| Sulphur (Ref: SAN 7116) |

Last updated: 25/02/2026
|
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(Also known as: sulfur; BAS 1750F; brimstone; elemental sulphur; elemental sulfur) |
| Sulphur is a general purpose fungicide. It has a low aqueous solubility and is not considered to be highly volatile. It may be persistent in soil but as a naturally occurring substance is unlikely to cause significant environmental problems. It is highly toxic to aquatic systems but tends to have a low toxicity to most other species. Sulphur has a low mammalian toxicity if ingested and, may be a respiratory and skin irritant. |
The following Pesticide Hazard Tricolour (PHT) 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. The alerts for Highly Hazardous Pesticides (HHPs) are based on applying the FAO/WHO (Type 1) and the PAN (Type II) criteria to PPDB data. Further details on the HHP indicators are given in the tables below. Neither the PHT nor the HHP hazard alerts take account of usage patterns or exposure, thus they do not represent risk.
| PHT: Environmental fate |
PHT: Ecotoxicity |
PHT: Human health |
Highly Hazardous Pesticide |
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A general use fungicide, foliar feed and acaricide widely used on many different crops |
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Scab; Powdery mildew; Brown rot; Leafspot; Gall mites; Spider mites |
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Fruit including apples, pears, gooseberries, grapes, peaches, strawberries, melons; Cereals; Hops; Beans; Carrots; Lucerne; Tomatoes; Peanuts; Ornamentals including roses |
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Sulphur has been used in agriculture and viticulture for a considerable length of time, globally. |
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- |
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- |
| EC Regulation 1107/2009 (repealing 91/414) |
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Approved |
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France/Slovenia |
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31/07/2026 |
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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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USA; Australia; Morocco; Japan |
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None |
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S |
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S |
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- |
|
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NINIDFKCEFEMDL-UHFFFAOYSA-N |
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InChI=1S/S |
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Yes |
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Fungicide; Acaricide; Other substance |
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Foliar feed |
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Inorganic compound |
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990 g kg⁻¹ |
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EU dossier - Mercury < 0.1 mg kg⁻¹; Arsenic < 0.1 mg kg⁻¹; Cadmium < 0.1 mg kg⁻¹; Lead < 0.9 mg kg⁻¹; Nickel < 1.2 mg kg⁻¹ |
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Natural |
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Broad-spectrum with contact and vapour action with protectant properties. Multi-site activity. |
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Abundant naturally |
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Crop protection |
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Scab; Powdery mildew; Brown rot; Leafspot; Gall mites; Spider mites |
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Fruit including apples, pears, gooseberries, grapes, peaches, strawberries, melons; Cereals; Hops; Beans; Carrots; Lucerne; Tomatoes; Peanuts; Ornamentals including roses |
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- |
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7704-34-9 |
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231-722-6 |
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18 |
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077501 |
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5362487 |
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016-094-00-1 |
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32.064 |
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sulphur |
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sulphur |
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|
sulphur |
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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 [ 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) ; R11 Rule 11: Pesticide active ingredients that are environmentally persistent (where sediment phase only DT₅₀ => 90 days or water phase only DT₅₀ => 90 days or DT₅₀ (field) => 60 days (note lab values are used when field values are not available)) ] |
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EU Low-risk active substance |
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Not applicable |
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Not applicable |
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UN |
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M02 |
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- |
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Yellow crystalline powder |
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Current |
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150 A.D., first recorded use as a fungicide; Circa 1850s, common use in Europe |
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- BASF
- Headland
- Nufarm UK
- Syngenta AG
- Albaugh Asia Pacific Ltd
- Amaroc
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- Kumulus DF
- Thiovit Jet
- Microthiol Disperss
- Albaugh Versado
- Azumo MG
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Often supplied as water dispersable granules or soluble concentrates that are mixed with water for use as a foliar spray |
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There are three main methods used for the commercial production of agricultural sulphur. (1) mining native sulphur using the Frasch process, (2) recovering sulphur from petroleum and natural gas refining, and (3) extracting it from open-pit surface deposits. The Frasch process is especially notable—it uses superheated water and compressed air to melt underground sulphur deposits and bring the molten sulphur to the surface, where it solidifies upon cooling. Sulphur recovered from oil and gas streams is also highly pure and widely used. |
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Precise life cycle emissions are unpublished and will vary with the production method. For example, the Frasch process involves superheating water and using compressed air which will consume significant energy. Audsley et al. (2009) reported that it takes 3.7 MJ of energy per kg produced but does not specify a production method. This is equivalent to approximately 0.26 kg CO₂e. There will also be emissions associated with packaging, transport and application. |
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0.063 |
|
Low |
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1800 |
n-Heptane |
- |
| 15700 |
Toluene |
- |
| 11000 |
Dichloromethane |
- |
| 480 |
Acetone |
- |
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115.8 |
|
- |
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444.6 |
|
- |
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Decomposes on boiling |
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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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2.36 |
L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
- |
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Not applicable |
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- |
| No dissociation |
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0.098 |
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Low volatility |
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0.05 |
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Non-volatile |
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- |
- |
- |
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- |
- |
- |
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220nm = 1451, 264nm = 805, 300nm = 400 |
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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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Sulphur is a naturally occurring element and will not degrade. |
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- |
- |
- |
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- |
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- |
- |
- |
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- |
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0.2 |
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Fast |
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- |
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1000 |
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Very persistent |
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Not a main degradation route |
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Stable |
S2 S = Expert judgement 2 = Unverified data of unknown source |
Stable |
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250 |
S2 S = Expert judgement 2 = Unverified data of unknown source |
Stable |
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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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- |
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Slightly mobile |
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1950 |
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Calculated |
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- |
- |
- |
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- |
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- |
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- |
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- |
None
| Terrestrial ecotoxicology |
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> 2000 |
Rat |
Low |
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- |
- |
- |
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- |
- |
- |
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> 2000 |
Colinus virginianus |
Low |
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> 1335 |
Colinus virginianus |
- |
|
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- |
- |
- |
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> 2000 |
Eisenia foetida |
Low |
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> 1000 |
Eisenia foetida |
Low |
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- |
- |
- |
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|
- |
- |
- |
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142.6 |
Folsomia candida |
- |
|
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> 25200 |
Zea mays Avena sativa Allica cepa |
- |
|
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- |
- |
- |
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> 100 |
Apis mellifera |
Low |
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> 106.8 |
Apis mellifera |
Low |
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- |
- |
- |
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> 149.3 |
Apis mellifera |
- |
|
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- |
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- |
- |
- |
| - |
|
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- |
- |
- |
| - |
|
|
|
- |
- |
- |
|
|
- |
- |
- |
|
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|
- |
- |
- |
|
|
- |
|
|
|
- |
- |
- |
|
|
- |
|
|
- |
- |
- |
|
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- |
- |
- |
|
|
10000 |
Aphidius rhopalosiphi |
Low |
|
|
10340 |
Typhlodromus pyri |
Low |
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> 8000 |
Poecilus cupreus |
Low |
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- |
- |
- |
|
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- |
|
- |
- |
- |
|
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- |
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> 0.063 |
Oncorhynchus mykiss solubility limited |
High |
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> 0.063 |
Oncorhynchus mykiss |
Moderate |
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- |
- |
- |
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> 0.063 |
Daphnia magna solubility limited |
High |
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- |
- |
- |
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- |
- |
- |
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> 646 |
Americamysis bahia |
Low |
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- |
- |
- |
|
|
- |
- |
- |
|
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- |
- |
- |
|
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- |
- |
- |
|
|
- |
- |
- |
|
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> 0.063 |
Raphidocelis subcapitata |
Moderate |
|
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- |
- |
- |
|
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|
- |
- |
- |
|
- |
- |
- |
|
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- |
- |
- |
| Regulatory Threshold Levels (RTLs) used to calculate Total Applied Toxicity (TAT) |
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200 |
Worst case of acute and chronic mammals |
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200 |
Worst case of acute and chronic birds |
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200 |
Worst case of acute and chronic earthworms |
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5040 |
Worst case of non-target plants vegetative vigour and seedling emergence |
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2 |
Worst case of contact and oral honeybees |
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5000 |
Worst case of parasitic wasps and predatory mites |
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0.00063 |
Worst case of temperate acute and chronic fish |
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0.00063 |
Worst case of temperate acute and chronic aquatic invertebrates |
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0.0063 |
Worst case of free-floating plants, rooted plants, acute and chronic algae |
| HUMAN HEALTH AND PROTECTION |
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High (class III) |
- |
- |
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> 2000 |
Rat |
Low |
|
|
- |
- |
- |
|
|
- |
- |
- |
|
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> 2000 |
Rat |
- |
|
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> 5.43 |
Rat 4 hr (nose only) |
- |
|
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- |
- |
- |
|
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None allocated |
|
- |
|
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None allocated |
|
- |
|
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- |
- |
- |
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None allocated |
|
- |
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10 |
default |
- |
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- |
- |
- |
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Negligible risk to bystanders |
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No unacceptable risks to operators or other farm workers forseen |
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- |
- |
- |
|
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| Carcinogen |
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Endocrine disruptor |
XNo, known not to cause a problem |
A0 A = Chromosome aberration (EFSA database) 0 = No data ; 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 ; E0 E = Unspecified genotoxicity type (miscellaneous data source) 0 = No data |
No data found |
| Reproduction / development effects |
Acetyl cholinesterase inhibitor |
Neurotoxicant |
XNo, known not to cause a problem |
XNo, known not to cause a problem |
XNo, known not to cause a problem |
| Respiratory tract irritant |
Skin irritant |
Skin sensitiser |
✓Yes, known to cause a problem |
✓Yes, known to cause a problem |
XNo, known not to cause a problem |
| Eye irritant |
Phototoxicant |
  |
✓Yes, known to cause a problem |
XNo, known not to cause a problem |
  |
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Excessive use linked to reduced lung function and increased asthma-related symptoms |
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Not expected to auto-ignite; Flammable Not explosive Exhibits oxidising properties IMDG Transport Hazard Class 4.1 Flammable solid |
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Health: H335, H319, H315 |
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III (Slightly hazardous) |
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UN1350 |
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Packaging Group III (minor danger) |
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Stable under standard ambient conditions |
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|
sulphur |
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|
soufre |
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Schwefel |
|
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svovl |
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|
zolfo |
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azufre |
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- |
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siarka |
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svavel |
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|
ken |
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|
zwavel |
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|
svovel |
| Record last updated: |
25/02/2026 |
| 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 |
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