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Pyrethrum

Pyrethrum is the powdered or extracted form of the dried flower heads from Tanacetum cinerariifolium (synonym Chrysanthemum cinerariifolium), a perennial herbaceous plant in the Asteraceae family native to the Balkan Peninsula and Caucasus region, valued primarily for its natural insecticidal properties derived from pyrethrins. These pyrethrins consist of six closely related esters—pyrethrin I and II, cinerin I and II, and jasmolin I and II—that occur in the glandular trichomes of the plant's inflorescences and function as neurotoxins, rapidly paralyzing and killing insects by prolonging sodium channel opening in their nerve cells while exhibiting low toxicity to mammals due to differences in body temperature and detoxification enzymes. Historically, pyrethrum's insect-repellent qualities were recognized in the as early as the 17th century, with trade reaching by the ; commercial extraction began in the in regions like (modern-day ), and production surged during to meet demand for delousing agents, leading to widespread cultivation in starting in the 1920s. As of 2024, global pyrethrum production of dried flowers is dominated by East African countries, with , , and together supplying over 80% of the world's pyrethrins (derived at 1–2% content from the flowers)—approximately 8,000 metric tons from , 3,500 from , and 1,000 from —as well as output from (particularly ) and , where the crop is grown at high altitudes (1,800–3,000 meters) for optimal pyrethrin content. As a key component in pest management, pyrethrum is formulated into over 2,000 registered products worldwide, including agricultural sprays for crops like fruits and , household aerosols against flies and ants, pet shampoos for fleas, and tools such as insecticide-treated bed nets for control, prized for its broad-spectrum efficacy, quick degradation in sunlight ( of about 12 hours), and minimal environmental persistence compared to synthetic alternatives. Despite its safety profile—classified by the EPA as low acute toxicity to humans, with primary effects limited to skin irritation or respiratory symptoms from high exposure—pyrethrum remains highly toxic to beneficial insects like bees and aquatic organisms like fish, necessitating careful application to avoid non-target impacts.

Botanical Overview

Description and Morphology

Pyrethrum (Tanacetum cinerariifolium) is a herbaceous perennial plant in the Asteraceae family, characterized by its tufted growth habit and slender, erect stems that reach heights of 50–80 cm. The leaves are alternate, pinnately divided into fern-like segments, gray-green in color, and densely covered with white tomentum on both surfaces. This woolly covering gives the foliage a distinctive silvery appearance. The plant produces daisy-like flower heads (capitula) measuring 2–3 cm in diameter, borne singly on rigid stems. Each capitulum features 18–22 white ray florets surrounding 40–100 yellow disc florets, arranged on a convex receptacle within an involucre of 12–18 mm diameter. Flowering typically occurs in summer, with the plant exhibiting a short-lived , though it can be managed as an annual in . Native to the Balkan Peninsula, particularly the Dalmatia region along the eastern Adriatic coast, from to elevations up to about 1,300 m, it forms shallow fibrous . Pyrethrum prefers temperate climates and well-drained, fertile soils rich in , calcium, and magnesium, with a neutral to slightly alkaline of 6.0–7.5. It thrives at elevations of 1500–2500 m in commercial settings, where cooler temperatures enhance growth. Key cultivars, such as those selected in , are prized for their elevated content (up to 2.0%) while maintaining the standard flower morphology of ray and disc florets.

Taxonomy and Species

Pyrethrum is scientifically classified under the Tanacetum cinerariifolium (Trevir.) Sch. Bip., with notable synonyms including Chrysanthemum cinerariifolium (Trevir.) Vis. and Pyrethrum cinerariifolium Trevir.. The species belongs to the genus Tanacetum within the family, a diverse group of flowering in the order , where pyrethrins—its key secondary metabolites—have evolved primarily as a mechanism against herbivorous and pathogens. Within the Tanacetum genus, which encompasses around 160 species of mostly perennial herbs, T. cinerariifolium stands out for its high-yield production of pyrethrins, rendering it the only commercially viable species for insecticide extraction. Related species include Tanacetum coccineum, known as the painted daisy and primarily cultivated as an ornamental for its vibrant flowers, which produces only trace amounts of pyrethrins insufficient for commercial use; and Tanacetum parthenium, or feverfew, valued for its medicinal properties due to sesquiterpene lactones like parthenolide but lacking significant pyrethrin content. These distinctions highlight T. cinerariifolium's specialized biochemical adaptations within the genus. The common name "pyrethrum" derives from the Greek word pyretos, meaning "fever," reflecting the plant's historical application in to treat febrile conditions, though its insecticidal properties later became the focus of its .

Historical Development

Traditional Uses

Pyrethrum has been valued for its insecticidal properties since ancient times. The earliest recorded use dates to around in Persia, where dried flower powder was used to delouse children during the reign of King . Indigenous communities in the , particularly in Croatia's Dalmatian region, have long employed ground dried pyrethrum flowers as a household to protect stored grains from and as a natural repellent in agricultural settings. Following its introduction in the 1920s, small-scale farmers in and have applied pyrethrum dust or infusions for fumigation to safeguard stored grains and repel pests in subsistence farming.

Modern Commercialization

Commercial extraction of pyrethrum began in the 1820s in (modern-day ), where dried flowers of (synonym Chrysanthemum cinerariifolium) were processed into insecticidal powders. These powders were exported to France, where they were commercialized for use in early formulations targeting household pests. In the 20th century, British colonial authorities introduced pyrethrum cultivation to in the late , initially by European settlers in high-altitude regions suitable for the crop, marking the start of organized production in Africa. By the 1930s, expansion efforts supported by colonial agricultural services transformed it into a key , with emerging as the world's largest producer by the 1950s, accounting for over 70% of global supply through exports of dried flowers. The surge in demand during , driven by military needs for effective, low-toxicity insecticides amid shortages from Japanese sources, further boosted Kenyan output as a preferred alternative to emerging synthetics like . Post-war, pyrethrum's dominance waned in the and due to the development of cheaper, more stable synthetic pyrethroids, such as allethrin in , which offered greater persistence and scalability for agricultural use. Global production shifted toward these analogs, leading to a sharp decline in natural pyrethrum demand and reduced cultivation in traditional areas. A revival began in the , fueled by growing interest in and restrictions on synthetic pesticides, repositioning pyrethrum as an eco-friendly option and restoring its role in . Today, pyrethrum production centers on , , and , where smallholder farmers predominate and the crop supports rural livelihoods through stable income from biweekly harvests. In , ongoing revival initiatives since 2017 have distributed millions of seedlings to over 15,000 households, benefiting more than 100,000 farmers economically by funding , local businesses, and . Typical yields range from 500-800 kg/ha of dry flowers, contributing to global supply amid rising demand for sustainable alternatives.

Chemical Properties

Active Compounds: Pyrethrins

Pyrethrins are the principal insecticidal constituents extracted from the dried flowers of , comprising a of six structurally similar esters that account for the plant's natural pesticidal properties. These compounds are biosynthesized in the glandular trichomes of the flower heads and serve as a defense mechanism against herbivorous . The six pyrethrins are classified into two groups based on their acid components: I, cinerin I, and jasmolin I, which are esters of chrysanthemic acid (a cyclopropanecarboxylic acid); and II, cinerin II, and jasmolin II, which are esters of pyrethric acid (a related acid with an additional carboxyl group). Each is formed by esterification with one of three moieties (pyrethrolone, cinerolone, or jasmololone), resulting in the following molecular formulas: I (C21H28O3), cinerin I (C20H28O3), jasmolin I (C21H30O3), II (C22H28O5), cinerin II (C21H28O5), and jasmolin II (C22H30O5). The insecticidal potency of pyrethrins is critically dependent on their , particularly the (1R,3R)- configuration of the ring in the acid moiety and specific configurations in the portion, with only certain stereoisomers exhibiting significant bioactivity. Pyrethrins typically represent 1–2% of the dry weight of pyrethrum flowers, with concentrations varying by and environmental factors; the highest levels are concentrated in the achenes (seed-like structures) of the flower heads. Pyrethrins act primarily by binding to a distinct site on voltage-gated sodium channels in insect nerve membranes, slowing channel activation and inactivation while prolonging the open state, which causes repetitive spontaneous firing of action potentials. This disruption leads to hyperexcitation, uncoordinated tremors, paralysis, and rapid knockdown of target insects, often within minutes of exposure. Their short residual activity stems from instability in environmental conditions, as pyrethrins degrade quickly via photolysis and oxidation when exposed to sunlight and air.

Extraction and Formulation

The extraction of pyrethrins from pyrethrum flowers primarily involves solvent-based methods to isolate these active esters from the dried flower heads of Tanacetum cinerariifolium. Traditional solvent extraction uses non-polar solvents such as , which is applied to ground flowers in a or immersion , yielding a crude containing 20-50% total pyrethrins by weight. This represents a concentrated form of the natural insecticidal compounds, with the recovered through evaporation to minimize losses. Alternatively, supercritical carbon dioxide (CO₂) extraction has gained prominence as an environmentally friendly method, operating at pressures of 100-300 bar and temperatures around 40-60°C to selectively extract pyrethrins while avoiding residual solvents; yields from this typically achieve 1-2% extraction efficiency from dry flower material, producing an of comparable pyrethrin content to solvent methods. Following initial extraction, purification steps remove impurities like waxes, pigments, and plant debris to enhance the purity and stability of the pyrethrin concentrate. Filtration through celite or similar media separates solid residues, followed by distillation—often under vacuum to prevent thermal degradation—to eliminate residual solvents and volatile impurities, achieving a refined extract with 45-60% pyrethrin concentration. Recovery efficiencies in these purification processes generally range from 70-100%, depending on the scale and conditions, with supercritical methods often attaining higher selectivity and near-complete pyrethrin recovery. Commercial formulations of pyrethrum extracts are developed to suit various application needs, incorporating the purified pyrethrins into stable delivery systems. Common types include emulsifiable concentrates (ECs), which mix pyrethrins with and solvents for dilution in water; dusts, blending the extract with inert carriers like for direct application; and aerosols, where pyrethrins are suspended in propellants for fogging. To counter the rapid degradation of pyrethrins by oxidation and UV light, synergists such as are added at ratios of 2-10:1, inhibiting detoxifying enzymes and extending efficacy without altering the natural profile. Quality control in pyrethrum processing ensures consistent potency through standardization of the final extract to 25-50% total pyrethrins, verified by (HPLC) analysis of the six key components (pyrethrin I and II, cinerin I and II, jasmolin I and II). This standardization aligns with regulatory requirements, such as those specifying 45-55% w/w pyrethrins for technical-grade products, facilitating reliable performance in end-use insecticides.

Agricultural Production

Cultivation Practices

Pyrethrum cultivation requires careful site selection to optimize growth and content. In high-altitude n regions like and , which dominate global production, cool conditions between 1,500 and 2,500 meters above are favored, with temperatures ranging from 15°C to 20°C and a period below 18°C for at least six weeks to initiate flowering. In contrast, in (), cultivation occurs at lower altitudes (typically 100–500 m) in cool temperate climates, relying on supplementary to mimic conditions. Ecuadorian production emphasizes altitudes up to 3,000 m for optimal levels. Annual rainfall of 800 to 1,200 mm, well-distributed throughout the year, is essential in , though a minimum of 750 mm suffices in areas with lower ; semi-arid conditions with cool winters enhance productivity. Soils should be well-drained sandy loams or loamy volcanic types rich in , with a of 5.5 to 7.0 to prevent deficiencies or ; waterlogging must be avoided to reduce disease risk. The herbaceous of pyrethrum, with its shallow , aligns well with these fertile yet non-excessively rich soils. Planting typically involves seed propagation, where seedlings are raised for 5 to 8 months and transplanted before the rainy to establish in East African systems, though vegetative cuttings from healthy clones can be used for uniformity in commercial fields. In , direct seeding in late winter is common, with a longer establishment phase. Optimal spacing is 30 to 60 cm between plants within rows spaced 60 to 70 cm apart, allowing approximately 21,000 plants per to balance airflow and light exposure. Crop rotation with , such as beans or , every 3 to 4 years is recommended to restore and mitigate depletion from the nutrient-demanding perennial growth cycle. Fertilization focuses on phosphorus and nitrogen to support root development and foliage, with applications of 50 to 100 kg per hectare of (e.g., triple superphosphate at 50-60 kg per ) and complementary nitrogen sources, alongside 4 tonnes per of incorporated three months prior to planting. In acidic soils (pH below 5.6), or is added to adjust , while balanced NPK fertilizers ensure steady nutrient supply without excess that could dilute pyrethrins. Irrigation, particularly systems, is employed in drier regions like parts of or to supplement rainfall during establishment and dry spells, maintaining consistent moisture without overhead wetting that promotes foliar diseases. Pest and disease control relies on integrated management practices to maintain , avoiding synthetic chemicals that could contaminate pyrethrins. Common pests include , (such as flower and leaf thrips), , and root-knot nematodes, managed through biological agents like predatory , resistant varieties, and cultural methods such as annual cut-back and burning of stalks to disrupt life cycles. Diseases like , caused by fungal pathogens in poorly drained soils, are prevented by site preparation, , and avoiding overhead ; biopesticides derived from neem or other botanicals supplement and rogueing of infected plants.

Harvesting and Yield

In East African cultivation, harvesting of pyrethrum flowers begins approximately four months after , with subsequent picks occurring every two weeks during the flowering season, which typically spans 3 to 5 cycles over 4 to 6 months depending on the and environmental conditions. In , the first harvest occurs 14–18 months after seeding. Flowers are selectively picked by hand when about 50% are open, with ray florets horizontal and 3 to 4 outer disc florets visible, to maximize content while minimizing contamination from leaves or immature buds. The preferred hand-picking technique involves holding the flower head between the first and second fingers and jerking it free with the thumb, ensuring only clean capitula are collected and avoiding rainy conditions that could lead to . Following harvest, flowers must be dried promptly to preserve pyrethrins, the active insecticidal compounds, which are sensitive to , , and . Traditional sun drying reduces content to around 10%, but controlled methods such as drying at 50°C for 21 hours or using solar dryers yield higher pyrethrin retention, achieving up to 1.44% extractable content compared to 1.02% in direct . Dried flowers are then stored in cool, dark, well-ventilated containers like baskets to prevent from oxidation or microbial activity, maintaining potency for . Yields of dry pyrethrum flowers typically range from 250 to 1,200 kg per , with lower outputs (around 250 kg/ha) in the first year increasing to 1,000–1,200 kg/ha in subsequent years under optimal conditions. Pyrethrin yields vary from 8 to 20 kg per , influenced by , altitude, and soil; for instance, production in the Kenyan highlands often reaches 700–1,000 kg/ha of dry flowers due to cooler temperatures that enhance pyrethrin concentration (1.8–2.2%), while Tasmanian yields can average around 1,700 kg/ha. Improper post-harvest handling, such as exposure to during or temperatures exceeding 50°C, can cause significant degradation, with losses of 20–30% reported from to inactive forms or at moisture levels above 10%. These factors underscore the importance of timely and protected storage to minimize economic losses for producers.

Insecticidal Applications

As Natural Insecticide

Pyrethrum extracts, rich in pyrethrins, serve as a broad-spectrum natural effective against a wide range of pests, including flying insects such as mosquitoes and flies, crawling insects like and , and agricultural pests including and . This efficacy stems from the compounds' ability to disrupt insect nervous systems, leading to rapid and death, while their biodegradable nature minimizes long-term environmental residue. Pyrethrum is particularly valued in for its low toxicity to mammals and quick degradation in sunlight and air, making it suitable for both household and field applications. Common application forms include liquid sprays at concentrations of 1-2%, formulations at 0.5-1%, and fogging systems for broader coverage. Sprays are typically diluted in or for direct application on plants or surfaces, targeting pests like on crops or in homes. provide residual control in or areas, while fogging—often using ultra-low volume techniques—is employed in efforts, such as to combat transmission. Pyrethrum's efficacy is characterized by rapid knockdown, often within 5-15 minutes of , due to immediate neurotoxic effects on . However, its short persistence—typically 1-2 days in the —necessitates reapplication for sustained , with half-lives of about 12 hours on surfaces exposed to , but 2-10 days in under aerobic conditions. This transience aligns well with practices, where pyrethrum is applied to over 100 crops to manage pests without violating standards. Regulatory bodies have approved pyrethrum for use, with the U.S. EPA registering pyrethrins since the and listing them as compliant for organic production on more than 200 fruits and . In the , pyrethrins are authorized under Regulation (EC) No 1107/2009 for plant protection and , subject to national conditions. Examples include household aerosol products for indoor and crop protectants like Pyrethrum Concentrate for agricultural use.

Companion Planting and Organic Gardening

Pyrethrum (Tanacetum cinerariifolium), a perennial daisy known for its insect-repelling qualities, plays a key role in companion planting strategies within organic gardening. While pyrethrins provide insecticidal properties, the plant is traditionally used in companion planting for potential repellency, possibly due to volatile compounds, though scientific evidence for strong protective effects is limited. It is intercropped with crops such as roses, tomatoes, and cabbage to deter pests like aphids and whiteflies. Recent genetic studies (2024) have uncovered mechanisms enhancing pyrethrum's potential as a companion plant in eco-friendly pest management. In and biodynamic systems, pyrethrum contributes to holistic pest management by fostering in mixed plantings, where it integrates seamlessly with other species to suppress populations naturally. Practical examples include using it in mixed borders alongside , which can significantly decrease the overall need for external pesticides while enhancing resilience. Its compatibility with standards stems from the eco-friendly degradation of pyrethrins, making it a preferred for certified organic operations. For home gardeners, pyrethrum excels as a border around patches or as a to fruit trees, where it provides ongoing protection against aerial pests like and . is simple and accessible: sow seeds on the surface in under for , or divide established clumps every 2-3 years in early or fall to propagate new and prevent overcrowding. Well-drained and full sun ensure vigorous growth, allowing gardeners to establish colonies that offer season-long benefits. Despite its advantages, pyrethrum's efficacy in has limitations; it primarily targets above-ground, soft-bodied insects and offers minimal control over soil-dwelling pests due to the localized action of its compounds. Achieving optimal repulsion often necessitates dense plantings to create an effective perimeter, as sparse arrangements may allow pests to bypass the barrier.

Toxicity and Environmental Impact

Mammalian Toxicity

Pyrethrins, the active compounds in pyrethrum, exhibit low to mammals, with oral LD50 values in rats ranging from 1,030 mg/kg in females to 2,370 mg/kg in males, classifying them as slightly under EPA Toxicity Category III for acute oral exposure. This low toxicity profile stems from their rapid detoxification in mammalian systems, in contrast to the prolonged action on sodium channels. Exposure to pyrethrum concentrates can cause mild skin , including (tingling or numbness) and , particularly in occupational settings or with direct handling. may result in mild and excessive lacrimation, while of aerosols or dusts can lead to , such as nasal or discomfort and, in rare cases, labored breathing. Allergic reactions, known as pyrethrum , are uncommon but can manifest as skin rashes, urticaria, or responses like respiratory distress in sensitized individuals. In mammals, pyrethrins undergo rapid primarily through of the bond by carboxylesterases in the liver, followed by oxidation via enzymes, resulting in nontoxic metabolites excreted mainly in . The elimination is short, typically ranging from 6 to 12 hours in blood and tissues, preventing significant even with repeated low-level exposures. Safety guidelines recommend using (PPE), such as gloves, long sleeves, , and respirators, during handling or application of pyrethrum formulations to minimize dermal, ocular, and risks. At recommended low doses, pyrethrins are generally safe for mammalian pets , but they pose a higher risk to due to their inefficient pathway, which impairs and can lead to severe neurological symptoms like tremors and seizures even from spot-on products intended for other animals.

Effects on Non-Target Organisms

Pyrethrins, the active compounds in pyrethrum, exhibit high toxicity to beneficial insects, including pollinators and predators essential for ecosystem balance. Honey bees (Apis mellifera) are particularly vulnerable, with an acute contact LD50 of 0.022 μg per bee, classifying pyrethrins as highly toxic and capable of causing rapid paralysis and death upon exposure. Predatory insects such as wasps also face significant risks, as pyrethrins disrupt sodium channels in their nervous systems, leading to mortality rates exceeding 80% in direct contact scenarios similar to those observed in field applications. To mitigate these impacts, applications are recommended in the late evening or early morning when foraging activity is minimal, allowing partial degradation before peak insect activity resumes. Among wildlife, experience moderate risk due to low oral , with acute LD50 values exceeding 2000 mg/kg body weight in species like the bobwhite quail, indicating practical non-toxicity under typical exposure levels. In contrast, fish and amphibians face higher threats, as pyrethrins are extremely toxic to aquatic vertebrates; for instance, the 96-hour LC50 for is 5.1 μg/L, and for sheepshead minnows it is 16 μg/L, with amphibians showing comparable sensitivity due to shared ectothermic physiology. In aquatic environments, pyrethrins pose risks to non-target despite their relatively short persistence. They strongly bind to sediments, with an adsorption coefficient (Kd) of approximately 302 L/kg, reducing bioavailability in water columns but concentrating exposure for benthic organisms. Species like the water () are highly susceptible, exhibiting an of 11.6 μg/L for , which disrupts populations of grazers and prey in freshwater systems. accelerates breakdown under sunlight, with a of 11.8 hours in water, or up to 14-17 days in darkness, prolonging potential harm during low-light periods. Field trials underscore these effects, revealing approximately 10-fold higher mortality in non-target arthropods following applications compared to control areas, particularly among small-bodied species in sprayed areas, though larger arthropods often recover due to the compounds' rapid dissipation. These impacts highlight the need for targeted use to preserve , contrasting with lower risks to mammals where safety margins are broader.

Ecological Considerations

Pyrethrins, the active compounds in pyrethrum, exhibit rapid environmental degradation primarily through photolysis upon exposure to and in aqueous environments, with additional breakdown via microbial activity in . These processes result in low , with half-lives (DT50) in typically ranging from 2.2 to 9.5 days under aerobic conditions, contrasting with the longer of many synthetic alternatives. In terms of sustainability, pyrethrum production aligns with principles by minimizing chemical inputs and reducing runoff into waterways, thereby supporting in regions like where it is predominantly grown. However, reliance on practices in these highland areas can lead to biodiversity erosion, as intensive cultivation diminishes diversity and increases vulnerability to pests and diseases, prompting recommendations for and to mitigate these effects. Pyrethrum cultivation demands well-distributed annual rainfall of 800 to 1,200 , often supplemented by in drier seasons, which can elevate local water consumption to significant levels depending on and conditions in zones. Additionally, the of pyrethrum is influenced by the transportation of dried flowers from remote farms in to facilities, contributing an estimated 7.74 kg CO₂e per kg of product at gate, though overall emissions remain lower than those of persistent synthetic pesticides due to its biodegradable nature. Conservation efforts surrounding pyrethrum emphasize its integration into agroecological systems through (IPM), where it serves as a targeted, low-residue option that preserves beneficial and ecosystems. By prioritizing biological and cultural controls alongside selective pyrethrum applications, IPM frameworks enhance in treated fields and position pyrethrum as a viable green alternative in , reducing reliance on broad-spectrum chemicals that harm non-target species.

Synthetic Pyrethroids

Synthetic pyrethroids are man-made insecticides chemically derived from the natural pyrethrins found in pyrethrum flowers, with modifications to enhance stability and efficacy. The development of these compounds began in the late when the first synthetic analog, allethrin, was created at the (USDA) in 1949 through structural modifications of pyrethrin esters to improve insecticidal activity while addressing the natural compounds' rapid degradation. Subsequent advancements in the 1960s and 1970s at in the UK led to more stable variants, including resmethrin in 1967 and permethrin, which was synthesized and patented in 1973, marking a breakthrough in photostable pyrethroids suitable for outdoor use. Synthetic pyrethroids are classified into two main types based on their and toxicological effects. Type I pyrethroids, lacking an α-cyano group, include compounds like allethrin, , and resmethrin; these exhibit rapid knockdown of by disrupting sodium channels in cells, leading to quick and death. Type II pyrethroids, which contain the α-cyano group, such as and , are generally more potent and provide longer residual activity due to slower metabolism in target pests, often causing convulsions in addition to knockdown. Structural alterations, particularly in the and moieties of the pyrethrin backbone, were key to achieving this stability against light, heat, and oxidation. Compared to natural pyrethrins, synthetic pyrethroids offer significant advantages, including enhanced photostability that prevents rapid breakdown under sunlight, allowing efficacy to last weeks rather than hours or days. They are also more cost-effective to produce at scale and require lower application rates for equivalent control, making them economical for large-scale use. These properties have enabled widespread adoption in agriculture for crop protection against pests like aphids and bollworms, as well as in veterinary applications such as flea and tick collars for pets. By the , synthetic pyrethroids dominated the market, accounting for over 90% of pyrethroid-based products due to their superior performance and reduced reliance on natural pyrethrum extraction, which has consequently seen declining demand.

Current Research and Alternatives

Recent research on pyrethrum focuses on genetic enhancements to boost pyrethrin yields, addressing limitations in natural extraction efficiency. A 2024 study elucidated the biosynthetic pathways of in Tanacetum cinerariifolium, identifying key genes such as those involved in and (E)-β-farnesene production, which could enable targeted breeding for higher pyrethrin content. In , 2020s breeding trials in have explored and analysis to develop cultivars with elevated pyrethrin levels, leveraging global diversity through selection for high-yielding traits. Overexpression of genes like TcCHS in transgenic approaches has demonstrated increases in pyrethrin accumulation, supporting genotype-independent transformation systems for commercial improvement. Insect resistance to pyrethrins is an emerging challenge, particularly in mosquito vectors, prompting studies on integrated management strategies. Research from the 2020s indicates widespread resistance in Anopheles gambiae to pyrethrins and related pyrethroids, driven by metabolic detoxification and target-site mutations, which reduces efficacy in malaria control. To counter this, investigations have explored insecticide rotation, including alternation with neonicotinoids like imidacloprid, which target distinct biochemical pathways and show promise in restoring susceptibility in resistant populations. Experimental evolution studies confirm that neonicotinoids can manage pyrethroid resistance without cross-selection, offering a viable rotation option for vector control programs. Alternatives to pyrethrum emphasize sustainable, low-toxicity options, including plant-derived essential oils and biological agents. (Azadirachta indica) extracts, rich in , provide effective insecticidal activity against pests like beetles and mosquitoes, serving as a in with minimal environmental persistence. (Cymbopogon nardus) acts as a repellent and contact toxicant, particularly in nanoemulsion formulations that enhance stability and efficacy against vectors without synthetic additives. Biological controls such as Bacillus thuringiensis (Bt) toxins target specific lepidopteran pests via gut disruption, offering a selective alternative in systems. advancements include nanoencapsulated pyrethrins and essential oils, improving delivery, bioavailability, and resistance to degradation for prolonged . Future trends in pyrethrum research prioritize climate-resilient cultivars and regulatory shifts toward insecticides. Studies on local genetic adaptation reveal that environmental factors influence pyrethrin , guiding for cultivars tolerant to and stresses prevalent in production regions like and . Regulatory pressures, including EU reforms post-2020 bans on hazardous synthetics like , are accelerating approvals for s, with proposed amendments to Regulation 1107/2009 in 2025 aiming to fast-track alternatives like pyrethrum to reduce synthetic reliance. These efforts underscore a shift toward sustainable, eco-friendly pest management amid global calls for integration.

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