the liver to inactive metabolites, with about 40% excreted in within 48 hours. Acute dermal exposure often results in transient paresthesia, characterized by tingling, numbness, itching, or burning sensations on contact areas, which typically resolve within 1-2 days but may persist for weeks in severe cases; these symptoms are exacerbated by or . Inhalation of cyfluthrin aerosols or dust can cause respiratory irritation, including coughing, sneezing, and mild , along with systemic symptoms such as , , , and . Acute oral exhibits low , with LD50 values exceeding 500 mg/kg depending on the , though high doses may induce neurotoxic symptoms like tremors, muscle fasciculations, and . Chronic exposure to cyfluthrin has been associated with potential neurotoxic effects, including possible cognitive impairments or neurological symptoms in pesticide applicators, though no permanent damage has been documented. inflammation may occur with prolonged exposure, as indicated by showing effects on multiple systems, but data remain limited. Standard tests indicate no carcinogenicity or in humans, with the U.S. EPA classifying cyfluthrin as "not likely to be carcinogenic" based on studies, and minimal impact on or . The EPA's 2020 interim registration review confirmed the existing profile with no unacceptable risks. Overall, cyfluthrin demonstrates lower to humans compared to aquatic species.

Mammalian Toxicity Data

Cyfluthrin exhibits moderate via the oral route in mammals, with reported LD50 values in rats ranging from 590 to 869 mg/kg in males and 1189 to 1271 mg/kg in females when administered in vehicle. The dermal LD50 in rats exceeds 5000 mg/kg, indicating low acute dermal . For , the 4-hour LC50 in rats is greater than 0.96 mg/L, classifying it as moderately toxic by this route. In subchronic and chronic exposure studies, the (NOAEL) for cyfluthrin was established at 9.5 mg/kg/day (125 ) in a 13-week dietary rat study, based on the absence of significant effects at this dose. At higher doses, such as 38 mg/kg/day, effects included reduced body weight gain and neurobehavioral changes like decreased motor activity. In a 2-year chronic dietary study in rats, the NOAEL was 6.2 mg/kg/day, with body weight reductions observed at 12.4 mg/kg/day. Developmental toxicity studies in rats and rabbits showed no evidence of teratogenicity across tested doses. The NOAEL for developmental effects was 10 mg/kg/day in rats and 20 mg/kg/day in rabbits, with slight maternal , including reduced , noted at higher doses such as 42 mg/kg/day in rats and 60 mg/kg/day in rabbits. Reproductive assessments in rats identified a NOAEL of 34.7 mg/kg/day, with no adverse effects on or offspring viability at the highest tested dose. Key mammalian toxicity evaluations by the U.S. Environmental Protection Agency highlight potential, including functional observational battery changes in rats at doses above 2 mg/kg/day in acute studies. EPA assessments also reference studies in hens showing symptoms of at high doses (e.g., 500 mg/kg bw) but no evidence of delayed neuropathy or fiber degeneration. These animal data align with observed neurobehavioral symptoms in human exposure cases, such as tremors and .

Environmental Impact

Fate in the Environment

Cyfluthrin exhibits moderate persistence in , where it primarily undergoes aerobic microbial degradation with a typical of 33 days under conditions, though values can range from 7 to 90 days depending on , , and microbial activity. conditions extend this significantly, with studies showing only gradual decline over 140 days in heavy clay soils. The compound binds strongly to , with organic carbon-water partition coefficients (Koc) ranging from 73,000 to 180,000 mL/g, which greatly limits its mobility and potential for into . In aquatic environments, cyfluthrin's low solubility (approximately 0.0066 mg/L at 7 and 20°C) further restricts its dissolution and transport, minimizing risks from soil applications. It hydrolyzes slowly under neutral conditions, with a degradation time for 50% (DT50) of about 215 days at 7 and 20°C, though this accelerates to 1.6 days at 9. in is more rapid, achieving a DT50 of 1 day at 7 in the presence of , primarily through cleavage of the ester bond. In -sediment systems, overall DT50 is around 8 days, with faster dissipation in the water phase due to combined microbial and photolytic processes. Cyfluthrin has low volatility due to its of about 2 × 10^{-9} mm at 25°C, reducing atmospheric transport, though any airborne residues degrade quickly via photolysis with a of 1–2 days under exposure. Bioaccumulation potential is moderate to high in aquatic organisms, evidenced by a bioconcentration factor (BCF) of 506 in , but rapid and depuration (CT50 of 9 days) limit long-term buildup in tissues. Primary degradation pathways involve microbial ester hydrolysis in and water, yielding key metabolites such as 3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylic acid and 4-fluoro-3-phenoxybenzoic acid, which are less persistent and further mineralized to .

Ecotoxicity to Non-Target Organisms

Cyfluthrin exhibits extremely high toxicity to aquatic organisms, posing significant risks to freshwater ecosystems through direct exposure or runoff. For instance, the 96-hour LC50 for rainbow trout (Oncorhynchus mykiss) is reported as 0.68 μg/L in static tests, indicating acute lethality at very low concentrations. Similarly, the 48-hour LC50 for the water flea (Daphnia magna) is 0.00014 μg/L (0.14 ng/L), classifying cyfluthrin as one of the most potent pyrethroids against aquatic invertebrates. These values underscore its potential to disrupt aquatic food webs, with sublethal effects such as impaired reproduction and locomotion observed in surviving populations. Pollinators, particularly honey bees (Apis mellifera), face severe threats from cyfluthrin due to its high contact toxicity, with an acute LD50 of 0.025 μg/bee, leading to rapid mortality and potential colony disruption through foraging exposure. This toxicity extends to non-target insects beneficial in (IPM), such as ladybugs () and predatory mites, where cyfluthrin causes broad-spectrum mortality that reduces natural pest control efficacy. In contrast, cyfluthrin shows low to birds, with avian oral LD50 values exceeding 2000 mg/kg in species like bobwhite quail and mallard ducks, suggesting minimal direct risk to avian populations from ingestion. Earthworms () experience moderate toxicity from cyfluthrin, with a contact LC50 of 0.5 μg/cm² in assays, which can reduce and affect nutrient cycling in treated . Field studies on agricultural runoff have detected cyfluthrin in sediments at concentrations exceeding U.S. EPA aquatic life benchmarks by factors of 10 to 100 times, particularly following storm events in urban and cropland watersheds, amplifying exposure to benthic organisms. This sediment contamination, often linked to its moderate persistence in soils, prolongs ecological risks in receiving waters.

Approvals and Restrictions

Cyfluthrin was unconditionally registered by the (EPA) on December 30, 1987, for use as an in agricultural and non-agricultural settings. The EPA has established tolerances for cyfluthrin residues in over 50 raw agricultural commodities under 40 CFR 180.436, with maximum levels ranging from 0.01 ppm (e.g., in processed foods) to 12 ppm (e.g., in grass ), including 0.2 ppm for , undelinted seed. To protect environments, EPA restrictions prohibit direct applications to water bodies or areas where is present, and labels require no aerial applications over habitats; for ultra-low volume (ULV) aerial applications, no applications within 450 feet of such areas; for other aerial applications, within 150 feet; and for ground applications, within 25 feet, to prevent drift and runoff. In the , cyfluthrin is no longer approved as an active substance for plant protection products under Regulation (EC) No 1107/2009, with the approval expiring on April 30, 2014, following a non-renewal decision. Current maximum residue levels (MRLs) for cyfluthrin have been reduced to the default value of 0.01 mg/kg for most food commodities, reflecting its non-approved status, though higher levels up to 0.5 mg/kg apply in specific cases like certain animal products. Prior to expiration, risk mitigation measures included mandatory buffer zones near water bodies to minimize spray drift and protect non-target aquatic organisms. Health Canada's Pest Management Regulatory Agency (PMRA) completed a re-evaluation of in 2018 (Re-evaluation Decision RVD2018-35), confirming its continued registration for agricultural uses but imposing limits on non-agricultural applications to reduce human exposure risks. These include restrictions to spot or crack-and-crevice treatments only, with no broadcast sprays or space sprays permitted indoors, and ventilation requirements post-application. Cyfluthrin pesticide labels in the and generally require the signal word "Caution" due to its moderate profile. Handlers must wear (PPE), including long-sleeved shirts, long pants, shoes, socks, and chemical-resistant gloves, with additional respiratory protection for certain mixing/loading activities. The restricted-entry interval () is 12 hours in the , during which treated areas must not be entered without appropriate PPE, while Canadian labels specify a 6-hour re-entry period for people and pets after application dries.

International Variations

The (WHO) classifies cyfluthrin as moderately hazardous (Class II) based on its acute oral profile. It recommends cyfluthrin for in tropical regions, particularly for indoor residual spraying against vectors, with precautions to mitigate risks to applicators and non-target . In and , cyfluthrin is approved for agricultural and uses similar to those in other regions, including in crops and households. However, maximum residue limits (MRLs) are generally stricter; if no specific MRL is established, residues above 0.01 mg/kg (limit of quantification) are not permitted, with specific values such as 0.2 mg/kg for tomatoes. Beta-cyfluthrin, an isomer-enriched variant, is often preferred in formulations due to its enhanced efficacy and stability. In developing countries across and , cyfluthrin is widely employed for vector control through indoor spraying and treated materials, contributing to reduced in endemic areas. For instance, studies in demonstrate its effectiveness in impregnated nets for lowering incidence. However, import and use restrictions exist in parts of due to widespread insecticide resistance in vectors like culicifacies. Regulatory differences are notable globally: the does not approve cyfluthrin for plant protection products following the expiration of its authorization in 2014, leading to lowered MRLs (often 0.01 mg/kg as the limit of quantification) and bans on certain emulsifiable concentrate formulations to protect aquatic environments near water bodies. No full global bans exist, though phase-outs occur in systems that prohibit synthetic insecticides. Ongoing re-assessments, such as the U.S. EPA's 2020 interim registration review (which as of March 2025 remains ongoing with no final decision), evaluate risks to support continued use with mitigation measures. International trade is facilitated by MRLs, which harmonize standards; for example, 0.05 mg/kg applies to bananas and certain spice fruits, aiding export compliance across borders.

References

  1. [1]
    Cyfluthrin | C22H18Cl2FNO3 | CID 104926 - PubChem - NIH
    The WHO Recommended Classification of Pesticides by Hazard identifies Cyfluthrin and beta-Cyfluthrin (technical grade) as Class II: moderately hazardous; Main ...
  2. [2]
    Cyfluthrin Fact Sheet - National Pesticide Information Center
    Cyfluthrin is used to control pests like ants, silverfish, cockroaches, termites, weevils, fleas, mosquitoes and flies.
  3. [3]
    EXTOXNET PIP - CYFLUTHRIN - Oregon State University
    Water Solubility: 0.002 mg/ml @ 20 degrees C. Solubility in Other Solvents: > 200 g/l in dichloromethane and toluene, 10-20 g/l hexane, 20-50 g/l propan-2-ol. ...
  4. [4]
    ICSC 1764 - Cyfluthrin - INCHEM
    Melting point: 60°C Solubility in water, mg/l at 20°C: 0.003. Density (at 20°C): 1.27 g/cm³. Octanol/water partition coefficient as log Pow: 5.9. Vapour ...
  5. [5]
    [PDF] US EPA - Cyfluthrin and Beta-Cyfluthrin Interim Registration Review ...
    Sep 30, 2020 · This document is the Environmental Protection Agency's (EPA or the Agency) Interim. Registration Review Decision (ID) for cyfluthrin and ...
  6. [6]
    Toxicological Profile for Pyrethrins and Pyrethroids - NCBI - NIH
    The pyrethroids are synthetic analogs and derivatives of the original pyrethrins and represent a diverse group of over 1,000 powerful insecticides.
  7. [7]
    Cyfluthrin (UK PID) - INCHEM
    Cyfluthrin is effective against many pests. It has a rapid knockdown effect and long-lasting residual activity (Pesticide Manual, 1997).Missing: broad- spectrum stomach
  8. [8]
    Cyfluthrin; Pesticide Tolerance - Federal Register
    Sep 13, 2005 · Cyfluthrin is a member of the pyrethroid class of pesticides. EPA is not currently following a cumulative risk approach based on a common ...Missing: properties | Show results with:properties
  9. [9]
    891. Cyfluthrin (WHO Food Additives Series 39) - INCHEM
    EXPLANATION Cyfluthrin (Figure 1) is a synthetic cyano-containing pyrethroid insecticide. ... type-II pyrethroid poisoning. After oral administration, the ...
  10. [10]
    Cyfluthrin - an overview | ScienceDirect Topics
    It is generally supplied as a 10–25% liquid concentrate for commercial use. View chapterExplore book · Read full chapter. URL: https://www.sciencedirect.com ...
  11. [11]
    [PDF] ATSDR Pyrethrins and Pyrethroids Tox Profile
    Other case studies of interest include Reproductive and Developmental. Hazards; Skin Lesions and Environmental Exposures; Cholinesterase-Inhibiting Pesticide.
  12. [12]
    The history of extensive structural modifications of pyrethroids - PMC
    Nov 20, 2019 · The first synthetic pyrethroid, allethrin, was invented at the United States Department of Agriculture (USDA) in 1949, and its patent was opened ...<|control11|><|separator|>
  13. [13]
    US5028731A - Preparation of mixtures of cypermethrin or cyfluthrin ...
    Preparation of mixtures of cypermethrin or cyfluthrin isomers enriched in more active species.
  14. [14]
    Cyfluthrin - the NIST WebBook
    Cyfluthrin · Formula: C22H18Cl2FNO · Molecular weight: 434.288 · IUPAC Standard InChI: InChI=1S/C22H18Cl2FNO3/c1-22(2)15(11-19(23)24)20(22)21(27)29-18(12-26)13-8-9 ...
  15. [15]
    Cyfluthrin | 68359-37-5 - ChemicalBook
    ChEBI: A carboxylic ester obtained by formal condensation between 3-(2,2-dichloroethenyl)-2,2-dimethylcyclopropanecarboxylic acid and (4-fluoro-3-phenoxyphenyl)( ...
  16. [16]
    [PDF] fao specifications and evaluations
    Melting point and temperature of decomposition. Melting ... Chemical composition and physico-chemical properties of cyfluthrin technical material (TC).
  17. [17]
    Cyfluthrin (Ref: OMS 2012) - AERU - University of Hertfordshire
    Cyfluthrin is a pyrethroid insecticide. It has a low aqueous solubility and is non-volatile. It may be moderately persistent in some soil systems.
  18. [18]
    [PDF] TECHNICAL DATA SHEET - Endura
    Nov 13, 2013 · Solubility in other solvents. Xylene: > 250 g/l at 20 °C. Solubility in other solvents. Acetone: > 250 g/l at 20 °C. Viscosity, kinematic ca ...
  19. [19]
    Cyfluthrin - Endura
    CYFLUTHRIN is an effective photostable synthetic pyrethroid insecticide with killing effect on a broad spectrum of insects such as flies, mosquitoes ...Missing: photostability | Show results with:photostability
  20. [20]
    [PDF] cyfluthrin (157)/beta-cyfluthrin (228)
    Beta-cyfluthrin is an enriched isomeric form of the two biologically active diastereoisomeric pairs of isomers of cyfluthrin. It is considered a new compound ...
  21. [21]
    Stereochemical and chiral aspects in the synthesis of 3‐(2,2 ...
    The synthesis of (1RS)-cis,trans-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylic acid by dehydrohalogenation of 4,6,6,6-tetrahalohexanoates has been ...
  22. [22]
    Stereoselective synthesis of cis-3-(2,2-dichlorovinyl)
    Stereoselective synthesis of cis-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylic acid ... ChemInform Abstract: Stereoselective Synthesis of cis‐3 ...
  23. [23]
    Cyfluthrin hapten compound, its synthesis method and use
    Wash with water, add 30ml of ethyl acetate to dilute, first extract with 5% NaOH (30ml×3), combine, wash the lye with ether (20ml×3), then adjust the pH value ...
  24. [24]
    Synthesis of optically active cis-3-(2,2-dichlorovinyl)
    Jul 1, 1987 · Synthesis of optically active cis-3-(2,2-dichlorovinyl)-2,2-dimethylcyclopropanecarboxylic acid via intramolecular alkylation of a chiral ...
  25. [25]
    [PDF] fao specifications and evaluations
    The material shall consist of technical beta-cyfluthrin, complying with the requirements of FAO specification 482/TC (August 2016), dissolved in suitable ...
  26. [26]
    Baythroid XL Insecticide - Bayer Crop Science
    Baythroid XL insecticide is the complete pyrethroid for many crops and provides fast, effective control of labeled primary and secondary pests.Missing: introduction 1981
  27. [27]
    [PDF] Health Questions and Answers for Tempo Insecticidal Products
    Q: What is Tempo®? A: Tempo® is a line of pesticide products containing the active ingredient beta-cyfluthrin, which is in the pyrethroid family of ...
  28. [28]
    Cyfluthrin Market 2025 Forecast to 2032 - 24ChemicalResearch
    Rating 4.9 (3,567) Nov 1, 2025 · Global Cyfluthrin market was valued at USD 342.7 million in 2024 and is projected to reach USD 412.8 million by 2032, at a CAGR of 2.4% ...Missing: generics | Show results with:generics
  29. [29]
    [PDF] 2025 Insect Control Guide for Agronomic Crops
    Successful, economical control of cotton insect pests requires using a variety of control methods instead of only one, such as scheduled insecticide use. This ...
  30. [30]
    None
    Below is a merged summary of the agricultural uses of cyfluthrin extracted from the NDSU Insect Management Guide E1143-22. To retain all information in a dense and organized format, I’ve used tables in CSV-style text for key details (crops, pests, application rates, and PHI). Additional notes, efficacy details, examples, and URLs are provided in a narrative format following the tables.
  31. [31]
    [PDF] CYFLUTHRIN | National Pesticide Information Center
    What is cyfluthrin. Cyfluthrin is in a group of man-made insecticides called pyrethroids.1 It was first registered in the US in 1987.
  32. [32]
    Evaluation of Cyfluthrin and Etofenprox Resistance in House Fly ...
    Sep 26, 2024 · ... molecular weight: 376.49 g/mol) and cyfluthrin (C22H18Cl2NO3, CAS number: 68359-37-5, molecular weight: 434.29 g/mol), purchased from Sigma ...
  33. [33]
    [PDF] WHO Guidelines for malaria - 16 February 2021
    Feb 16, 2021 · cyhalothrin, etofenprox, bifenthrin, cyfluthrin ... Larval source management: a supplementary measure for malaria vector control.
  34. [34]
    Beta-cyfluthrin, a synthetic pyrethroid for mosquito control - PubMed
    Residual efficacy at 50 mg(ai)/m2 was more persistent (for 14-25 weeks) on thatch and asbestos among the four treated surfaces. This compound also elicited ...
  35. [35]
    Voltage-gated sodium channels as targets for pyrethroid insecticides
    Jan 9, 2017 · The mode of action of pyrethroids is known to be via interactions with the voltage-gated sodium channel.
  36. [36]
    Biomarkers of Type II Synthetic Pyrethroid Pesticides in Freshwater ...
    Mar 31, 2014 · Type II synthetic pyrethroids contain an alpha-cyano group which renders them more neurotoxic than their noncyano type I counterparts.
  37. [37]
    Characterization of pyrethroid hydrolysis by the human liver ...
    Differences in the activities of carboxylesterases and P450s between mammals and insects contribute to the low mammalian toxicity of pyrethroids (i.e., ...
  38. [38]
    Pyrethroids: mammalian metabolism and toxicity - PubMed
    Apr 13, 2011 · They showed that ester hydrolysis and oxidation play predominant roles in mammalian metabolism of pyrethroids and that rapid metabolism leads to low mammalian ...
  39. [39]
    Sodium Channel Mutations and Pyrethroid Resistance in Aedes ...
    Oct 31, 2016 · Mutations in the sodium channel have been shown to be responsible for pyrethroid resistance, known as knockdown resistance (kdr), in various insects including ...
  40. [40]
    Neurotoxicity of Pesticides - PMC - PubMed Central
    Neurological effects, including cognitive impairment, have been observed following pyrethroid exposure of pesticide applicators and their families [96, 136].
  41. [41]
    [PDF] Cyfluthrin C hemicalWatch Factsheet - Beyond Pesticides
    CAS Registry Number: 68359-37-5. Chemical Class: Synthetic pyrethroid. Use: Broad spectrum insecticide for a variety of agri- cultural crops.
  42. [42]
    Cyfluthrin; Pesticide Tolerance - Federal Register
    Sep 27, 2002 · iii. Cancer. Cyfluthrin has been classified as “not likely to be carcinogenic in humans” based on the results of a carcinogenicity study in ...Missing: inflammation | Show results with:inflammation
  43. [43]
    [PDF] (Pesticide residues in food \227 2006: Toxicological evaluations)
    For cyfluthrin, the specifications were established by the FAO/WHO Joint Meeting on Pesticide ... containing technical-grade cyfluthrin (purity, 95.5%–96.2%) at a ...
  44. [44]
    [PDF] UNITED STATES ENVIRONMENTAL PROTECTION AGENCY ...
    Jun 14, 2025 · agricultural uses of cyfluthrin and beta-cyfluthrin, assuming baseline clothing and no PPE. The inhalation risk estimates for scenarios that ...
  45. [45]
    US EPA-Pesticides; Cyfluthrin
    It is noted, however, that Koc values for cyfluthrin vary considerably (73,500 mL/g – 180,300 mL/g.-OC) which likely reflect differences in organic carbon ...
  46. [46]
    [PDF] Literature Review for Candidate Chemical Control Agents for ...
    Hyatt (2004) reported even more rapid degradation with significant chemical losses within an hour after application. Photodegradation and sedi- ment binding ...
  47. [47]
    Role of Sediments in Insecticide Runoff from Urban Surfaces
    Jul 11, 2018 · Insecticides, such as pyrethroids, have frequently been detected in runoff from urban areas, and their offsite transport can cause aquatic ...
  48. [48]
    [PDF] FAO SPECIFICATIONS AND EVALUATIONS FOR PLANT ...
    The material shall consist of technical beta-cyfluthrin, complying with the requirements of FAO specification 482/TC (1999), dissolved in suitable solvents, ...
  49. [49]
    Pesticide Fact Sheet: Cyfluthrin - epa nepis
    ... Registration Date Issued: December 30, 1987 Fact Sheet Number: 164 ... Sufficient data are available to characterize cyfluthrin from an environmental fate and ...
  50. [50]
    The potential acute and chronic toxicity of cyfluthrin on the soil ...
    Aug 6, 2025 · ... earthworm progeny. Li et al. (2017) also showed that applying cyfluthrin at more than 20 mg/kg considerably reduced the number of cocoons ...
  51. [51]
    [PDF] attachment_3.pdf - Regulations.gov
    Jul 31, 2012 · most of the fipronil sulfone and cyfluthrin detections were above their lowest US EPA aquatic benchmark. ... pesticide runoff studies with changes ...
  52. [52]
    Storm-event-transport of urban-use pesticides to streams likely ...
    Multiple U.S. EPA benchmark or criterion exceedances occurred in 40 % of urban streams sampled. Bed sediment concentrations of bifenthrin were highly correlated ...
  53. [53]
    40 CFR 180.436 -- Cyfluthrin and the isomer beta-cyfluthrin - eCFR
    40 CFR 180.436 establishes tolerances for cyfluthrin and beta-cyfluthrin residues in raw agricultural commodities, such as alfalfa (5.0 ppm) and barley grain ( ...Missing: crops | Show results with:crops
  54. [54]
    [PDF] Updated Spray Drift Language for Pyrethroid Agricultural Use Products
    Do not apply within 450 feet of aquatic habitats (such as, but not limited to, lakes, reservoirs, rivers, streams, marshes, ponds, estuaries, and commercial ...<|separator|>
  55. [55]
    Review of the existing maximum residue levels for Beta‐cyfluthrin ...
    Sep 23, 2021 · EFSA has reviewed the maximum residue levels (MRLs) currently established at European level for the pesticide active substances Beta‐cyfluthrin and Cyfluthrin.
  56. [56]
    Review of the existing maximum residue levels for Beta‐cyfluthrin ...
    Sep 23, 2021 · EFSA has reviewed the maximum residue levels (MRLs) currently established at European level for the pesticide active substances Beta‐cyfluthrin and Cyfluthrin.
  57. [57]
    Maximum residue levels for cyfluthrin - AGRINFO Platform
    Feb 6, 2023 · The EU has lowered MRLs for cyfluthrin to the lowest limit of analytical detection (LOD: 0.01 – 0.05 mg/kg), on certain fruits.
  58. [58]
    [PDF] commission implementing regulation (eu) 2020/968
    Jul 3, 2020 · e.g. no-spray buffer zones and/or spray drift reduction, to achieve a low risk for sediment-dwelling organisms and aquatic organisms. As ...
  59. [59]
    [PDF] Re-evaluation Decision RVD2018-35 - à www.publications.gc.ca
    Oct 31, 2018 · 1.1 Toxicology Assessment for Cyfluthrin. The initial toxicological assessment for cyfluthrin was presented in the Proposed Re-evaluation.Missing: efficacy boll weevils
  60. [60]
    Changes to the cyfluthrin pesticides registration (non-agricultural uses)
    Jan 19, 2024 · Domestic products are for indoor use against household pests such as ants, earwigs, cockroaches and spiders.Missing: fleas | Show results with:fleas
  61. [61]
    Mandatory Intervals Between Application, Reentry, Harvest ... - UC IPM
    Mandatory Intervals Between Application, Reentry, Harvest, and Hazards to Bees ; cyfluthrin, Tombstone, 12, 0, 3A ; diflubenzuron, Micromite 80WGS and 2L, 12, 7 ...Missing: PPE | Show results with:PPE
  62. [62]
    [PDF] Food Notice: Maximum Residue Levels for Agricultural Compounds
    Jul 31, 2025 · The purpose of the Food Act 2014 (the Act) includes achieving the safety and suitability of food for sale, maintaining and improving confidence ...
  63. [63]
    [PDF] Cyflu hrin & Beta-cyfluthrin - EPA
    This document provides a review of the appropriate studies for cyfluthrin and beta-cyfluthrin to determine their Global Harmonised System (GHS)/EPA hazard ...Missing: fact | Show results with:fact
  64. [64]
    Impact of cyfluthrin (Solfac EW050) impregnated bed nets on ...
    Jan 11, 2013 · Conclusion. The study confirms the effectiveness of cyfluthrin impregnated nets in reducing malaria transmission. Lessons from this study could ...
  65. [65]
    Insecticide resistance status of malaria vectors in ... - PubMed Central
    Nov 26, 2022 · An. fluviatilis was susceptible to malathion, cyfluthrin, and deltamethrin in the two tribal districts (mortality – 98–100%) but possible ...
  66. [66]
    Review of the existing maximum residue levels for Beta‐cyfluthrin ...
    Sep 23, 2021 · EFSA has reviewed the maximum residue levels (MRLs) currently established at European level for the pesticide active substances Beta-cyfluthrin and Cyfluthrin.
  67. [67]
    Pesticide Detail | CODEXALIMENTARIUS FAO-WHO
    Commodity name. 157 - Cyfluthrin/beta-cyfluthrin. Functional class ... Spices, fruits and berries, 0.03 mg/Kg, 2011. Spices, roots and rhizomes, 0.05 mg/Kg ...