| Codlemone (Ref: BAS 2851) |

Last updated: 23/10/2025
|
 |
(Also known as: E8E10-12OH; E,E-8,10-dodecadien-1-ol; codlelure; Codling moth pheromone; Cydia pomonella pheromone; Hickory shuckworm 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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Naturally occuring substance used for the biological control of codling moth and other insects |
|
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Codling moth (Cydia pomonella), Hickory shuckworm (Cydia caryana) |
|
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Fruit including apples, pears, peaches, plums, citrus, stone fruit; Tree nuts; Ornamentals |
|
|
- |
|
|
- |
|
|
- |
|
|
Approved |
|
|
30/08/2029 |
|
|
Not applicable |
| EC Regulation 1107/2009 (repealing 91/414) |
|
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Approved |
|
|
Not applicable |
|
|
30/08/2037 |
|
|
- |
|
|
Yes |
|
|
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 |
|   |
  |
✓ |
✓ |
✓ |
  |
✓ |
✓ |
  |
|
|
|
ISIceland |
NONorway |
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|   |
  |
  |
  |
  |
  |
  |
  |
  |
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Codlemone exhibits geometric (cis-trans) isomerism due to the presence of two double bonds in its carbon chain. |
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C₁₂H₂₂O |
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CC=CC=CCCCCCCCO |
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C/C=C/C=C/CCCCCCCO |
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CSWBSLXBXRFNST-MQQKCMAXSA-N |
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InChI=1S/C12H22O/c1-2-3-4-5-6-7-8-9-10-11-12-13/h2-5,13H,6-12H2,1H3/b3-2+,5-4+ |
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Yes |
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Semiochemical; Insecticide |
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Pheromone |
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- |
|
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- |
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Natural |
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Distrupts mating |
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Sex pheromone of the female codling moth (Cydia pomonella Linnaeus) |
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Crop protection |
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Codling moth (Cydia pomonella), Hickory shuckworm (Cydia caryana) |
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Fruit including apples, pears, peaches, plums, citrus, stone fruit; Tree nuts; Ornamentals |
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Suitable for use in all farming systems where approved for use in that country |
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33956-49-9 |
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251-761-2 |
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None allocated |
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129028 |
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- |
|
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182.31 |
|
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- |
|
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(8E,10E)-8,10-Dodecadien-1-ol |
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(E,E)-8,10-dodecadien-1-ol |
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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) ] |
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Marine pollutant |
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Not applicable |
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Not applicable |
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UNM |
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Not applicable |
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- |
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Yellow liquid or solid depending upon temperature |
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Current |
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1990, introduced |
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- BASF
- Suterra
- BioGlobal
- Hercon Environmental
|
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- RAK 3+4
- Rak 3
- Checkmate CM-F
- Isomate CTT
- Hercon Disrupt II
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Usually supplied in slow release containers that emit the phermone as a vapour. Spray formulations are also available. |
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Codlemone is produced commercially through a process called metabolic engineering. This involves genetically modifying a crop (often Camelina sativa) to produce codlemone precursors. The crop is then cultivated, harvested and seeds collecting containing the codlemone precursors. The fatty acids in the seeds are extracted and converted into the corresponding alcohols, which are the active components of codlemone. |
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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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21.2 |
|
Moderate |
|
|
1000 |
Ethyl acetate |
- |
| 1000 |
Acetone |
- |
| 1000 |
Methanol |
- |
| 1000 |
Acetone |
- |
|
|
32 |
|
- |
|
|
120 |
|
- |
|
|
- |
- |
- |
|
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135 |
|
- |
|
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2.29 X 1004 |
Calculated |
- |
|
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4.36 |
|
High |
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|
- |
- |
- |
|
|
- |
- |
- |
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0.86 |
L3 L = Pesticide manuals and hard copy reference books / other sources 3 = Unverified data of known source |
- |
|
|
- |
- |
- |
| - |
|
|
33 |
|
Highly volatile. If applied directly to plants or soil, drift is a concern & mitigation is advisable |
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0.028 |
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Non-volatile |
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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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Stable |
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Stable |
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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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- |
Q2 Q = Miscellaneous data from online sources 2 = Unverified data of unknown source |
Slightly mobile |
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3996 |
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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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> 5000 |
Rat |
Low |
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- |
- |
- |
|
|
- |
- |
- |
|
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> 2150 |
Colinus virginianus |
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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> 85 |
|
Moderate |
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- |
- |
- |
|
|
- |
- |
- |
|
|
- |
|
|
|
- |
- |
- |
| - |
|
|
- |
- |
- |
| - |
|
|
|
- |
- |
- |
|
|
- |
- |
- |
|
|
|
- |
- |
- |
|
|
- |
|
|
|
- |
- |
- |
|
|
- |
|
|
- |
- |
- |
|
|
- |
- |
- |
|
|
- |
- |
- |
|
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- |
- |
- |
|
|
- |
- |
- |
|
|
|
- |
- |
- |
|
|
- |
|
- |
- |
- |
|
|
- |
|
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> 5.67 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source Oncorhynchus mykiss |
Moderate |
|
|
- |
- |
- |
|
|
> 0.685 |
Danio rerio |
Moderate |
|
|
> 0.3 |
Daphnia magna |
Moderate |
|
|
- |
- |
- |
|
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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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215 |
Worst case of acute and chronic birds |
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No data |
No data for acute and chronic earthworms |
|
|
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 |
|
|
0.0567 |
Worst case of 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) |
- |
- |
|
|
> 5000 |
Rat |
Low |
|
|
- |
- |
- |
|
|
- |
- |
- |
|
|
> 2000 |
Rat |
- |
|
|
> 5.0 |
Rat 4 hr (whole body) |
- |
|
|
- |
- |
- |
|
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None allocated |
|
- |
|
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None allocated |
|
- |
|
|
- |
- |
- |
|
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None allocated |
|
- |
|
|
- |
- |
- |
|
|
- |
- |
- |
|
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Negligible for proposed uses |
|
|
Negligible for proposed uses |
|
|
- |
- |
- |
|
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| Carcinogen |
|
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 |
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 |
✓Yes, known to cause a problem |
?Possibly, status not identified |
| Eye irritant |
Phototoxicant |
  |
✓Yes, known to cause a problem |
No data found |
  |
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|
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Possible kidney toxicant |
|
|
|
|
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Not oxidising or explosive IMDG Transport hazard Code 9 |
|
|
Not classified as hazardous |
|
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Not listed (Not listed) |
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UN3082 |
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Packaging group III (minor danger} |
|
|
- |
|
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codlemone |
|
|
- |
|
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Codlemone |
|
|
- |
|
|
- |
|
|
- |
|
|
- |
|
|
kodlemone |
|
|
- |
|
|
- |
|
|
- |
|
|
- |
| 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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