| Rapeseed oil |

Last updated: 23/10/2025
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(Also known as: Rape oil; Brassica campestris oil; Colza oil; Refined Rubol; Canola oil; Vegetable oil; Field mustard oil; Plant oil) |
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 plant derived oil used for the control of a range of sucking and chewing insects |
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Mites, Spider mites, Mealybugs, Product performance |
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Ornamentals; Glasshouse crops; Fruit including appls, pears |
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- |
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- |
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Class: Magnoliopsida; Order: Brassicales; Family: Brassicaceae |
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Approved |
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31/08/2029 |
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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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Netherlands/France |
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31/03/2026 |
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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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Insecticide; Acaricide; Other substance |
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Synergist |
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Plant-derived substance; Plant oil |
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- |
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EU dossier: Erucic acid <2% |
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Natural; Complex mixture |
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Non-toxic - repels insects and acts via suffocation |
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Plant oil extracted from rapeseed (Brassica napus) |
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Crop protection |
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Sucking insects such as mites and mealybugs |
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Top and stone fruit; Ornamentals |
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- |
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8002-13-9 |
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232-299-0 |
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- |
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- |
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- |
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- |
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rapeseed oil |
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- |
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- |
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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 [ R12 Rule 12: Pesticide active ingredients that are bioaccumulative (where bio-concentration factor (BCF) > 2000 l kg⁻¹ (if BCF is not available, where Log P >=5)) ] |
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- |
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Not applicable |
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Not applicable |
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UNE |
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Not applicable |
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- |
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Pale yellow oil comprised of a complex mixture of botanical substances which are predominately fatty acids (>90%) |
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Current |
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1990s. approx start of informal use; 2008, registered EU |
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- Floramite 240 SC
- Codacide Oil
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Usually supplied as an emulsifiable concentrate. Apply with knapsack or handsprayer |
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Commercial production of rapeseed oil begins with harvesting the seeds of the Brassica napus plant. The seeds are cleaned and then subjected to either mechanical pressing or solvent extraction to release the oil. Cold pressing retains more nutrients but yields less oil, while solvent extraction is more efficient for large-scale production. The crude oil undergoes refining processes including degumming, neutralisation, bleaching, and deodorisation to remove impurities, improve clarity, and enhance shelf life. |
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The carbon footprint of refined rapeseed oil has been estimated at between 1.0 and 2.5 kg CO₂e per kg of oil. |
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0.001 |
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Low |
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250000 |
1,2-Dichloroethane |
- |
| 250000 |
p-Xylene |
- |
| 250000 |
Ethyl acetate |
- |
| 10000 |
Methanol |
- |
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-29.5 |
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- |
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>412 |
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- |
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350 |
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- |
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234.4 |
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- |
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2.00 X 1023 |
Calculated |
- |
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23.3 |
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High |
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- |
- |
- |
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- |
- |
- |
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0.914 |
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- |
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Does not dissociate |
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- |
| - |
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6.2 X 10-04 |
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Low volatility |
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1.49 X 10-10 |
for Triolein at 20 °C |
Non-volatile |
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- |
- |
- |
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- |
- |
- |
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Maxima at 206nm |
- |
- |
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- |
- |
- |
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Readily biodegrades |
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1.02 |
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Non-persistent |
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1.02 |
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Non-persistent |
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- |
- |
- |
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4.82 |
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Non-persistent |
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- |
- |
- |
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- |
- |
- |
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EU 2020 RAR: Lab studies DT₅₀ (normalised) range 0.8-1.2 days, DT₉₀ (measured) range 4.12-5.91 days, Soils=4 |
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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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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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None
| Terrestrial ecotoxicology |
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> 2000 |
Rat |
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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3550 |
Eisenia foetida |
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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> 640 |
Apis mellifera |
Low |
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> 2572 |
Apis mellifera |
Low |
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- |
- |
- |
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1421.02 |
Apis mellifera |
- |
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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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192 |
Oncorhynchus mykiss |
Low |
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19.6 |
Danio rerio 35 day |
Low |
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- |
- |
- |
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91 |
Daphnia magna |
Moderate |
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1.34 |
Daphnia magna |
Moderate |
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- |
- |
- |
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- |
- |
- |
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47.26 |
Chironomum riparius |
Moderate |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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39.0 |
Desmodesmus subspicatus |
Low |
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- |
- |
- |
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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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No data |
No data for acute and chronic birds |
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710 |
Worst case of acute and chronic earthworms |
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No data |
No data for non-target plants vegetative vigour and seedling emergence |
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12.8 |
Worst case of contact and oral honeybees |
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No data |
No data for parasitic wasps and predatory mites |
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1.92 |
Worst case of temperate acute and chronic fish |
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0.134 |
Worst case of temperate acute and chronic aquatic invertebrates |
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3.9 |
Worst case of free-floating plants, rooted plants, acute and chronic algae |
| HUMAN HEALTH AND PROTECTION |
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Not applicable |
- |
- |
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> 2000 |
Rat |
Low |
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- |
- |
- |
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- |
- |
- |
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> 2000 |
Rat |
- |
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> 2.36 |
Rat |
- |
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- |
- |
- |
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None allocated |
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None allocated |
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- |
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- |
- |
- |
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None allocated |
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- |
- |
- |
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- |
- |
- |
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No risks identified for proposed uses |
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No risks identified for proposed uses |
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- |
- |
- |
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| Carcinogen |
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Endocrine disruptor |
| No data found |
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 |
XNo, known not to cause a problem |
| Reproduction / development effects |
Acetyl cholinesterase inhibitor |
Neurotoxicant |
| No data found |
XNo, known not to cause a problem |
No data found |
| Respiratory tract irritant |
Skin irritant |
Skin sensitiser |
XNo, known not to cause a problem |
XNo, known not to cause a problem |
XNo, known not to cause a problem |
| Eye irritant |
Phototoxicant |
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XNo, known not to cause a problem |
XNo, known not to cause a problem |
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No further information available |
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Not explosive or oxidising |
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- |
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Not listed (Not listed) |
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- |
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- |
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- |
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rapeseed oil |
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rapsolje |
| Record last updated: |
23/10/2025 |
| 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 |
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