🏷️ Brand Names — Same Active Ingredient
🎯 What It Kills
⚙️ How It Works
Pyrethrin is extracted from Chrysanthemum flowers. Extremely fast knockdown but breaks down within hours in sunlight — no residual. OMRI-listed for certified organic production.
⚗️ Mixing & Application
⚠️ Safety
- ⚠ Still toxic to bees when wet — apply evening only
- ⚠ Toxic to fish
- ⚠ Very short residual — frequent reapplication needed
- ⚠ PBO synergist in some formulations not accepted by all organic certifiers
🐛 Pests This Treats — Learn More
Click any pest to view its full identification guide, biology, and treatment options.
🌿 Environmental & Ecological Impact
⏱️ Residual & Re-entry Timeline
🔄 Alternatives & Related Products
Same chemical class or different approaches to the same pests.
🔄Same class: Botanical
Different approach: Inorganic
Different approach: IGR
❓ Frequently Asked Questions
📋 Safety Data Sheet (SDS)
PyGanic EC 1.4 — Safety Data Sheet
View the official SDS document for this product directly on the CDMS label database.
Known limitations of Pyrethrin — PyGanic, Evergreen
No active ingredient is universal, and Pyrethrin — PyGanic, Evergreen has specific weak points worth understanding before purchase. Resistance is the most common limitation — populations in heavily-treated areas (commercial kitchens, multi-unit housing, urban cores) often show measurable tolerance compared to populations in less-treated environments. Rotating between chemical classes every two or three applications reduces resistance pressure significantly.
Substrate binding is another limitation. Pyrethrin — PyGanic, Evergreen on highly absorbent surfaces like unfinished wood or carpet can become bound to the substrate within hours of application and never reach the pest in active form. For these surfaces, dust formulations or baits perform better than liquid sprays. Crack-and-crevice application using a precision tip places product where it reaches the pest while minimizing exposed-surface residue.
Pollinator and beneficial-insect impact is the third limitation to plan around. Outdoor application timing should avoid blooming plants, and any application near beneficial habitat (gardens, water features, pollinator strips) should be made in late evening when beneficials are inactive.
How Pyrethrin — PyGanic, Evergreen performs in real-world conditions
Laboratory efficacy numbers for Pyrethrin — PyGanic, Evergreen rarely match field performance, and the gap is wider for some product categories than others. Residual life on porous surfaces (brick, unsealed wood, concrete) is typically 30 to 50 percent shorter than on the sealed lab surfaces used in registration data. Direct sunlight reduces persistence further — UV breakdown can cut a 90-day residual to under 45 days on south-facing exterior walls. For interior treatments these effects are smaller, but humidity, cleaning products, and foot traffic all reduce real-world residual life.
Temperature interaction is equally important. Pyrethrin — PyGanic, Evergreen, like most modern active ingredients, has an optimal temperature window for both delivery and pest susceptibility. Outside that window, the same dose may underperform by half. Field operators usually adjust application timing rather than rate to compensate, since increasing the rate beyond label specification produces diminishing returns and increases off-target risk.
Mixing partners and tank-mix compatibility also affect real-world performance. Adding an insect growth regulator extends control by addressing eggs and immatures that the adulticide misses. The cost premium for a tank mix is usually under 20 percent and doubles the effective control window.
Practical safety considerations for Pyrethrin — PyGanic, Evergreen
The label is the law, and it covers the legal minimum. Practical safety for Pyrethrin — PyGanic, Evergreen in a household setting goes beyond label compliance — children, pets, and food-contact surfaces all merit precautions above the regulatory floor. Re-entry intervals on consumer labels are typically calibrated for healthy adults; for nurseries, pet bedding areas, and pregnant-occupant homes, doubling the indicated interval is a reasonable default.
Ventilation matters more than most homeowners realize. Even low-VOC formulations release detectable airborne residues for several hours post-application, and an HVAC system that is running during treatment will redistribute those residues throughout the structure. Standard practice is to turn off forced air for the treatment window and the first hour after, then run on high circulation for 30 minutes before normal occupancy resumes.
Personal protective equipment listed on the label is the minimum. For larger volumes, a half-face respirator with organic-vapor cartridges adds meaningful protection at modest cost. Nitrile gloves outperform latex for solvent-based formulations and are inexpensive enough to use single-use.
Active ingredient classes and rotation principles
Pesticide active ingredients are organized into classes based on their mode of action — the biological mechanism through which they affect target pests. The EPA mode-of-action (MoA) classification (and the analogous IRAC classification used internationally for insecticides) labels products by their MoA group, which is the relevant grouping for resistance management. Common residential MoA classes include pyrethroids (group 3, affecting sodium channels), neonicotinoids (group 4, affecting acetylcholine receptors), spinosyns (group 5, separate acetylcholine mechanism), insect growth regulators (group 7, hormone disruption), avermectins (group 6, chloride channels), and several others. Rotating among MoA classes — not just product brands — is the resistance management practice that matters. A homeowner using a pyrethroid product for two seasons then switching to another pyrethroid brand has not rotated meaningfully; switching to a spinosyn or neonicotinoid would be a real rotation. Product labels typically list the IRAC group number on the front panel.
Children, pets, and pesticide exposure: practical risk reduction
Pesticide safety guidance is often written for licensed applicators and translates awkwardly to households with children and pets. The practical residential framework: keep treated surfaces dry before re-entry (typically two to four hours for most water-based residuals, longer for solvent-based), keep pets away from treated zones until dry plus a buffer, store products in original containers in locked storage out of reach of children, never decant products into food or beverage containers (a documented cause of accidental poisonings), and rinse outdoor toys, dog beds, and similar items before re-introducing them to a treated yard area. The exposure routes that matter most are ingestion (children mouthing treated surfaces or contaminated items) and prolonged dermal contact (pets sleeping on freshly-treated carpet). Targeted application — crack-and-crevice, bait stations, perimeter exterior — produces far lower exposure than broadcast spraying, which is one of several reasons IPM-style targeted treatment has displaced broadcast approaches in residential settings.
Application timing within the day and weather conditions
Pesticide applications produce significantly different results depending on application timing, and matching application to conditions improves outcomes substantially. For outdoor liquid applications, early morning (after dew has evaporated, before pollinators are active) and late evening (after pollinators have stopped foraging, before evening dew) produce best results: temperatures are moderate, wind is typically lower, and non-target exposure is reduced. Mid-day applications during high temperatures cause volatility losses and faster degradation. For interior treatments, timing depends on the pest: cockroach baiting works at any time but should follow rather than precede cleaning; bed bug treatments need to follow vacuuming and clutter reduction; ant baits work best when active trails are present, which often means specific times of day for specific species. Rain within 4 hours of outdoor liquid application washes off most surface residue except specifically rainfast formulations; checking the next 24-hour forecast before any outdoor treatment is the basic discipline that prevents this loss. Temperatures above 90°F or below 50°F outside the product label's recommended range produce reduced efficacy.
How treatment thresholds change what 'success' should mean
Most homeowners frame pest control as elimination — zero individuals seen — but professional programs operate on threshold concepts that better match what's actually achievable and economically reasonable. A treatment threshold is the population level at which intervention is justified; below it, the cost and disruption of treatment outweigh the damage prevented. For aesthetic pests like the occasional ant or spider, the threshold is essentially zero only because tolerance is low, not because zero is biologically realistic. For pests with health implications (cockroaches, rodents) or property damage potential (termites, carpenter ants), thresholds are set well below visible damage to allow time for response. The implication for self-evaluation: a program that drops a cockroach population by 95% without reaching zero may be functioning correctly, and pushing for the last 5% may require disproportionate effort or treatment intensity that creates other problems. Reframing 'success' as durable reduction below threshold rather than absolute zero produces saner program design, more reasonable expectations of paid services, and less wasted DIY effort chasing the long tail of a population that's already controlled in any practical sense.
Pesticide rotation and the resistance management problem
Resistance management — using multiple active ingredients in sequence so that no single mode of action selects for resistant individuals — is standard practice in agricultural and commercial pest control but rarely makes it into residential treatment decisions. The underlying concern is real: chronic use of a single pyrethroid product against bed bugs has produced widespread pyrethroid resistance, with some populations now showing resistance factors of 1000x or more. The same pattern is documented in German cockroach resistance to chlorpyrifos and other historical actives, mosquito resistance to organophosphates in heavy-use regions, and house fly resistance across multiple compound classes. For residential treatment, the practical implication is to avoid using the same active ingredient repeatedly across multiple treatment cycles; rotating between products in different chemical families (e.g., pyrethroid → neonicotinoid → insect growth regulator → carbamate, or whatever subset is appropriate to the target pest) reduces selection pressure and preserves efficacy. The product label specifies the active ingredient family, allowing rotation choices to be made on actual chemistry rather than brand name.
Reduced-risk pesticide selection: a category worth knowing
The EPA's reduced-risk pesticide program identifies active ingredients and formulations that meet specific criteria for lower toxicity to non-target organisms, reduced potential for groundwater contamination, lower likelihood of resistance development, or better compatibility with integrated pest management. Products in this category aren't free of toxicity — they're pesticides, and all pesticides have some toxic profile — but they represent the lower end of the risk distribution within their pest categories. For homeowners who want to use pesticides but are concerned about minimizing exposure and environmental impact, looking for products with reduced-risk actives is a defensible filter. Examples include some of the diamide insecticides, spinosyns, and certain microbial products. The catch is that retail availability lags behind the professional market for many reduced-risk products, and consumer pesticide aisles still skew heavily toward older pyrethroid and carbamate formulations. For homeowners willing to source products from agricultural supply channels or work with a pest control company that uses these products, the option exists; for those buying off the shelf at typical retail, the choices are narrower.
When neighborhood-level coordination matters for treatment
Some pests are house-scale problems and some are neighborhood-scale problems, and treating a neighborhood-scale problem as if it were house-scale leads to a familiar frustration: treatment works, then activity returns within weeks because the source was never inside your property. German cockroach problems in multi-unit buildings are the canonical example — treating one unit while the rest of the building is untreated produces temporary relief at best. Rodent infestations frequently span multiple adjacent properties, especially row houses, condo complexes, and dense suburban developments with shared boundary fencing or shared utility easements. Mosquito problems are obviously neighborhood-scale because adult mosquitoes don't respect property lines. The practical implication is that for these pests, isolated treatment is not just incomplete but in some cases economically wasteful. Coordinating with neighbors, talking to HOA or property management about whole-building or whole-block treatment, and identifying the actual sources rather than the symptom locations is what produces durable results. This is uncomfortable work in some neighborhoods, but no amount of treatment intensity in a single unit substitutes for it.
Pesticide drift and the neighbor dimension
Pesticide drift — the off-target movement of applied product through air, water, or runoff — is an under-discussed dimension of residential pesticide use, but it's an increasingly common source of conflict between neighbors and a real factor in the cumulative environmental load of pesticide use. Foliar sprays applied in even light wind drift further than most homeowners expect, particularly with finer droplet sizes. Granular products applied near property lines wash into adjacent properties in significant rainfall. Mosquito fogging can move across multiple properties depending on conditions. The implications are partly legal — drift onto neighboring property without consent has been the basis of successful nuisance claims in some jurisdictions — and partly ethical. Applying products only in low-wind conditions, choosing coarser droplet sizes when possible, using granulars rather than sprays near property lines, and timing applications to avoid imminent rainfall all reduce drift. For homeowners concerned about pesticide exposure from neighbors' applications, the productive conversation is usually about timing and product choice rather than about pesticide use in general, and approaching it that way tends to produce cooperation rather than escalation.