| Fatty acids (generic C7-C18) |

Last updated: 24/02/2026
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(Also known as: nonaoic; soap) |
| A naturally occurring soap insecticide and acaricide used to control soft-bodied pests but which also has other applications in crop protection. It has a low water solubility and is quite volatile. It is not persistent in water systems. There are no major concerns regarding its impact on human health having a low oral toxicity but may irritate skin and eyes. Risks to biodiversity are also considered low to moderate.. |
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 soap concentrate insecticide and acaricide used to control soft-bodied pests. Also used as an additive in formulations and as an adjuvant |
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Aphids; Mealybugs; Thrips |
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Vegetables; Fruit; Ornamentals |
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- |
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- |
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- |
| EC Regulation 1107/2009 (repealing 91/414) |
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Approved (as potassium salts) |
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Greece/Austria |
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01/12/2026 |
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No |
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Yes |
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ATAustria |
BEBelgium |
BGBulgaria |
CYCyprus |
CZCzech Republic |
DEGermany |
DKDenmark |
EEEstonia |
ELGreece |
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ESSpain |
FIFinland |
FRFrance |
HRCroatia |
HUHungary |
IEIreland |
ITItaly |
LTLithuania |
LULuxembourg |
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LVLatvia |
MTMalta |
NLNetherlands |
PLPoland |
PTPortugal |
RORomania |
SESweden |
SISlovenia |
SKSlovakia |
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ISIceland |
NONorway |
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Fatty acids are isomeric compounds, existing in multiple structural forms that arise through variations in the position of double bonds (positional isomers), the spatial arrangement around those bonds (geometric isomers such as cis and trans), and branching along the carbon chain. Natural fatty acids are typically found in the cis form, while trans isomers are often produced through industrial processing. |
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C₇H₁₄O₂ to C₁₈H₃₄O₂ |
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- |
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- |
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- |
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- |
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Yes |
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Insecticide; Fungicide; Other substance |
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Surfactant; Adjuvant |
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Plant-derived substance; Animal-derived substance |
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- |
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- |
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Natural |
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Contact action. Fatty acids disrupt the cell membranes of insects causing them to dehydrate and die |
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Naturally occurring substance, extracted from plant and animal sources. It is also a major constituent of azadirachtin |
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“Fatty acids” in the context of crop protection refers to a mixture of naturally derived saturated and unsaturated C7–C18 fatty acids, typically obtained from plant oils (often coconut, palm, or tall oil sources) of an unknown or variable composition. Major components (usually 70–95% of total) include lauric acid, myristic acid, palmitic acid, stearic acid, oleic acid and linoleic acid. |
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Crop protection |
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Soft-bodied insects such as aphids, thrips, scale insects and leafhoppers |
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Vegetables; Fruit; Ornamentals |
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Suitable for use in all farming systems where approved for use in that country |
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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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889 |
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Variable |
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- |
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Fatty acids (C7 to C18) |
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Nonanoic acids |
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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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- |
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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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Colourless solid to liquid material depending on chemical composition. Composition is a complex mic of palmitic acid (~45%), oleic acid (~20%) plus arachidic acid, stearic acid, linoleic acid and other substances. |
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Current |
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1947, first registration of soaps as pesticides in US; 2021, EU approval expired |
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- Amvac Chemical Corporation
- Koppert Biological Systems, NL
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- Savona
- Hinder Mammal Repellant
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Often supplied as a soluble concentrate which is mixed with water and applied as a foliar spray |
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Fatty acids for agricultural use are commercially produced through both plant-based extraction and microbial fermentation. Traditionally, they are derived from vegetable oils which undergo hydrolysis or transesterification to release free fatty acids or convert them into derivatives like fatty acid methyl esters. More recently, oleaginous microorganisms, including fungi, algae, and engineered cyanobacteria, have emerged as sustainable platforms for fatty acid production. These microbes are cultivated in bioreactors using nutrient-rich media, and they accumulate lipids intracellularly, which are then extracted using solvents or mechanical disruption. Advances in metabolic engineering have further optimised these systems to produce tailored fatty acid profiles for use in biostimulants, bioherbicides, and soil conditioners. |
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The GHG emissions from producing fatty acids for agricultural use can vary significantly depending on the source material and processing method. For example, Palm oil as the source emits high GHG emissions due to deforestation and land-use change, potentially up to 8–20 tonnes CO₂ per tonne of oil processed depending on practices. Whereas, soybean oil emits slightly less than palm oil but still significant, at 2–4 tonnes CO₂e per tonne. Extraction from canola oil, which is often considered more sustainable, has emissions closer to 1.5–3 tonnes CO₂e per tonne. In addition, there are emissions from fractionation and purification These steps add 0.5–1.5 tonnes CO₂e per tonne depending on energy sources and technology. Combining data, the total GHG emissions for fatty acid production typically range from 2 to 6 tonnes CO₂e per tonne of fatty acids, with palm-based sources at the higher end. |
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0.012 |
at 25 °C |
Low |
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250000 |
n-Heptane |
- |
| 250000 |
p-Xylene |
- |
| 250000 |
1,2-Dichloroethane |
- |
| 250000 |
Acetone |
- |
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12 |
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- |
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80 |
E3 E = Manufacturers safety data sheets 3 = Unverified data of known source |
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350 |
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- |
- |
- |
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4.37 X 1007 |
Calculated |
- |
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7.64 |
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High |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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4.9 |
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| - |
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900 |
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Highly volatile. If applied directly to plants or soil, drift is a concern & mitigation is advisable |
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0.33 |
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Moderately volatile |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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34.6 |
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- |
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3 |
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Non-persistent |
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3 |
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Non-persistent |
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- |
- |
- |
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9 |
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Non-persistent |
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- |
- |
- |
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- |
- |
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EU Dossier |
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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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Moderately mobile |
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137 |
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estimated |
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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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> 2510 |
Anas platyrhynchos |
Low |
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- |
- |
- |
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- |
- |
- |
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> 105 |
Eisenia foetida corr |
Moderate |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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- |
- |
- |
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~ 10000 |
Brassica oleracea Allium cepa |
- |
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- |
- |
- |
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> 100 |
Apis mellifera |
Low |
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> 96.04 |
Apis mellifera |
Moderate |
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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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3900 |
Aphidius rhopalosiphi as pelargonic acid |
Low |
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3900 |
Typhlodromus pyri as pelargonic acid |
Low |
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31740 |
Poecilus cupreus as pelargonic acid |
Low |
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- |
- |
- |
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- |
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- |
- |
- |
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- |
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8.8 |
Salmo gairdneri |
Moderate |
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5.0 |
Oncorhynchus mykiss |
Moderate |
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- |
- |
- |
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> 1.2 |
Daphnia magna |
Moderate |
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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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3.8 |
Desmodesmus subspicatus |
Moderate |
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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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251 |
Worst case of acute and chronic birds |
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21 |
Worst case of acute and chronic earthworms |
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2000 |
Worst case of non-target plants vegetative vigour and seedling emergence |
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1.9208 |
Worst case of contact and oral honeybees |
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1950 |
Worst case of parasitic wasps and predatory mites |
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0.088 |
Worst case of temperate acute and chronic fish |
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0.012 |
Worst case of temperate acute and chronic aquatic invertebrates |
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0.38 |
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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> 1.82 |
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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- |
- |
- |
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- |
- |
- |
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- |
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- |
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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 |
XNo, known not to cause a problem |
| Reproduction / development effects |
Acetyl cholinesterase inhibitor |
Neurotoxicant |
| No data found |
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 |
?Possibly, status not identified |
| Eye irritant |
Phototoxicant |
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✓Yes, known to cause a problem |
No data found |
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No further information available |
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Not explosive or oxidising Corrosive Not explected to auto-ignite, Not highly flammable |
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Health: H315, H319, H335 Environment: H411 |
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Not listed (Not listed) |
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fatty acids (generic C7-C18) |
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acides gras |
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Fettsäuren |
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fedtsyrer |
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acidi grassi |
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acido graso |
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- |
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kwasy tluszczowe |
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- |
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- |
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- |
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- |
| Record last updated: |
24/02/2026 |
| 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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