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Beta-thujone
Last updated: 22/02/2026
(Also known as: (+)-thujone; (+)-beta-thujone; 3-isothujone)

Hazard alerts

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
   
Human health
High alert:
Acetyl cholinesterase inhibitor; Neurotoxicant
 
GENERAL INFORMATION
Description
A botanical substance, common in some plant essential oils and which exhibits insecticidal activity
Example pests controlled
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
Example applications
Potatoes; Tomatoes; Vegetables; Stored produce
Efficacy & activity
-
Appearance and life cycle
-
Taxonomic classification
-
GB regulatory status
GB COPR regulatory status
Not approved
Date COPR inclusion expires
Not applicable
GB LERAP status
No UK approval for use as a pest management agent
EC Regulation 1107/2009 (repealing 91/414)
EC Regulation 1107/2009 status
Not approved
Dossier rapporteur/co-rapporteur
Not applicable
Date EC 1107/2009 inclusion expires
Not applicable
EU Candidate for substitution (CfS)
Not applicable
Listed in EU database
No
Approved for use (✓) under EC 1107/2009 in the following EU Member States
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
                 
Approved for use (✓) under EC 1107/2009 by Mutual Recognition of Authorisation and/or national regulations in the following EEA countries
ISIceland
NONorway
                 
Additional information
Also used in
-
Chemical structure
Isomerism
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.
Chemical formula
C₁₀H₁₆O
Canonical SMILES
C[C@H]1[C@H]2C[C@]2(CC1=O)C(C)C
Isomeric SMILES
-
International Chemical Identifier key (InChIKey)
USMNOWBWPHYOEA-XKSSXDPKSA-N
International Chemical Identifier (InChI)
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
2D structure diagram/image available?
Yes
General status
Biopesticide type
Insecticide; Repellent; Other substance
Other bioactivity & uses
Fragrance
Substance groups
Plant derived substance; Monoterpene ketone
Minimum active substance purity
-
Known relevant impurities
-
Substance origin
Natural
Mode of action
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.
Substance source
Commonly found in various plant essential oils, particularly those of the Artemisia, Salvia and Thuja species
Uses
Crop protection
Target pests
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
Target host
Potatoes; Tomatoes; Vegetables; Stored produce
Farming system suitability
-
CAS RN
471‑15‑8
EC number
620-564-7
CIPAC number
-
US EPA chemical code
-
PubChem CID
91456
Molecular mass
152.23
PIN (Preferred Identification Name)
-
IUPAC name
(1S,4S,5R)-4‑methyl‑1‑propan‑2‑ylbicyclo[3.1.0]hexan‑3‑one
CAS name
-
Global Governance status: Listed (✓) under
UK Poisons List Order 1972 Rotterdam Convention Montreal Protocol
Stockholm Convention OSPAR EU Water Framework Directive
Relevant Environmental Water Quality Standards
-
Forever chemical
-
Highly Hazardous Pesticide (HHP)
Type I
-
Type II
-
Other status information
-
Herbicide Resistance Class (HRAC MoA class)
Not applicable
Herbicide Resistance Class (WSSA MoA class)
Not applicable
Insecticide Resistance Class (IRAC MoA class)
Not applicable
Fungicide Resistance Class (FRAC MOA class)
Not applicable
Examples of recorded resistance
-
Physical state
Colourless to pale yellow liquid
Commercial
Property
Value
Availability status
Current
Introduction & key dates
-
Example manufacturers & suppliers of products using this active now or historically
  • Not produced specifically as a biopesticide
Example products using this active
-
Formulation and application details
-
Commercial production
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.
Impact on climate of production and use
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.
ENVIRONMENTAL FATE
Property
Value
Source; quality score; and other information
Interpretation
Solubility - In water at 20 °C at pH 7 (mg l⁻¹)
407
Q3 Q = Miscellaneous data from online sources
3 = Unverified data of known source
at 25 °C
Moderate
Solubility - In organic solvents at 20 °C (mg l⁻¹)
- - -
Melting point (°C)
- - -
Boiling point (°C)
201
Q3 Q = Miscellaneous data from online sources
3 = Unverified data of known source
-
Degradation point (°C)
23
Q3 Q = Miscellaneous data from online sources
3 = Unverified data of known source
-
Flashpoint (°C)
- - -
Octanol-water partition coefficient at pH 7, 20 °C
P
4.90 X 1002 Calculated -
Log P
2.69
Q3 Q = Miscellaneous data from online sources
3 = Unverified data of known source
Low
Fat solubility of residues
Solubility
- - -
Data type
- - -
Density (g ml⁻¹)
0.925
Q3 Q = Miscellaneous data from online sources
3 = Unverified data of known source
-
Dissociation constant pKa) at 25 °C
- - -
-
Vapour pressure at 20 °C (mPa)
- - -
Henry's law constant at 25 °C (Pa m³ mol⁻¹)
- - -
Volatilisation as max % of applied dose lost
From plant surface
- - -
From soil surface
- - -
Maximum UV-vis absorption L mol⁻¹ cm⁻¹
- - -
Surface tension (mN m⁻¹)
- - -
Degradation
Property
Value
Source; quality score; and other information
Interpretation
General biodegradability
Readily biodegradable
Soil degradation (days) (aerobic)
DT₅₀ (typical)
- - -
DT₅₀ (lab at 20 °C)
- - -
DT₅₀ (field)
- - -
DT₉₀ (lab at 20 °C)
- - -
DT₉₀ (field)
- - -
DT₅₀ modelling endpoint
- - -
Note
-
Dissipation rate RL₅₀ (days) on plant matrix
Value
- - -
Note
-
Dissipation rate RL₅₀ (days) on and in plant matrix
Value
- - -
Note
-
Aqueous photolysis DT₅₀ (days) at pH 7
Value
- - -
Note
-
Aqueous hydrolysis DT₅₀ (days) at 20 °C and pH 7
Value
- - -
Note
-
Water-sediment DT₅₀ (days)
- - -
Water phase only DT₅₀ (days)
- - -
Sediment phase only DT₅₀ (days)
- - -
Air degradation
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.
Decay in stored produce DT₅₀
-
Soil adsorption and mobility
Property
Value
Source; quality score; and other information
Interpretation
Linear
Kd (mL g⁻¹)
- - -
Koc (mL g⁻¹)
-
Notes and range
-
Freundlich
Kf (mL g⁻¹)
- - -
Kfoc (mL g⁻¹)
-
1/n
-
Notes and range
-
pH sensitivity
-
Known soil and groundwater metabolites

None

Other known metabolites
Metabolite name and reference
Aliases
Formation medium / Rate
Estimated maximum occurrence fraction
- 7-hydroxy-beta-thujone Humans -
- 4-hydroxy-beta-thujone Humans -
ECOTOXICOLOGY
Terrestrial ecotoxicology
Property
Value
Source; quality score; and other information
Interpretation
Mammals - Acute oral LD₅₀ (mg kg⁻¹)
- - -
Mammals - Short Term Oral NOAEL (mg kg⁻¹ bw d⁻¹)
- - -
Mammals - Long Term (Chronic) Oral NOAEL (mg kg⁻¹ bw d⁻¹)
11
Q3 Q = Miscellaneous data from online sources
3 = Unverified data of known source
Rat NOAEL
Moderate
Birds - Acute LD₅₀ (mg kg⁻¹)
- - -
Birds - Short term dietary LC₅₀ (mg kg⁻¹ bw d⁻¹)
- - -
Birds - Chronic 21d NOEL (mg kg⁻¹ bw d⁻¹)
- - -
Earthworms - Acute 14 day LC₅₀ (mg kg⁻¹ dw soil)
- - -
Earthworms - Chronic NOEC, reproduction (mg kg⁻¹ dw soil)
- - -
Soil micro-organisms
- - -
Collembola
Acute LC₅₀ (mg kg⁻¹)
- - -
Chronic NOEC (mg kg⁻¹)
- - -
Non-target plants
Vegetative vigour ER₅₀ (g ha⁻¹)
- - -
Seedling emergence ER₅₀ (g ha⁻¹)
- - -
Honeybees (Apis spp.)
Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
Unknown mode acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
Chronic
- - -
Notes
-
Bumblebees (Bombus spp.)
Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
-
Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
-
Mason bees (Osmia spp.)
Contact acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
Oral acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg bee⁻¹)
- - -
Other bee species (1)
Acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg insect⁻¹)
- - -
Mode of exposure
-
Other bee species (2)
Acute LD₅₀ (worst case from 24, 48 and 72 hour values - μg insect⁻¹)
- - -
Mode of exposure
-
Beneficial insects (Ladybirds)
- - -
Beneficial insects (Lacewings)
- - -
Beneficial insects (Parasitic wasps)
- - -
Beneficial insects (Predatory mites)
- - -
Beneficial insects (Ground beetles)
- - -
Beneficial insects (Butterflies)
Contact
- - -
Notes
-
Oral
- - -
Notes
-
Aquatic ecotoxicology
Property
Value
Source; quality score; and other information
Interpretation
Temperate Freshwater Fish - Acute 96 hour LC₅₀ (mg l⁻¹)
- - -
Temperate Freshwater Fish - Chronic 21 day NOEC (mg l⁻¹)
- - -
Tropical Freshwater Fish - Acute 96 hour LC₅₀ (mg l⁻¹)
- - -
Temperate Freshwater Aquatic invertebrates - Acute 48 hour EC₅₀ (mg l⁻¹)
- - -
Temperate Freshwater Aquatic invertebrates - Chronic 21 day NOEC (mg l⁻¹)
- - -
Tropical Freshwater Aquatic invertebrates - Acute 48 hour EC₅₀ (mg l⁻¹)
- - -
Aquatic crustaceans - Acute 96 hour LC₅₀ (mg l⁻¹)
- - -
Sediment dwelling organisms - Acute 96 hour LC₅₀ (mg l⁻¹)
- - -
Sediment dwelling organisms - Chronic 28 day NOEC, static, water (mg l⁻¹)
- - -
Sediment dwelling organisms - Chronic 28 day NOEC, sediment (mg kg⁻¹)
- - -
Aquatic Plants (free-floating, fonds growth, fresh) - 7 day (mg l⁻¹)
- - -
Aquatic plants (rooted, growth rate, fresh) - 14 day (mg l⁻¹)
- - -
Algae - Acute (growth rate, fresh; mg l⁻¹)
- - -
Algae - Chronic (growth rate, fresh; mg l⁻¹)
- - -
Mesocosm study data
NOEAEC mg l⁻¹
- - -
NOEAEC mg l⁻¹
- - -
Marine bivalves
- - -
Regulatory Threshold Levels (RTLs)

Note: These RTLs have been calculated using the regulatory approach used in the European Union and based on ecotoxocity values in the PPDB.

Species group
RTL
Notes
Mammals
2.2 Worst case of acute and chronic mammals
Birds
No data No data for acute and chronic birds
Soil organisms
No data No data for acute and chronic earthworms
Terrestrial plants
No data No data for non-target plants vegetative vigour and seedling emergence
Pollinators
No data No data for contact and oral honeybees
Arthropods
No data No data for parasitic wasps and predatory mites
Fish
No data No data for temperate acute and chronic fish
Aquatic invertebrates
No data No data for temperate acute and chronic aquatic invertebrates
Aquatic plants
No data No data for free-floating plants, rooted plants, acute and chronic algae
HUMAN HEALTH AND PROTECTION
General
Property
Value
Source; quality score; and other information
Interpretation
Threshold of Toxicological Concern (Cramer Class)
- - -
Mammals - Acute oral LD₅₀ (mg kg⁻¹)
- - -
Mammals - Short Term Oral NOAEL (mg kg⁻¹ bw d⁻¹)
- - -
Mammals - Long Term (Chronic) Oral NOAEL (mg kg⁻¹ bw d⁻¹)
11
Q3 Q = Miscellaneous data from online sources
3 = Unverified data of known source
Rat NOAEL
Moderate
Mammals - Dermal LD₅₀ (mg kg⁻¹ body weight)
- - -
Mammals - Inhalation LC₅₀ (mg l⁻¹)
- - -
Other Mammal toxicity endpoints
Intraperitoneal LD₅₀ = 45.0 mg kg⁻¹
Q3 Q = Miscellaneous data from online sources
3 = Unverified data of known source
Mouse
-
Subcutaneous LD₅₀ = 442 mg kg⁻¹
F3 F = U.S. EPA ECOTOX database / U.S. EPA pesticide fate database / Miscellaneous WHO documents / FAO data, IPCS INCHEM data (US EPA Databases Related to Pesticide Risk Assessment )
3 = Unverified data of known source
Mouse
-
ADI - Acceptable Daily Intake (mg kg⁻¹ bw day⁻¹)
- - -
ARfD - Acute Reference Dose (mg kg⁻¹ bw day⁻¹)
- - -
AAOEL - Acute Acceptable Operator Exposure Level (mg kg⁻¹ bw day⁻¹)
- - -
AOEL - Acceptable Operator Exposure Level - Systemic (mg kg⁻¹ bw day⁻¹)
- - -
Dermal penetration studies (%)
- - -
Dangerous Substances Directive 76/464
- - -
Exposure Routes
Public
-
Occupational
-
Mammalian dose elimination route and rate
- - -
Health issues
Specific human health issues (hazard-based)
Carcinogen
Genotoxic
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  
XNo, known not to cause a problem
No data found  
General human health issues
No information available
Handling issues
Property
Value and interpretation
General
No information available
CLP classification 2013
Health: H302
WHO Classification
-
UN Number
-
Waste disposal & packaging
-
Shelf-life, storage, stability and reactivity
-
TRANSLATIONS
Language
Name
English
beta-thujone
French
-
German
-
Danish
-
Italian
-
Spanish
-
Greek
-
Polish
-
Swedish
-
Hungarian
-
Dutch
-
Norwegian
-

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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