As of 2011, NPIC stopped creating technical pesticide fact sheets. The old collection of technical fact sheets will remain available in this archive, but they may contain out-of-date material. NPIC no longer has the capacity to consistently update them. To visit our general fact sheets, click here. For up-to-date technical fact sheets, please visit the Environmental Protection Agency’s webpage.
Molecular Structure -
Zinc Phosphide
Laboratory Testing: Before pesticides are registered by
the U.S. EPA, they must undergo laboratory testing for
short-term (acute) and long-term (chronic) health effects.
Laboratory animals are purposely given high enough doses
to cause toxic effects. These tests help scientists judge how
these chemicals might affect humans, domestic animals,
and wildlife in cases of overexposure.
- Zinc phosphide is an inorganic compound that is used in pesticide products as
a rodenticide. The International Union of Pure and Applied Chemistry (IUPAC)
chemical name is trizinc diphosphide,1 and the Chemical Abstracts Service
(CAS) registry number is 1314-84-7.2
- Zinc phosphide was first registered for use as a pesticide in the United States by
the U.S. Department of Agriculture (USDA) in 1947.2 Subsequently, a Registration
Standard for zinc phosphide was issued by the United States Environmental
Protection Agency (U.S. EPA) in 1982.3 A Reregistration Eligibility Decision,
or RED, was issued by the U.S. EPA in 1998.2 See the text box on Laboratory Testing.
- Zinc phosphide converts to phosphine gas in the presence of moisture and
acid in the stomach. The toxicity of zinc phosphide is due to phosphine gas
exposure.2 This fact sheet will discuss both zinc phosphide and phosphine.
- Phospine in this fact sheet refers to the gaseous form of this compound The
chemical reaction that releases phosphine is11: Zn3P2 + 6H → PH3 ↑ + 3Zn++
- Aluminum phosphide and magnesium phosphide also react with water to produce phosphine. These compounds are frequently
used to fumigate grain storage facilities. They may be used as rodenticides as well as insecticides.3
- Phosphine is used in the electronics industry and in the manufacture
of organophosphate insecticides.4 Phosphine may also
be produced during the manufacture of methamphetamine
depending on the method used.5
- Under natural conditions, phosphine can be produced during
the anaerobic decomposition of organic matter, such as in the
production of swamp gas.4,6 It is also produced in sewage treatment
plant sediments.7
- Zinc phosphide is a gray-black powder with an odor similar to garlic.1 Phosphine is a colorless and flammable gas. The odor
of industrial or technical grade phosphine gas is similar to garlic or rotting fish, but phosphine in its pure form is odorless.1,8
Humans can begin to detect phosphine at 2 ppm, although toxicity can occur at lower concentrations.9
- Vapor pressure: When dry, zinc phosphide has negligible vapor pressure.1 The vapor pressure of phosphine is 2.93 x 104 mmHg at 25 °C.8
- Octanol-Water Partition Coefficient (log Kow)10: Not found. Zinc phosphide is not soluble in alcohol or water.
- Henry's constant8: Zinc phosphide, none found; phosphine, 2.44 x 10-2 atm·m3/mol.
- Molecular weight (g/mol)8: Zinc phosphide, 258.12 g/mol; phosphine, 34 g/mol.
- Solubility (water): Zinc phosphide is practically insoluble in water1 and insoluble in alcohol.10 Phosphine is considered
slightly soluble in water.8
- Soil Sorption Coefficient (Koc): Not found.
- Rodenticides containing zinc phosphide are used in both agricultural and residential settings. Formulations include bait
pellets, granules, dust, and tracking powders.2 Uses for individual products containing zinc phosphide vary widely. Always
read and follow the label when applying pesticide products.
- Signal words for products containing zinc phosphide may range from Caution to Danger. The signal word reflects the combined
toxicity of the active ingredient and other ingredients in the product. See the pesticide label on the product and refer to
the NPIC fact sheets on Signal Words and Inert or "Other" Ingredients.
- To find a list of products containing zinc phosphide which are registered in your state, visit the website
https://npic.orst.edu/reg/state_agencies.html select your state then click on the link for "State Products."
Target Organisms
- Rodenticide baits containing zinc phosphide must be ingested to be effective.2 They are used to control both commensal
rodents such as house mice and rats, and "field" rodents such as voles, ground squirrels, pocket gophers, and prairie dogs.
Jack rabbits are also targeted pests.2
- The toxicity of zinc phosphide is due to the production of phosphine.10 This is also true of aluminum phosphide and magnesium
phosphide.3 Zinc phosphide requires acidic conditions for appreciable hydrolysis and subsequent formation of
phosphine, whereas aluminum phosphide and magnesium phosphide will hydrolyze to form phosphine in neutral pH.11
- Hydrolysis is strongly pH-dependent for zinc phosphide. At pH 4, 7.1% of zinc phosphide hydrolyzed in 12 hours, whereas
38.8% hydrolyzed at pH 2 over the same period.4
- Once released in the gastrointestinal tract, phosphine gas is absorbed along with zinc.12
- Phosphine disrupts mitochondrial respiration once it is absorbed. The exact mechanism is unknown, but phosphine appears
to block protein and enzyme synthesis.13 Phosphine is a cytochrome C oxidase inhibitor, but this does not appear to
be its sole mechanism of toxicity.14
- Other possible mechanisms of action for phosphine include creation of hydroxyl radicals while simultaneously inhibiting
catalase and peroxidase, corrosion of exposed tissues, and metal toxicity from the zinc, magnesium or aluminum.6,14,15
- Anticholinesterase activity by phosphine has also been suggested, but evidence for this has been mixed.14
Non-target Organisms
- Ingestion of zinc phosphide by non-target mammals or birds leads to the liberation of phosphine and subsequent toxicosis
in the same manner that target mammals are affected. Zinc phosphide is highly toxic to sheep, cows, and goats as well
as non-ruminants.16
- Non-target organisms such as rabbits that are unable to vomit are at particular risk of phosphine poisoning.11
- Phosphine production is increased at decreasing pH. Animals that have recently eaten and have food in their stomachs are
at greater risk than animals with empty stomachs prior to consuming zinc phosphide. This is because of the secretion of
gastric acid into the stomach for digestion.17,18
- Animals with relatively constant release of gastric acid regardless of food intake, such as rats, are at greater risk than animals
such as dogs whose gastric acid is released only following ingestion of food.17
- Zinc phosphide is not expected to pose a secondary poisoning hazard because of its rapid breakdown in the bodies of
animals that ingested it directly. However, experimental oral exposures to animals poisoned by zinc phosphide have led to
secondary poisonings in both cats and dogs.19
- Secondary poisoning appears to be rare in wildlife, although it has occurred in experimental settings. Risk appears to be
dependent at least in part on the consumption of the gastrointestinal tract of the poisoned animal by either a predator or
scavenger. Domestic dogs and cats appear to be more likely to consume the gastrointestinal tract of poisoned prey than
are wild animals.19
TOXICITY CLASSIFICATION - ZINC PHOSPHIDE/PHOSPHINE |
|
High Toxicity |
Moderate Toxicity |
Low Toxicity |
Very Low Toxicity |
Acute Oral LD50 |
Up to and including 50 mg/kg (≤ 50 mg/kg) |
Greater than 50 through 500 mg/kg (>50-500 mg/kg) |
Greater than 500 through 5000 mg/kg (>500-5000 mg/kg) |
Greater than 5000 mg/kg (>5000 mg/kg) |
Inhalation LC50 |
Up to and including 0.05 mg/L (≤0.05 mg/L) |
Greater than 0.05 through 0.5 mg/L (>0.05-0.5 mg/L) |
Greater than 0.5 through 2.0 mg/L (>0.5-2.0 mg/L) |
Greater than 2.0 mg/L (>2.0 mg/L) |
Dermal LD50 |
Up to and including 200 mg/kg (≤200 mg/kg) |
Greater than 200 through 2000 mg/kg (>200-2000 mg/kg) |
Greater than 2000 through 5000 mg/kg (>2000-5000 mg/kg) |
Greater than 5000 mg/kg (>5000 mg/kg) |
Primary Eye Irritation |
Corrosive (irreversible destruction of
ocular tissue) or corneal involvement or
irritation persisting for more than 21 days |
Corneal involvement or other
eye irritation clearing in 8 -
21 days |
Corneal involvement or other
eye irritation clearing in 7
days or less |
Minimal effects clearing in less than 24 hours |
Primary Skin Irritation |
Corrosive (tissue destruction into the
dermis and/or scarring) |
Severe irritation at 72 hours
(severe erythema or edema) |
Moderate irritation at 72
hours (moderate erythema) |
Mild or slight irritation at
72 hours (no irritation or
erythema) |
The highlighted boxes reflect the values in the "Acute Toxicity" section of this fact sheet. Modeled after the U.S. Environmental Protection Agency, Office of Pesticide Programs, Label Review Manual, Chapter 7: Precautionary Labeling. https://www.epa.gov/sites/default/files/2018-04/documents/chap-07-mar-2018.pdf |
Oral
- The oral LD50 for rats was determined to be 21 mg/kg, with a
range of 12-35 mg/kg in one study, and 43-56 mg/kg in another.20,21 The U.S. EPA considered zinc phosphide to be highly toxic
via oral exposure.2 See the text boxes on Toxicity Classification and LD50/LC50.
LD50/LC50: A common
measure of acute toxicity is the lethal dose (LD50) or
lethal concentration (LC50) that causes death (resulting
from a single or limited exposure) in 50 percent of the treated
animals. LD50 is generally expressed as the dose in
milligrams (mg) of chemical per kilogram (kg) of body
weight. LC50 is often expressed as mg of chemical per
volume (e.g., liter (L)) of medium (i.e., air or water) the organism
is exposed to. Chemicals are considered highly toxic when the
LD50/LC50 is small and practically non-toxic
when the value is large. However, the LD50/LC50
does not reflect any effects from long-term exposure (i.e., cancer,
birth defects or reproductive toxicity) that may occur at levels below
those that cause death.
- The oral LD50 for sheep is 60-70 mg/kg.16
- Oral LD50 values were compiled for wild mammals and ranged
from 8 mg/kg for kangaroo rats (Dipodomys spectabilis) and
black-tailed jackrabbits (Lepus californicus) to 93 mg/kg for a kit fox (Vulpes macrotus mutica).19
Dermal
- The dermal LD50 in rabbits was determined to be 2000-5000 mg/kg.22 Zinc phosphide is considered to be low in toxicitybased
on these results.2
- Eye irritation tests performed with zinc phosphide on rabbits resulted in discharge, chemosis or swelling of the eyelid and
eye surface tissue, and some redness in the conjunctiva. The U.S. EPA considered zinc phosphide to be very low in toxicty
for eye irritation.2
- Researchers applied zinc phosphide to the skin of rabbits to determine if it is a skin irritant. Zinc phosphide was found to
be non-irritating. Based on the low dermal toxicity and lack of dermal irritation, the U.S. EPA waived the skin sensitization
tests.2
Inhalation
- The U.S. EPA waived the re-registration requirement of determining an inhalation LC50 for zinc phosphide and considered
it highly toxic via inhalation exposure.2
- Rats exposed to 0, 2.5, 5.0, and 10.0 ppm phosphine for 6 hours all survived, although some animals exhibited nasal discharge
during the exposure. Nasal discharge cleared after the exposure ended, and no exposure-related effects were
noted 14 days after exposure.23
Signs of Toxicity - Animals
- Animals that ingest zinc phosphide may begin showing clinical signs within 1 to 4 hours. Early signs of exposure include
loss of appetite and depressed activity followed by vomiting and painful retching. These signs progress to anxiousness,
ataxia or uncoordinated movements, weakness, labored breathing, thrashing, muscle tremors and convulsions.9,11
- Onset of signs may be delayed for up to 12 hours or more in animals who consumed the bait without any other food in
their stomachs.9 Gastric acid release in animals that have recently eaten causes more rapid release of phosphine.17
- The vomit of poisoned animals may contain blood. The vomit can also include phosphine, which can be dangerous to humans
at levels below which its odor can be detected.9,11
- Rats poisoned with 10 mg/kg aluminum phosphide administered intraperitoneally demonstrated a drop of 47% in cholinesterase
activity.24
- Researchers exposed rats to aluminum phosphide by inserting it through the stomach wall. Treated rats developed methemoglobinemia.25
Signs of Toxicity - Humans
- Zinc phosphide dust may release phosphine once it contacts the moist tissues of the respiratory tract if the dust is inhaled,
resulting in pulmonary edema and cardiotoxicity. If ingested, zinc phosphide releases phosphine in the gut and may cause
headache, dizziness, fatigue, nausea and vomiting, cough, dypsnea, chest tightness, and thirst. Other signs include liver
failure, jaundice, loss of ability to urinate, tetany, delirium, convulsions, coma, and death.12,14
- Death in humans from fatal doses may be delayed for 30 hours after exposure, with the majority of tissue damage occurring
in the liver, kidneys and heart.26
- Victims of lethal phosphine exposure were found to have liver, myocardial, and alveolar cell necrosis, pulmonary edema
and microscopic pulmonary congestion, and anoxic damage in the brain.6
- Hyperglycemia following exposure to phosphine has also been reported.13,27 In a study of 45 patients admitted to the hospital
following aluminum phosphide poisoning, researchers noted that increased blood glucose levels or hyperglycemia
were associated with fatal outcomes.13
- Elevated levels of the enzyme creatine phosphokinase were found in two instances of severe poisoning by phosphine.28,29
- Aluminum and phosphine have been shown to interfere with acetylcholinesterase in humans, but the impact of this inhibition
on the toxicity is not clear.14
- Always follow label instructions and take steps to minimize exposure. If any exposure occurs, be sure to follow the First Aid
instructions on the product label carefully. For additional treatment advice, contact the Poison Control Center at 1-800-
222-1222. If you wish to discuss an incident with the National Pesticide Information Center, please call 1-800-858-7378.
Animals
- Rats inhaled phosphine 5 days a week, 6 hours a day, for up to 2 years. The concentrations tested were 0.3, 1.0, and 3.0 ppm.
The researchers did not detect any toxic or carcinogenic effects from these exposures.30
- Rats inhaled phosphine at concentrations of 0, 0.3, 1.0, and 3.0 ppm for 6 hours a day for 13 weeks. An additional group
of rats was exposed to 5.0 ppm of phosphine for 6 hours a day for 13 days. Rats exposed to 1.0 ppm or more gained less
weight and consumed less food than controls. Minor changes in blood parameters and kidney function were noted in animals
in the 3.0 and 5.0 ppm exposure groups, although all effects disappeared after cessation of exposure.23
- Mice inhaled phosphine at concentrations of 0, 0.3, 1.0, and 4.5 ppm for 6 hours per day, 5 days per week for 13 weeks. Doserelated
decrease in weight gain was noted particularly in female mice. Masses of male kidneys, heart, brain, and lungs were
less than those of controls at all dose levels, whereas females' organs increased in mass at the 4.5 ppm exposure level.31
- Researchers fed rats baits containing either 0.02 or 0.03% zinc phosphide
for up to 58 or 31 days, respectively. During the first week, rats
in the treatment groups gained less weight than control group rats. All
rats in the 0.03% treatment group died, and two rats from the lowerdose
group died by the end of the study. Researchers found liver injury
in rats from the high-dose group. Lung damage was also noted.17
NOAEL: No Observable Adverse Effect Level
NOEL: No Observed Effect Level
LOAEL: Lowest Observable Adverse Effect Level
LOEL: Lowest Observed Effect Level
- A 90-day subchronic study was performed on rats. Researchers administered zinc phosphide by gavage (stomach tube) at
doses of 0.1, 1.0, or 3.0 mg/kg/day. Animals dosed with 1.0 or 3.0 mg/kg/day showed excess salivation and lowered external
body temperature. Hydronephrosis, or swelling of the kidney with excess urine, was noted in the male rats in the 1.0 and 3.0
mg/kg/day dose groups, and males in the highest dose group also developed kidney infections. The NOEL was established
at 0.1 mg/kg/day.2 See the text boxes on NOAEL, NOEL, LOAEL, and LOEL.
- The chronic RfD for zinc phosphide was set at 0.0001 mg/kg/day based on the subchronic exposure study in rats.2 See the text box on Reference Dose (RfD).
- Rats were dosed with 40, 80, or 160 mg zinc phosphide or fed bait containing 2% zinc phosphide prior to being offered to
ferrets. Ferrets were fed a total of five rats over a 10-day period. Ferrets fed control rats readily ate the gastrointestinal tracts,
but ferrets fed dosed rats began to avoid eating the gastrointestinal tracts of poisoned rats after 4 days, particularly those
in the high-dose group. Blood chemistry of ferrets fed poisoned rats had reduced hemoglobin-to-iron ratios and increased
triglyceride concentrations compared to control ferrets, although there was considerable individual variation.32
- Researchers fed gray foxes (Urocyon cinereoargeneus) and red foxes (Vulpes vulpes) exclusively on voles killed with zinc
phosphide for 3 days. Dosed foxes ate less food and cached fewer poisoned voles than they had when fed unpoisoned
voles prior to the study.33
Humans
- Chronic, low-level inhalation or oral exposures to zinc phosphide in people have been associated with weakness, anemia,
toothache, necrosis of the jaw bones and associated swelling, weight loss, and spontaneous fractures.4
- Blood samples taken from fumigant applicators and control subjects were examined for chromosomal abnormalities. Researchers
collected samples during the application season, and 6 weeks to 3 months after application. Fumigant applicators
who had been exposed to phosphine had more chromosome abnormalities than control subjects during the application
season. Chromosomal rearrangements were more common in phosphine applicators than in controls 3 months after
exposure.34
- More recent investigations repeated the earlier work above, but found no such differences.35,36 One group of researchers
hypothesized that improved personal protective equipment practices were responsible for the change.36 Other researchers
reported that chromosomal breaks were more prevalent in men who used fumigants relative to controls, but these
applicators also used insecticides and herbicides.37
Cancer: Government agencies in the United States and abroad have developed programs to evaluate the
potential for a chemical to cause cancer. Testing guidelines and classification systems vary. To learn more
about the meaning of various cancer classification descriptors listed in this fact sheet, please visit the
appropriate reference, or call NPIC.
- No data were found on the ability of zinc phosphide or phosphine to disrupt the endocrine system.
Animals
- The U.S. EPA waived requirements for carcinogenicity studies for zinc phosphide because chronic exposure is not expected.2
- Rats were fed diets for 2 years that had been fumigated with phosphine at rates of 48 and 90 g/metric ton for 48 and 72
hours, respectively. Feed was stored frozen following fumigation and residues at time of thawing averaged 1 ppm. Residues
were expected to begin to dissipate at thawing, and were therefore unknown at time of consumption. No signs of carcinogenicity
were noted.38
- Rats exposed to phosphine through whole-body inhalation at concentrations of 0.3, 1.0, and 3.0 ppm for up to 2 years exhibited
no carcinogenic effects.30
Humans
- The U.S. EPA determined that chronic exposure to zinc phosphide should be negligible and therefore waived carcinogenicity
testing requirements for reregistration.2 See the text box on Cancer.
- No human data were found on carcinogenic effects of zinc phosphide or phosphine.
Animals
- Researchers dosed 25 pregnant female rats per group daily by stomach tube at doses of 1, 2, or 4 mg/kg/day during the
second week of the pregnancy. Nine of the rats in the highest dose group died although the cause of death was not determined.
Rats in the highest dose group also ate less and lost weight in the first half of the week. Both parameters returned
to pre-study levels by the end of the treatment period. The maternal NOEL was established at 2 mg/kg/day.39
- Researchers exposed 24 pregnant female rats to phosphine for the 20 days of gestation at concentrations of 0, 0.03, 0.33,
2.80, 4.90, and 7.50 ppm in whole-body exposure tests. Fourteen of the females died by day 10 in the high-dose group. No
treatment-related effects were noted in the dams of all other exposure groups.23
- Ten male and 10 female adult rats were fed 0.03% zinc phosphide for 22 days. One male and four females died before the end
of the exposure. All of the surviving rats maintained their fertility despite the exposure.17
Humans
- No human data were found on the teratogenic or reproductive effects of zinc phosphide or phosphine exposure.
Absorption
- Absorption of phosphine occurs through inhalation. It also occurs across the gastro-intestinal tract following ingestion of
zinc phosphide and subsequent production of phosphine. Dermal absorption of zinc phosphide is low.4,16
- Aluminum phosphide and magnesium phosphide are expected to hydrolyze to phosphine upon contact with moist respiratory
membranes, and the phosphine can then be absorbed by the lungs.4
- Inhalation exposure to zinc phosphide may lead to exposure through the gastrointestinal tract via particulate clearance
mechanisms in the lungs, which could result in ingestion of particulate matter containing zinc phosphide. Subsequent
hydrolysis and absorption of phosphine may occur.4
Distribution
- Clinical signs in human poisonings suggest that phosphine is widely distributed to the liver, kidneys, and central nervous system.4
Metabolism
- Metabolism of zinc phosphide is not well understood.14
Excretion
- Phosphine may be exhaled from the lungs as the parent compound.4
- The primary metabolite excreted in animal urine is hypophosphite.4
- Tissue samples taken from suicide victims were analyzed using headspace gas chromatography with inductively coupled
plasma mass spectrometry or a nitrogen-phosphorus detector following the fatal ingestion of aluminum phosphide tablets.
Phosphine residues were detected in the brain, kidney, liver, heart, and surrenals. Phosphorus and aluminum residues
were detected in blood.40,41
- Silver nitrate strips have also been used to detect phosphine in post-mortem tissue samples. However, the process of anaerobic
decomposition may produce traces of phosphine that are independent of any exogenous exposure.42
- These biomarkers have not been widely utilized.
Soil
- Zinc phosphide oxidized in 5 weeks when placed in soils that had at least 50% moisture saturation.4
- Three volcanic soil types with organic matter ranging from 3-15% were mixed with water to 25, 50, 75, and 100% saturation.
Researchers then added 4.17 mg/g zinc phosphide to the soil and sealed the mixtures in glass vials. The maximum amount
of phosphine liberated from one saturated soil type was 32% of the total amount possible based on phosphorus content of the zinc phosphide. Phosphine production from the soils peaked at 1-9 days after addition, depending on soil type and
moisture content.43
- In the same study, researchers added zinc phosphide to dry soils and sealed the mixture in glass vials. During the incubation
process, no phosphine was detected in the headspace of the vials. The researchers concluded that zinc phosphide may
have oxidized to zinc phosphate, and that any phosphine produced during the decomposition subsequently oxidized as
well.43
- Phosphine diffuses into the voids within soil but this process is reduced with increasing soil moisture levels.43 Phosphine
absorbed by soils is subsequently oxidized to orthophosphate.4
- Five commercial zinc phosphide baits placed on silt clay loam from harvested sugar cane fields retained 50-100% of the
original zinc phosphide content at the end of 16 days. The loss was greatest in the oat bait that had a surface treatment of
zinc phosphide.44
The "half-life" is the time required for half of the
compound to break down in the environment.
1 half-life = 50% remaining
2 half-lives = 25% remaining
3 half-lives = 12% remaining
4 half-lives = 6% remaining
5 half-lives = 3% remaining
Half-lives can vary widely based on environmental
factors. The amount of chemical remaining after a
half-life will always depend on the amount of the
chemical originally applied. It should be noted that
some chemicals may degrade into compounds of
toxicological significance.
Water
- Zinc phosphide placed in fresh or salt water for 11 days showed little hydrolysis.4
- Hydrolysis of zinc phosphide is substantial only in highly acidic conditions
of pH 4 or below.4
- Sediments in water are expected to facilitate the breakdown of zinc
phosphide to either phosphine under anaerobic conditions, or phosphoric
acid under aerobic conditions.4
- Phosphine will oxidize in water to form hypophosphorus acid.4
Air
- Phospine released into the air rapidly breaks down following reaction
with hydroxyl radicals, with a half-life of 5-28 hours. The oxidation
products are inorganic phosphate and phosphorus oxyacids.4
See the text box on Half-life.
- Phosphine will spontaneously combust at concentrations of greater than 1.8% and temperatures of 38 °C (104 °F). If other
phosphorus hydride impurities are present, phosphine may ignite at room temperature.4
Plants
- Commercial rodenticide pellets containing 2% zinc phosphide were
placed in artificial gopher burrows in an alfalfa field. Pellets were
applied at 3 pounds per acre (the label rate), 6 pounds per acre, and
9 pounds per acre in burrows 8" deep and 10' apart. Above-ground
portions of the alfalfa were harvested after 1, 2, 7, and 30 days. No
residues of zinc phosphide were detected in the
alfalfa.45
- A rodenticide bait containing 2% zinc phosphide was broadcast at rates of 5, 10, and 50 lbs/acre on sugarcane in Hawaii
four times at two-month intervals. Samples of vegetation were taken one week after the final application and at harvest,
110 days later. The samples at one week contained 0.004-0.015 ppm of phosphine at the dry site and 0-0.045 ppm of phosphine
at the wet site. At harvest, phosphine residues at the dry site were 0.006-0.032 ppm. No residues were detected at
the wet site at harvest.46
Indoor
- No data were found on indoor fate of either zinc phosphide or phosphine.
Food Residue
- The USDA does not monitor food samples for zinc phosphide or phosphine as part of the Pesticide Data Program.47,48
Phosphine tolerances from the use of zinc phosphide are established for hay, wheat, alfalfa, barley, potatoes, grapes, sugar
beets, and beans.49
- The U.S. EPA determined that neither acute nor chronic exposure to zinc phosphide was expected through the diet.2
Birds
- The acute LD50 for northern bobwhite quail (Colinus virginianus) is 12.9 mg/kg,50 and the LD50 for mallard ducks (Anas platyrhynchos)
is 67.4 mg/kg.51 The 5-day LC50 was 469 ppm in bobwhite quail and 2885 ppm in mallards.52,53
- The LD50 values for other bird species ranged from 7.5 to 12.0 mg/kg for three species of geese (Canada goose Branta
canadensis, white-fronted goose Anser albifrons, and snow goose A. caerulescens) and 24 to 178 mg/kg for red-winged
blackbirds (Agelaius phoeniceus).19,54
- Canada geese (Branta canadensis moffitti) and white-fronted geese (Anser albifrons) were placed in pens in alfalfa and fescue
fields that were treated with a 1% zinc phosphide grain bait. The exposure interval was 4 days. Four of the six Canada
geese died following exposure to grain bait on fescue, and the rest lost weight. White-fronted geese exposed to bait on
alfalfa all survived, although the geese did consume sublethal amounts of the bait. The white-fronted geese appeared to
develop an aversion to the bait, which may have been due to the strong emetic action of zinc phosphide. The researchers
concluded that insufficient forage leads to greater likelihood of bait ingestion.54
- Wild geese and domestic fowl exposed to repeated sublethal doses of zinc phosphide appeared in some cases to develop
diarrhea. Researchers noted increased excretion of bile pigments in the droppings of the domestic fowl.54,55
- Researchers fed great horned owls (Bubo virginianus) for 3 days exclusively on voles killed with 87 mg/kg zinc phosphide
5 hours prior to being offered to the owls. The owls began roosting on the floor of their pens rather than on perches and
refused to take flight when disturbed.33
Fish and Aquatic Life
- Phosphine is poorly soluble in water, but when it is in solution it can be acutely toxic to aquatic life.4
EC50: The median effective concentration (EC50) may be
reported for sublethal or ambiguously lethal effects. This
measure is used in tests involving species such as aquatic
invertebrates where death may be difficult to determine.
This term is also used if sublethal events are being
monitored.
Newman, M.C.; Unger, M.A. Fundamentals of Ecotoxicology; CRC Press, LLC.:
Boca Raton, FL, 2003; p 178.
- The 96-hour LC50 for phosphine exposure in rainbow trout (Oncorhynchus
mykiss) was 0.0097 ppm. The EC50 for Daphnia exposed to phosphine in a 24-hour test was 0.2 mg/L.1 See the text box on EC50.
- An acute LC50 for rainbow trout exposed to phosphine was reported as 0.5 mg/L, and for bluegill sunfish (Lepomis macrochirus)
the LC50 was 0.8 mg/L.1
Terrestrial Invertebrates
- No information was found on the effects of zinc phosphide or phosphine on terrestrial invertebrates.
- The chronic reference dose or cRfD for zinc phosphide is 0.0001 mg/kg/day.2 See the text box on Reference Dose (RfD).
Reference Dose (RfD): The RfD is an estimate of the quantity of
chemical that a person could be exposed to every day for the rest
of their life with no appreciable risk of adverse health effects. The
reference dose is typically measured in milligrams (mg) of chemical
per kilogram (kg) of body weight per day.
U.S. Environmental Protection Agency, Integrated Risk Information System, IRIS Glossary, 2009. https://www.epa.gov/iris/iris-glossary#r
- The U.S. EPA did not classify zinc phosphide or phosphine with regards to carcinogenicity because chronic exposure is not
expected.2 See the text box on Cancer.
- The National Institute for Occupational Safety and Health (NIOSH) Recommended Exposure Limit, Time-Weighted Average
(REL, TWA) for phosphine is 0.4 mg/m3.51
- The Permissible Exposure Limit (PEL) for phosphine is 0.4 mg/m3.56
- The Acute Exposure Guideline Levels, or AEGLs, for zinc phosphide range from 3.6 ppm for AEGL-3 for a 10-minute exposure
to 0.13 for an 8-hour exposure, AEGL-2.57
- The ACGIH Threshold Limit Value, or TLV, for phosphine is 0.3 ppm or 0.4 mg/m3.58
- The exposure level considered Immediately Dangerous to Life and Health, or IDLH, for phosphine is 50 ppm.58
Date Reviewed: September 2010
Please cite as: Gervais, J. A. ; Luukinen, B.; Buhl, K.; Stone, D. 2010. Zinc Phosphide/Phosphine Technical Fact Sheet; National
Pesticide Information Center, Oregon State University Extension Services. https://npic.orst.edu/factsheets/znptech.html.