| Beta-thujone |

Last updated: 22/02/2026
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(Also known as: (+)-thujone; (+)-beta-thujone; 3-isothujone) |
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 botanical substance, common in some plant essential oils and which exhibits insecticidal activity |
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Red fire ant (Solenopsis invicta); Aphids, particularly the peach-potato aphid (Myzus persicae); Caribbean fruit fly (Anastrepha suspensa); Mediterranean fruit fly (Ceratitis capitata); Weevils; Various beetles |
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Potatoes; Tomatoes; Vegetables; Stored produce |
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- |
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- |
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Not approved |
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Not applicable |
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No UK approval for use as a pest management agent |
| EC Regulation 1107/2009 (repealing 91/414) |
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Not approved |
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Not applicable |
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Not applicable |
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Not applicable |
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No |
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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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Beta-thujone is one of the two diastereoisomeric forms of the bicyclic monoterpene ketone thujone, naturally occurring as the (+)-beta-thujone enantiomer. It differs from its more toxic counterpart, alpha-thujone, specifically in the stereochemical configuration at the C-4 position, where the methyl group is oriented differently relative to the thujane skeleton. Alpha-thujone is defined as the (1S, 4R, 5R) isomer and beta-thujone is the (1S, 4S, 5R) diastereomer. These isomers are not mirror images but share the same connectivity, with their distinct spatial arrangements resulting in different biological activities. |
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C₁₀H₁₆O |
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C[C@H]1[C@H]2C[C@]2(CC1=O)C(C)C |
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- |
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USMNOWBWPHYOEA-XKSSXDPKSA-N |
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InChI=1S/C10H16O/c1-6(2)10-4-8(10)7(3)9(11)5-10/h6-8H,4-5H2,1-3H3/t7-,8+,10-/m0/s1 |
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Yes |
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Insecticide; Repellent; Other substance |
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Fragrance |
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Plant derived substance; Monoterpene ketone |
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- |
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Natural |
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Acts as a non-competitive blocker of the GABA-A receptor, preventing the inhibitory neurotransmitter GABA from binding. This leads to the hyper-excitation of neurons, causing muscle spasms, convulsions, and eventually insect death. GABA Receptor Antagonism. Also an antifeedant. |
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Commonly found in various plant essential oils, particularly those of the Artemisia, Salvia and Thuja species |
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Crop protection |
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Red fire ant (Solenopsis invicta); Aphids, particularly the peach-potato aphid (Myzus persicae); Caribbean fruit fly (Anastrepha suspensa); Mediterranean fruit fly (Ceratitis capitata); Weevils; Various beetles |
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Potatoes; Tomatoes; Vegetables; Stored produce |
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- |
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471‑15‑8 |
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620-564-7 |
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91456 |
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152.23 |
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- |
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(1S,4S,5R)-4‑methyl‑1‑propan‑2‑ylbicyclo[3.1.0]hexan‑3‑one |
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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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Not applicable |
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Not applicable |
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Not applicable |
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Not applicable |
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- |
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Colourless to pale yellow liquid |
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Current |
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- |
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- Not produced specifically as a biopesticide
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Beta-thujone is not produced commercially through synthetic routes on a large scale due to its natural abundance and the availability of low-cost plant sources; instead, it is primarily obtained by isolation and purification from essential oils of plants rich in the beta-isomer, most notably cedar leaf oil from Thuja occidentalis (white cedar), where it often predominates or occurs in significant proportions alongside alpha-thujone. The process typically involves steam distillation of fresh or dried cedar leaves and branchlets to yield the crude essential oil, followed by chemical separation methods such as formation of crystalline bisulphite adducts to selectively isolate the ketone fraction (thujone isomers), hydrolysis or regeneration via hydrodistillation, and further purification by fractional distillation, chromatography, or other techniques to achieve high-purity beta-thujone. In some research or small-scale contexts, microbial transformations or chemical modifications (e.g., Beckmann rearrangement for derivatives) start from isolated beta-thujone, but commercial supply for fragrance, research, or biopesticide applications relies on natural extraction. |
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Data for specific plant oils is scarce. However, from publicly available data the carbon footprint of plant oils has been estimated at between 1.0 and 4.0 kg CO₂e per kg of oil. This depends on the plant oil content, agricultural practices and processing methods used. |
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407 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source at 25 °C |
Moderate |
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201 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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23 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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4.90 X 1002 |
Calculated |
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2.69 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
Low |
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0.925 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source |
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Readily biodegradable |
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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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| Known soil and groundwater metabolites |
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None
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7-hydroxy-beta-thujone |
Humans |
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4-hydroxy-beta-thujone |
Humans |
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| Terrestrial ecotoxicology |
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11 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source Rat NOAEL |
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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2.2 |
Worst case of acute and chronic mammals |
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No data |
No data for acute and chronic birds |
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No data |
No data for 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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No data |
No data for 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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No data |
No data for temperate acute and chronic aquatic invertebrates |
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No data |
No data for free-floating plants, rooted plants, acute and chronic algae |
| HUMAN HEALTH AND PROTECTION |
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11 |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source Rat NOAEL |
Moderate |
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Intraperitoneal LD₅₀ = 45.0 mg kg⁻¹ |
Q3 Q = Miscellaneous data from online sources 3 = Unverified data of known source Mouse |
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| Subcutaneous LD₅₀ = 442 mg kg⁻¹ |
Mouse |
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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 |
No data found |
| Reproduction / development effects |
Acetyl cholinesterase inhibitor |
Neurotoxicant |
XNo, known not to cause a problem |
✓Yes, known to cause a problem |
✓Yes, known to cause a problem |
| 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 |
No data found |
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No information available |
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No information available |
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Health: H302 |
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beta-thujone |
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| Record last updated: |
22/02/2026 |
| 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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