| Myristyl alcohol |

Last updated: 23/10/2025
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(Also known as: n-tetradecyl alcohol; 1-tetradecanol; 1-hydroxytetradecane ; Straight Chain Lepidopteran Pheromone; SCLP; Codling moth pheromone; Hickory shuchworm pheromone; Oblique-banded leafroller pheromone) |
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 volatile substance that is a Straight Chain Lepidoteran Pheromone (SCLP) that is a common component of many biopesticide insect attractant |
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Various Lepidoptera insects including the codling moth (Cydia pomonella), pandemis leafroller (Pandemis pyrusana) and the fruit tree leafroller (Archips argyrospilus) |
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Top fruit; Stone fruit; Tree nuts |
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- |
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| EC Regulation 1107/2009 (repealing 91/414) |
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Approved |
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Italy/France |
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30/08/2037 |
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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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✓ |
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✓ |
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LVLatvia |
MTMalta |
NLNetherlands |
PLPoland |
PTPortugal |
RORomania |
SESweden |
SISlovenia |
SKSlovakia |
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✓ |
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ISIceland |
NONorway |
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Myristyl alcohol, also known as 1-tetradecanol, primarily exhibits chain isomerism and positional isomerism. As a saturated fatty alcohol its straight-chain form is the most common and naturally occurring. However, isomeric forms can arise when the hydroxyl group is attached to different carbon atoms along the chain, leading to positional isomers like 2-tetradecanol or 4-tetradecanol. Additionally, branched-chain isomers can be formed by rearranging the carbon skeleton, such as introducing methyl branches at various positions. |
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C₁₄H₃₀O |
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CCCCCCCCCCCCCCO |
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No data |
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HLZKNKRTKFSKGZ-UHFFFAOYSA-N |
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InChI=1S/C14H30O/c1-2-3-4-5-6-7-8-9-10-11-12-13-14-15/h15H,2-14H2,1H3 |
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Yes |
| Cambridge Crystallographic Data Centre diagrams |
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| Common Name |
Relationship |
Link |
| myristyl alcohol |
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Insecticide; Semiochemical; Other substance |
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Surfactant; Foaming agent; Stabiliser |
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Pheromone |
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>95% |
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- |
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Natural |
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Functions as an insect attractant |
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A sex pheromone component of several Lepidoptera species including the codling moth (Cydia pomonella). It also derived from various vegetable oils including palm kernel oil and coconut oil |
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Crop protection |
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Various Lepidoptera insects including the codling moth (Cydia pomonella), pandemis leafroller (Pandemis pyrusana) and the fruit tree leafroller (Archips argyrospilus) |
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Top fruit; Stone fruit; Tree nuts |
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Suitable for use in all farming systems where approved for use in that country |
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112-72-1 |
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204-000-3 |
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856 |
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001510 |
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- |
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214.39 |
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- |
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tetradecan-1-ol |
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1-tetradecyl alcohol |
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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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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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Not known |
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Not applicable |
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- |
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White crystalline solid |
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Current |
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- |
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- Isomate C Plus
- Mystrial alcohol
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Usually supplied in slow release formulations as a component of the pheromone product |
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Synthesised for commerical use by the hydrogenation of myristyl acid in the presence of a catalyst |
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While exact CO₂e values are not published for specific pheromones, some general information is available. The PHERA reported that biotechnological production (e.g. yeast fermentation) of pheromones can reduce GHG emissions by up to 90% compared to traditional chemical synthesis and GHG emissions are typically in the 5 to 10 kg CO₂e per kg of pheromone produced. Other sources suggest that small scale pheromone synthesis typically has emissions in the range 1 – 3 kg CO₂e per kg of pheromone produced. |
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0.71 |
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Low |
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Miscible |
Methanol |
- |
| Miscible |
n-Hexane |
- |
| Miscible |
Acetone |
- |
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39 |
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- |
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289 |
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- |
- |
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110 |
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5.62 X 1005 |
Calculated |
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5.75 |
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High |
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0.824 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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33.0 |
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Highly volatile. If applied directly to plants or soil, drift is a concern & mitigation is advisable |
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10.0 |
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Moderately volatile |
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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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> 5000 |
Rat |
Low |
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> 2050 |
Unknown species |
Low |
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> 1000 |
Q2 Q = Miscellaneous data from online sources 2 = Unverified data of unknown source Expert judgement |
Low |
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> 85.0 |
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Moderate |
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> 0.685 |
Brachydanio rerio |
Moderate |
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0.3 |
Daphnia magna |
Moderate |
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- |
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- |
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0.074 |
Desmodesmus subspicatus |
Moderate |
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| Regulatory Threshold Levels (RTLs) |
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Note: These RTLs have been calculated using the regulatory approach used in the European Union and based on ecotoxocity values in the PPDB.
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500 |
Worst case of acute and chronic mammals |
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205 |
Worst case of acute and chronic birds |
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200 |
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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1.7 |
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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No data |
No data for temperate acute and chronic fish |
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0.003 |
Worst case of temperate acute and chronic aquatic invertebrates |
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0.0074 |
Worst case of free-floating plants, rooted plants, acute and chronic algae |
| HUMAN HEALTH AND PROTECTION |
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Low (class I) |
- |
- |
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> 5000 |
Rat |
Low |
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- |
- |
- |
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- |
- |
- |
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> 2000 |
Rat |
- |
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> 5.0 |
Rat 4 hr (whole body) |
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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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Negligible risk for proposed uses |
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Negligible risk for proposed uses |
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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 ; E3 E = Unspecified genotoxicity type (miscellaneous data source) 3 = Negative |
XNo, known not to cause a problem |
| 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 |
XNo, known not to cause a problem |
?Possibly, status not identified |
?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 oxisiding |
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Health: H319 Environment: H400, H410 |
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Not listed (Not listed) |
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Not regulated |
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myristyl alcohol |
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tetradecanol |
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| 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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