🧪 Active Ingredient Profile

Cholecalciferol (Vitamin D3) Rodenticide

Acute Rodenticide (Hypercalcemia Agent)

Cholecalciferol — yes, it is literally Vitamin D3 — is used as a rodenticide at extremely high doses. It causes fatal hypercalcemia (calcium overload) in rodents within 3-4 days. It is gaining popularity as anticoagulant rodenticides face increasing restrictions due to secondary poisoning concerns.

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Classification
Acute Rodenticide (Hypercalcemia Agent)
Signal Word
Caution
Mode of Action
Hypercalcemia: massive calcium mobilization from bones → calcium deposits in kidneys, heart, blood vessels → organ failure
⚖️ Educational use only. Always read and follow the full product label — the label is the law under FIFRA. Full disclaimer → | ⚗️ Mixing Calculator →

🎯 Target Pests

Rats and mice. Less commonly used for other rodents. Requires multiple feedings over 2-3 days for lethal dose in most formulations — not a single-feed kill like zinc phosphide or bromethalin.

🏷️ Products & Brand Names

Terad3 Blox (Bell Labs — the dominant brand), d-Con (some formulations contain cholecalciferol), Selontra (BASF — professional, contains cholecalciferol). Growing number of products as anticoagulant alternatives.

⚠️ Safety & Precautions

The irony: Vitamin D3 is essential for human health at normal doses (400-4000 IU/day) but lethal to rodents at the doses in bait (40,000-60,000 IU/gram). However, concentrated rodenticide bait is absolutely toxic to pets and humans if ingested.

⚠️ PET DANGER: Dogs that eat cholecalciferol rodent bait face life-threatening hypercalcemia. Symptoms may not appear for 24-36 hours but can be fatal. Aggressive IV fluid therapy and calcitonin treatment are needed. If your dog eats this bait, go to emergency vet IMMEDIATELY — do not wait for symptoms.
⚠️ No antidote shortcut: Unlike anticoagulant rodenticides (which have a Vitamin K1 antidote), cholecalciferol poisoning requires intensive supportive care. Treatment is expensive and prolonged. Prevention is critical — use tamper-resistant bait stations.
Example
0.5 oz
per gallon
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💡 Pro Tips

Why it's growing in popularity: Cholecalciferol has lower secondary poisoning risk than second-generation anticoagulants. A predator that eats a poisoned rodent receives a fraction of the lethal dose. This makes it preferred in areas with endangered raptors or other wildlife.

Speed: Death typically occurs 3-4 days after lethal dose ingestion. Rodents become lethargic and seek water before dying. This is slower than zinc phosphide or bromethalin but faster than first-generation anticoagulants.

Resistance: No known resistance in any rodent population — a significant advantage over anticoagulant rodenticides, which face widespread resistance in some rat populations.

🐛 Pests This Treats — Learn More

Click any pest to view its full identification guide, biology, and treatment options.

🐛 Ants → 🐛 Mice → 🐛 Rats → 🐛 Scales → 🐛 Ticks →

🌿 Environmental & Ecological Impact

🐝 Bees / PollinatorsNONE
🐟 Fish / Aquatic LifeLOW
🐦 BirdsMODERATE
🐕 Mammals / PetsVERY HIGH
🦐 Aquatic InvertebratesLOW
💡 Vitamin D3 rodenticide. Extremely toxic to dogs — no antidote. Lower secondary poisoning risk than anticoagulants.

❓ Frequently Asked Questions

Q: Is cholecalciferol safe for pets?
Follow the product label. Keep pets out of treated areas until completely dried (2–4 hours for sprays). Once dry, treated surfaces pose minimal risk to dogs and cats.
Q: Can I use cholecalciferol indoors?
Check the specific product label — formulations vary. Baits and dusts often have indoor labeling; concentrates and granulars are typically outdoor.
Q: How long does cholecalciferol last after application?
Residual varies by formulation, surface type, weather, and UV exposure. Indoor applications last longer than outdoor. Check the product label for re-application intervals.
Q: What should I do if exposed?
Remove contaminated clothing, wash skin with soap and water. For eye contact, rinse 15–20 minutes. For ingestion or severe symptoms, call Poison Control (1-800-222-1222). Have the product label available.

📋 Safety Data Sheet (SDS)

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Cholecalciferol (Vitamin D3) Rodenticide — Safety Data Sheet

View the official SDS document for this product directly on the CDMS label database.

Cholecalciferol (Vitamin D3) Rodenticide Safety Data Sheet page 1
📄 Cholecalciferol (Vitamin D3) Rodenticide — Safety Data Sheet · View the complete SDS document above or download below
💡 Did you know? It takes about 50,000 times the normal human daily dose of Vitamin D3 to create a lethal rodenticide bait. The same vitamin that strengthens your bones causes fatal calcium deposits in rodent organs at these extreme concentrations.
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Reviewed by Derek GiordanoContent reviewed by a licensed pest management professional. Last reviewed: April 2026.
📚 Sources: EPA Pesticide Labels · NPIC Pesticide Info

How Cholecalciferol (Vitamin D3) Rodenticide performs in real-world conditions

Laboratory efficacy numbers for Cholecalciferol (Vitamin D3) Rodenticide 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. Cholecalciferol (Vitamin D3) Rodenticide, 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 Cholecalciferol (Vitamin D3) Rodenticide

The label is the law, and it covers the legal minimum. Practical safety for Cholecalciferol (Vitamin D3) Rodenticide 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.

Comparing Cholecalciferol (Vitamin D3) Rodenticide to alternatives

Choosing between Cholecalciferol (Vitamin D3) Rodenticide and a comparable product usually comes down to four factors: speed of kill, residual length, target spectrum, and household-sensitivity profile. No single product wins on all four — fast-acting contact kills typically have short residuals, while long-residual products often act slowly enough that homeowners assume they have failed within the first 48 hours. Matching the product to the situation is more important than picking the strongest available option.

Cost per application is a useful but incomplete metric. A cheaper concentrate that requires more frequent reapplication often costs more per season than a more expensive product with a longer effective window. Coverage area per gallon at the label rate is the better comparison number, and it is usually printed clearly on the label.

For most households, keeping two complementary products — one fast-acting and one long-residual, ideally from different chemical classes — covers more situations than a single all-purpose product and supports the resistance-management rotation noted above.

Published: Jan 1, 2025 · Updated: Apr 7, 2026

Storage and disposal of pesticide products

Pesticide storage and disposal practices have meaningful safety and environmental implications that many homeowners overlook. Storage practices that matter: keep products in original containers with intact labels (decanting is a documented poisoning cause and makes label-required information unavailable when needed), store in a locked area or cabinet inaccessible to children and pets, separate from food and animal feed, in a temperature-controlled location (extreme cold and extreme heat both degrade many products), and elevated above floor level to prevent contamination from spills. Disposal practices: never pour unused products down drains, on the ground, or into household trash; consult the label disposal instructions and your municipality's household hazardous waste program (most jurisdictions have collection events or permanent sites), and use up small remaining quantities at label rates rather than disposing of partial containers when possible. Empty containers, after triple rinsing as the label specifies, can typically go in recycling or trash per the label, but rinsate must be applied as the original product would be.

Documenting infestations: what helps and what doesn't

When a pest problem persists across multiple treatments, documentation becomes the single most useful tool for figuring out what's actually happening. The pattern that's worth tracking: date and location of every sighting, number of individuals, life stage if identifiable (adult, nymph, egg case), any treatment applied, and weather or seasonal context. Photos with a coin or ruler for scale matter more than people expect — species identification from memory is unreliable, while photos let an extension entomologist or professional confirm species accurately. A simple notebook or spreadsheet kept for one or two pest seasons reveals patterns that aren't visible in isolated observations: which rooms peak first, which months are reliable hot spots, which treatments seem to work and which don't. Professionals who inspect properties with this kind of homeowner-kept log diagnose faster and recommend more accurate interventions.

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.

The cost of doing nothing: implicit pest tolerance and its hidden expenses

Pest control discussions usually frame the costs of treatment without quantifying the costs of non-treatment, but the latter are often larger and almost always less visible. Cockroach allergens add measurable healthcare costs in homes with asthma. Rodent activity in attics damages insulation (reducing R-value and adding seasonal heating and cooling costs) and creates fire risk through wire chewing that doesn't show up until something fails. Termite damage in unmonitored properties produces structural repair bills in the five-figure range, often discovered during unrelated renovation. Stored-product pests destroy food inventory at rates that aren't tracked because items are discarded individually rather than tallied. The cumulative cost of doing nothing isn't a single line item but a sum of small chronic losses across years. The framing that helps: pest control isn't a luxury expense layered onto a working baseline; it's a maintenance expense that competes with the slow accumulating cost of allowing a problem to continue. Households running the comparison honestly almost always find that modest preventive spending is the cheaper path.

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.

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.

Pesticide residual life and reapplication intervals

The residual life of a pesticide is one of the most misunderstood properties in household pest management. Active ingredients vary widely in how long they remain bioavailable on a treated surface, and the same active can behave very differently depending on substrate, exposure to sunlight and rain, temperature, and the formulation it's carried in. A pyrethroid applied to a porous masonry surface in full sun will degrade in days; the same active in a microencapsulated formulation on a protected interior surface may remain effective for months. Understanding this is the difference between an evidence-based treatment schedule and one driven by superstition. Reapplying too soon wastes product and increases selection pressure for resistant individuals; reapplying too late creates gaps in coverage during which pest populations rebound. The right answer depends on specific conditions and is not the same number printed on the bottle in all circumstances. Field experience and willingness to monitor for early signs of pest return are what calibrate the schedule. The label is a guide, but conditions in front of you are the real input.

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.