| Zinc phosphide |

Last updated: 30/10/2025
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(Also known as: zincphos; zinc diphosphide) |
The following alerts are based on the data in the tables below. An absence of an alert does not imply the substance has no implications for human health, biodiversity or the environment but just that we do not have the data to form a judgement. These hazard alerts do not take account of usage patterns or exposure, thus do not represent risk.
| Environmental fate |
Ecotoxicity |
Human health |
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Used in bait products for the control of rodents in a variety of situations |
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Rats; Mice; Pocket gophers; Meadow voles |
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Agricultural crops; Vegetables; Ornamentals; Orchards; Crop storage. |
|
|
- |
|
|
- |
|
|
- |
|
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Not approved |
|
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Withdrawn |
|
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No UK approval for use as a plant protection agent |
| EC Regulation 1107/2009 (repealing 91/414) |
|
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Approved |
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Austria/Germany |
|
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31/12/2026 |
|
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No |
|
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Yes |
|
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ATAustria |
BEBelgium |
BGBulgaria |
CYCyprus |
CZCzech Republic |
DEGermany |
DKDenmark |
EEEstonia |
ELGreece |
| ✓ |
✓ |
✓ |
  |
✓ |
✓ |
  |
  |
  |
ESSpain |
FIFinland |
FRFrance |
HRCroatia |
HUHungary |
IEIreland |
ITItaly |
LTLithuania |
LULuxembourg |
| ✓ |
  |
✓ |
✓ |
✓ |
  |
✓ |
  |
✓ |
LVLatvia |
MTMalta |
NLNetherlands |
PLPoland |
PTPortugal |
RORomania |
SESweden |
SISlovenia |
SKSlovakia |
|   |
  |
  |
✓ |
  |
✓ |
  |
✓ |
✓ |
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|
ISIceland |
NONorway |
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|   |
  |
  |
  |
  |
  |
  |
  |
  |
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None |
|
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Zn₃P₂ |
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P=[Zn].P=[Zn].[Zn] |
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- |
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HOKBIQDJCNTWST-UHFFFAOYSA-N |
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InChI=1S/2P.3Zn |
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Yes |
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Rodenticide |
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Inorganic compound |
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>800 g kg⁻¹ |
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EU dossier - none declared |
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Synthetic |
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Toxicity caused by the production of phosphine under acid conditions in the rodents stomach. Phosphine, a nerve toxin, has respiratory action, mitochondrial complex IV electron transport inhibitor |
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- |
|
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- |
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- |
|
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- |
|
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- |
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1314-84-7 |
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215-244-5 |
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69 |
|
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088601 |
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25113606 |
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015-006-00-9 |
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258.1 |
|
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- |
|
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trizinc diphosphide |
|
|
zinc phosphide |
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| UK Poisons List Order 1972 |
Rotterdam Convention |
Montreal Protocol |
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| Stockholm Convention |
OSPAR |
EU Water Framework Directive |
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|
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- |
|
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- |
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Yes [ C1 Criterion 1: Pesticide active ingredients that meet the criteria of classes Ia or Ib of the WHO Recommended Classification of Pesticides by Hazard ] |
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Yes [ R01 Rule 1: Pesticide active ingredients that meet the criteria of classes Ia or Ib of the WHO Recommended Classification of Pesticides by Hazard (or those with a CLP classification of H330) ; R09 Rule 9: Pesticide active ingredients that have demonstrated a high aquatic toxicity (where acute ecotoxicity for fish, invertebrates or algae =< 0.1 mg l⁻¹) ] |
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- |
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None allocated |
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None allocated |
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None allocated |
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- |
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- |
|
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Grey-black coloured powder with strong characteristic odour |
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Current |
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1947, first registered USA. |
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- Arrex E Köder
- Blue-Ox
- Zinc-Tox
- Gopha-Rid
- Prozap
- Fumitoxin
- Modesto
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Usually formulated as bait or tracking powder |
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Zinc phosphide is typically produced by a direct synthesis method involving the reaction of metallic zinc powder with red phosphorus. The two components are mixed in a precise mass ratio, usually around 3.1 to 3.3 parts zinc to 1 part phosphorus, and placed into a high-purity graphite boat. This mixture is then introduced into a smelting furnace under a protective inert gas atmosphere, such as nitrogen or argon, to prevent unwanted oxidation. The sealed furnace is gradually heated, often between 100 and 900 DegC, allowing the elements to react and form zinc phosphide. |
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Data for the amount of life cycle GHGs produced by zinc phosphide are not available in the public domain. However, whilst estimates vary, more general data suggests that between 14 and 30 kilograms of CO₂e is emitted per kilogram of substance produced. |
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0.0014 |
|
Low |
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500 |
n-Heptane |
- |
| 500 |
Xylene |
- |
| 500 |
Methanol |
- |
| 500 |
Acetone |
- |
|
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500 |
|
- |
|
|
500 |
|
- |
|
|
500 |
|
- |
|
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- |
- |
- |
|
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|
- |
- |
- |
|
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- |
- |
- |
|
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- |
- |
- |
|
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
| - |
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6.5 X 10-06 |
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Low volatility |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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72.8 |
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- |
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- |
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10.95 |
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Non-persistent |
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10.95 |
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Non-persistent |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
|
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- |
- |
- |
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EU dossier lab studies DT₅₀ range 7.8-14.1 days |
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- |
- |
- |
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- |
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- |
- |
- |
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- |
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- |
- |
- |
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- |
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Stable |
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Stable |
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Stable at pH 5 to 9 and 20 °C, at pH4 DT₅₀ = 38 days |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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As this parameter is not normally measured directly, a surrogate measure is used: ‘Photochemical oxidative DT₅₀’. Where data is available, this can be found in the Fate Indices section below. |
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- |
| Soil adsorption and mobility |
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| Known groundwater metabolites |
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None
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| hypophosphite |
- |
Mammal (Urine); Animal |
- |
| phosphite |
- |
Mammal (Urine); Animal |
- |
| phosphonic acid |
- |
Air (photo-oxidation) |
- |
| phosphoric acid |
- |
Air (photo-oxidation) |
- |
| Terrestrial ecotoxicology |
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12 |
Rat |
High |
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- |
- |
- |
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- |
- |
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- |
- |
- |
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12.9 |
Colinus virginianus |
High |
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- |
- |
- |
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- |
- |
- |
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> 1000 |
Eisenia foetida |
Low |
|
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- |
- |
- |
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Nitrogen mineralisation: No significant adverse effect Carbon mineralisation: No significant adverse effect |
Dose = 240 g ha⁻¹ 28 Day |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
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- |
- |
- |
| - |
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- |
- |
- |
| - |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
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- |
- |
- |
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- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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> 21.7 |
Leuciscus idus |
Moderate |
|
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- |
- |
- |
|
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- |
- |
- |
|
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114 |
Daphnia magna |
Low |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
|
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- |
- |
- |
|
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- |
- |
- |
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0.00375 |
Desmodesmus subspicatus |
High |
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0.0014 |
Desmodesmus subspicatus |
Moderate |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
| HUMAN HEALTH AND PROTECTION |
|
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High (class III) |
- |
- |
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12 |
Rat |
High |
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~ 1000 |
Rat |
- |
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> 11 |
Rat |
- |
|
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- |
- |
- |
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0.042 |
Rat SF=100 |
- |
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0.073 |
Rat SF=100 |
- |
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- |
- |
- |
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0.042 |
Rat SF=100 |
- |
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10 |
default |
- |
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- |
- |
- |
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Negligible risk for bystanders |
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Acceptable risk for workers |
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- |
- |
- |
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| Carcinogen |
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Endocrine disruptor |
XNo, known not to cause a problem |
A3 A = Chromosome aberration (EFSA database) 3 = Negative ; B0 B = DNA damage/repair (EFSA database) 0 = No data ; C0 C = Gene mutation (EFSA database) 0 = No data ; D0 D = Genome mutation (EFSA database) 0 = No data ; E2 E = Unspecified genotoxicity type (miscellaneous data source) 2 = Mixed/ambiguous results |
No data found |
| Reproduction / development effects |
Acetyl cholinesterase inhibitor |
Neurotoxicant |
✓Yes, known to cause a problem |
?Possibly, status not identified |
No data found |
| Respiratory tract irritant |
Skin irritant |
Skin sensitiser |
| No data found |
XNo, known not to cause a problem |
No data found |
| Eye irritant |
Phototoxicant |
  |
XNo, known not to cause a problem |
No data found |
  |
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Highly toxic in phosphine form May be fatal if swallowed |
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Not explosive or oxidising Contact with acids liberates very toxic gas Moisture sensitive Not expected to auto-ignite; Not highly flammable IMDG Transport Hazard Class 4.3 |
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Health: H300 Handling: H260 Environment: H400, H410 |
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Ib (Highly hazardous) |
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UN1714 |
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Packaging Group 1 (great danger) |
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- |
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zinc phosphide |
|
|
phosphure de zinc |
|
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Zinkphosphid |
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- |
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zinco (fosfuro di) |
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- |
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- |
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- |
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- |
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- |
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zinkfosfide |
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- |
| Record last updated: |
30/10/2025 |
| Contact: |
aeru@herts.ac.uk |
| Please cite as: |
Lewis, K.A., Tzilivakis, J., Warner, D. and Green, A. (2016) An international database for pesticide risk assessments and management. Human and Ecological Risk Assessment: An International Journal, 22(4), 1050-1064. DOI: 10.1080/10807039.2015.1133242 |