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EC number: 218-827-2 | CAS number: 2244-16-8
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data

Endpoint summary
Administrative data
Description of key information
Acute Oral Toxicity:
In Acute oral toxicity,LD50 value for target substance d-Carvone (2244-16-8) was considered to be 3710 mg/kg bw and 3560 mg/kg bw in rats. All these studies concluded that the LD50 value is greater than 2000 mg/kg bw.Thus, comparing this value with the criteria of CLP regulation, d-Carvone (2244-16-8) cannot be classified for acute oral toxicity.
Acute Inhalation Toxicity:
In Acute inhalation toxicity, LD50 value was predicted based on OECD QSAR toolbox for target substance d-Carvone (2244-16-8) was estimated to be 22.07 mg/L in air ( 22070 mg/m3),and for differentstudies available on the structurally similar read across substance 2-Methyl-5-(1-methylethenyl)-2-cyclohexenone (99-49-0) was considered to be >5.66 mg/l in air and for Spearmint Oil (8008-79-5) was considered to be >5.43 mg/l in air. All these studies concluded that the LC50 value is greater than 5 mg/L air. Thus, comparing this value with the criteria of CLP regulation, d-Carvone (2244-16-8) cannot be classified for acute inhalation toxicity.
Acute Dermal Toxicity:
In Acute dermal toxicity, LD50 value for target substance d-Carvone (2244-16-8) was considered to be 4000 mg/kg bw; 3840 mg/kg bw and 3840 mg/kg bw in rabbits. All these studies concluded that the LD50 value is greater than 2000 mg/kg bw. Thus, comparing this value with the criteria of CLP regulation, d-Carvone (2244-16-8) cannot be classified for acute dermal toxicity.
Key value for chemical safety assessment
Acute toxicity: via oral route
Link to relevant study records
- Endpoint:
- acute toxicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Justification for type of information:
- data is from peer-reviewed journal
- Qualifier:
- according to guideline
- Guideline:
- other: as mentioned below
- Principles of method if other than guideline:
- Acute oral toxicity test was carried out to study the effects of d-Carvone (2244-16-8) on rats.
- GLP compliance:
- not specified
- Test type:
- other: no data available
- Limit test:
- no
- Specific details on test material used for the study:
- - Name of test material (as cited in study report):d-Carvone- Molecular formula :C10H14O- Molecular weight :150.22 g/mol- Substance type:organic
- Species:
- rat
- Strain:
- not specified
- Sex:
- not specified
- Details on test animals or test system and environmental conditions:
- No data available
- Route of administration:
- oral: unspecified
- Vehicle:
- not specified
- Details on oral exposure:
- No data available
- Doses:
- 3710 mg/kg bw
- No. of animals per sex per dose:
- No data available
- Control animals:
- not specified
- Details on study design:
- No data available
- Statistics:
- No data available
- Preliminary study:
- No data available
- Sex:
- not specified
- Dose descriptor:
- LD50
- Effect level:
- 3 710 mg/kg bw
- Based on:
- test mat.
- Remarks on result:
- other: 50% mortality was observed
- Mortality:
- 50% mortality was observed at dose 3710 mg/kg bw in treated rats
- Clinical signs:
- other: No data available
- Gross pathology:
- No data available
- Other findings:
- No data available
- Interpretation of results:
- other: not classified
- Conclusions:
- The lethal concentration (LD50) value for acute oral toxicity test was considered to be 3710 mg/kg bw,when rats were treated with d-Carvone (2244-16-8) orally.
- Executive summary:
Acute oral toxicity study was done in rats using test materiald-Carvone(2244-16-8).50% Mortality was observed at dose 3710 mg/kg bw. Hence,LD50 value was considered to be 3710 mg/kg bw,when rats were treated with d-Carvone(2244-16-8) orally.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 3 710 mg/kg bw
- Quality of whole database:
- Data is Klimisch 2 and from authoritative database
Acute toxicity: via inhalation route
Link to relevant study records
- Endpoint:
- acute toxicity: inhalation
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with limited documentation / justification
- Justification for type of information:
- Data is predicted using OECD QSAR toolbox version 3.3 and QMRF report has been attached
- Qualifier:
- according to guideline
- Guideline:
- other: as mentioned below
- Principles of method if other than guideline:
- Prediction was done by using OECD QSAR toolbox v3.3,2017
- GLP compliance:
- not specified
- Test type:
- standard acute method
- Limit test:
- no
- Specific details on test material used for the study:
- - Name of test material (IUPAC name): (5S)-2-methyl-5-(prop-1-en-2-yl)cyclohex-2-en-1-one- Common name: d-Carvone- Molecular formula: C10H14O- Molecular weight: 150.22 g/mol- Smiles notation: C1[C@H](CC=C(C1=O)C)C(C)=C- InChl: 1S/C10H14O/c1-7(2)9-5-4-8(3)10(11)6-9/h4,9H,1,5-6H2,2-3H3/t9-/m0/s1- Substance type: Organic
- Species:
- rat
- Strain:
- Sprague-Dawley
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- No data available
- Route of administration:
- inhalation: vapour
- Type of inhalation exposure:
- not specified
- Vehicle:
- not specified
- Remark on MMAD/GSD:
- No data available
- Details on inhalation exposure:
- No data available
- Analytical verification of test atmosphere concentrations:
- not specified
- Duration of exposure:
- 4 h
- Remarks on duration:
- No data available
- Concentrations:
- 22.07 mg/l in air
- No. of animals per sex per dose:
- No data available
- Control animals:
- not specified
- Details on study design:
- No data available
- Statistics:
- No data available
- Preliminary study:
- No data available
- Sex:
- male/female
- Dose descriptor:
- LC50
- Effect level:
- 22.07 mg/L air
- Based on:
- test mat.
- Exp. duration:
- 4 h
- Remarks on result:
- other: 50% Mortality was Observed
- Mortality:
- No data available
- Clinical signs:
- other: No data available
- Body weight:
- No data available
- Gross pathology:
- No data available
- Other findings:
- No data available
- Interpretation of results:
- other: not classified
- Conclusions:
- The LC50 value was estimated to be 22.07 mg/L in air when Sprague-Dawley male and female rats were exposed with (5S)-2-methyl-5-(prop-1-en-2-yl)cyclohex-2-en-1-one (cas no:2244-16-8) by inhalation for 4 hours.
- Executive summary:
In a prediction done by SSS (2017) using the OECD QSAR toolbox with log kow as the primary descriptor, the acute inhalation toxicity was estimated for (5S)-2-methyl-5-(prop-1-en-2-yl)cyclohex-2-en-1-one (cas no:2244-16-8). The LC50 was estimated to be 22.07 mg/L in air when Sprague-Dawley male and female rats were exposed with (5S)-2-methyl-5-(prop-1-en-2-yl)cyclohex-2-en-1-one (cas no:2244-16-8) by inahaltion for 4 hours.
Reference
The prediction was based on dataset comprised from the following descriptors: LC50
Estimation method: Takes average value from the 5 nearest neighbours
Domain logical expression:Result: In Domain
(((((((("a" or "b" or "c" or "d" ) and ("e" and ( not "f") ) ) and ("g" and ( not "h") ) ) and ("i" and ( not "j") ) ) and ("k" and ( not "l") ) ) and ("m" and ( not "n") ) ) and ("o" and ( not "p") ) ) and ("q" and "r" ) )
Domain logical expression index: "a"
Referential boundary: The target chemical should be classified as Michael addition AND Michael addition >> Polarised Alkenes-Michael addition AND Michael addition >> Polarised Alkenes-Michael addition >> Alpha, beta- unsaturated ketones by DNA binding by OECD
Domain logical expression index: "b"
Referential boundary: The target chemical should be classified as Michael Addition AND Michael Addition >> Michael addition on conjugated systems with electron withdrawing group AND Michael Addition >> Michael addition on conjugated systems with electron withdrawing group >> alpha,beta-Carbonyl compounds with polarized double bonds by Protein binding by OASIS v1.3
Domain logical expression index: "c"
Referential boundary: The target chemical should be classified as Michael addition AND Michael addition >> Polarised Alkenes AND Michael addition >> Polarised Alkenes >> Polarised alkene - ketones by Protein binding by OECD
Domain logical expression index: "d"
Referential boundary: The target chemical should be classified as Vinyl/Allyl Ketones by Aquatic toxicity classification by ECOSAR
Domain logical expression index: "e"
Referential boundary: The target chemical should be classified as Michael Addition AND Michael Addition >> Michael addition on conjugated systems with electron withdrawing group AND Michael Addition >> Michael addition on conjugated systems with electron withdrawing group >> alpha,beta-Carbonyl compounds with polarized double bonds by Protein binding by OASIS v1.3
Domain logical expression index: "f"
Referential boundary: The target chemical should be classified as Acylation OR Acylation >> Direct acylation involving a leaving group OR Acylation >> Direct acylation involving a leaving group >> Anhydrides (sulphur analogues of anhydrides) OR No alert found OR Nucleophilic addition OR Nucleophilic addition >> Addition to carbon-hetero double bonds OR Nucleophilic addition >> Addition to carbon-hetero double bonds >> Ketones by Protein binding by OASIS v1.3
Domain logical expression index: "g"
Referential boundary: The target chemical should be classified as Michael addition AND Michael addition >> Polarised Alkenes AND Michael addition >> Polarised Alkenes >> Polarised alkene - ketones by Protein binding by OECD
Domain logical expression index: "h"
Referential boundary: The target chemical should be classified as Michael addition >> Polarised Alkenes >> Polarised alkene - amides by Protein binding by OECD
Domain logical expression index: "i"
Referential boundary: The target chemical should be classified as Michael addition AND Michael addition >> Polarised Alkenes AND Michael addition >> Polarised Alkenes >> Polarised alkene - ketones by Protein binding by OECD
Domain logical expression index: "j"
Referential boundary: The target chemical should be classified as Michael addition >> Acid imides >> Acid imides-MA by Protein binding by OECD
Domain logical expression index: "k"
Referential boundary: The target chemical should be classified as Non-Metals by Groups of elements
Domain logical expression index: "l"
Referential boundary: The target chemical should be classified as Metalloids by Groups of elements
Domain logical expression index: "m"
Referential boundary: The target chemical should be classified as Aliphatic Carbon [CH] AND Aliphatic Carbon [-CH2-] AND Aliphatic Carbon [-CH3] AND Carbonyl, aliphatic attach [-C(=O)-] AND Carbonyl, olefinic attach [-C(=O)-] AND Miscellaneous sulfide (=S) or oxide (=O) AND Olefinic carbon [=CH- or =C<] AND Olefinic carbon [=CH2] AND Tertiary Carbon by Organic functional groups (US EPA)
Domain logical expression index: "n"
Referential boundary: The target chemical should be classified as Oxygen, aliphatic attach [-O-] by Organic functional groups (US EPA)
Domain logical expression index: "o"
Referential boundary: The target chemical should be classified as Aliphatic Carbon [CH] AND Aliphatic Carbon [-CH2-] AND Aliphatic Carbon [-CH3] AND Carbonyl, aliphatic attach [-C(=O)-] AND Carbonyl, olefinic attach [-C(=O)-] AND Miscellaneous sulfide (=S) or oxide (=O) AND Olefinic carbon [=CH- or =C<] AND Olefinic carbon [=CH2] AND Tertiary Carbon by Organic functional groups (US EPA)
Domain logical expression index: "p"
Referential boundary: The target chemical should be classified as Amino, aliphatic attach [-N<] by Organic functional groups (US EPA)
Domain logical expression index: "q"
Parametric boundary:The target chemical should have a value of log Kow which is >= 0.725
Domain logical expression index: "r"
Parametric boundary:The target chemical should have a value of log Kow which is <= 5.81
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LC50
- Value:
- 22 070 mg/m³ air
- Quality of whole database:
- Data is Klimisch 2 and from QSAR toolbox 3.3
Acute toxicity: via dermal route
Link to relevant study records
- Endpoint:
- acute toxicity: dermal
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
- Justification for type of information:
- data is from peer-reviewed journal
- Qualifier:
- according to guideline
- Guideline:
- other: as mentioned below
- Principles of method if other than guideline:
- Acute dermal toxicity test was carried out to study the effects of d-Carvone (2244-16-8) on rabbits.
- GLP compliance:
- not specified
- Test type:
- other: no data available
- Limit test:
- no
- Specific details on test material used for the study:
- - Name of test material (as cited in study report):d-Carvone- Molecular formula :C10H14O- Molecular weight :150.22 g/mol- Substance type:organic
- Species:
- rabbit
- Strain:
- not specified
- Sex:
- not specified
- Details on test animals or test system and environmental conditions:
- No data available
- Type of coverage:
- other: dermal
- Vehicle:
- not specified
- Details on dermal exposure:
- No data available
- Duration of exposure:
- No data available
- Doses:
- 4000 mg/kg bw
- No. of animals per sex per dose:
- No data available
- Control animals:
- not specified
- Details on study design:
- - Other examinations performed: clinical signs
- Statistics:
- No data available
- Preliminary study:
- No data available
- Sex:
- not specified
- Dose descriptor:
- LD50
- Effect level:
- 4 000 mg/kg bw
- Remarks on result:
- other: 50% mortality was observed at dose 4000 mg/kg bw in treated rabbits
- Mortality:
- 50% mortality was observed at dose 4000 mg/kg bw in treated rabbits
- Clinical signs:
- other: After systemic exposure,Skin dermatitis and changes in appendages were observed
- Gross pathology:
- No data available
- Other findings:
- No data available
- Interpretation of results:
- other: not classified
- Conclusions:
- The lethal concentration (LD50) value for acute dermal toxicity test was considered to be 4000 mg/kg bw,when rabbits were treated with d-Carvone (2244-16-8) orally.
- Executive summary:
In acute dermal toxicity study,rabbits were treated with d-Carvone(2244-16-8)in the concentration of 4000 mg/kg bw by dermal application.50% mortality was observed at dose 4000 mg/kg bw in treated rabbits.After systemic exposure,Skin dermatitis and changes in appendages were observed.Therefore, LD50 value was considered to be 4000 mg/kg bw,when rabbits were treated with d-Carvone (2244-16-8)by dermal application.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- LD50
- Value:
- 4 000 mg/kg bw
- Quality of whole database:
- Data is Klimisch 2 and from authoritative database
Additional information
Acute Oral Toxicity:
In different studies, d-Carvone (2244-16-8) has been investigated for acute oral toxicity to a greater or lesser extent. Often the studies are based on in vivo experimental data in rodents, i.e. most commonly in rats for d-Carvone (2244-16-8). The studies are summarized as below –
In experimental study conducted by U.S. National Library of Medicine (Chemidplus Database,U.S. National Library of Medicine,2017); Richard J. Lewis(Sax's Dangerous Properties of Industrial Materials, 12th Edition, 5 Volume Set,2012);RTECS (RTECS (registry of toxic effect of chemical substance data base ), 2017) andWorld Health Organization (the Fifty-first meeting of the Joint FAO/WHO Expert Committee on Food Additives (JECFA), WHO FOOD ADDITIVES SERIES: 42,1999) for the target substance d-Carvone (2244-16-8).Acute oral toxicity study was done in rats using test materiald-Carvone(2244-16-8).50% Mortality was observed at dose 3710 mg/kg bw. Hence,LD50 value was considered to be 3710 mg/kg bw,when rats were treated with d-Carvone(2244-16-8) orally.
This study is further supported by IFA GESTIS (Gestis Substance Database ,2017) for thetarget substance d-Carvone (2244-16-8). Acute oral toxicity study was done in rats using test material d-Carvone(2244-16-8).50% Mortality was observed at dose 3560 mg/kg bw. Hence,LD50 value was considered to be 3560 mg/kg bw,when rats were treated with d-Carvone(2244-16-8) orally.
Thus, based on the above studies on d-Carvone(2244-16-8), it can be concluded that LD50 value is greater than 2000 mg/kg bw. Thus, comparing this value with the criteria of CLP regulation, d-Carvone (2244-16-8) cannot be classified for acute oral toxicity.
Acute Inhalation toxicity:
In different studies, d-Carvone(2244-16-8) has been investigated for acute inhalation toxicity to a greater or lesser extent. Often are the studies based on in-vivo experiments in rodents, i.e. most commonly in rats for d-Carvone(2244-16-8) along with the study available on structurally similar read across substances 2-Methyl-5-(1-methylethenyl)-2-cyclohexenone (99-49-0) and Spearmint Oil (8008-79-5). The predicted data using the OECD QSAR toolbox has also been compared with the experimental studies. The studies are summarized as below –
In a prediction done by SSS (2017) using the OECD QSAR toolbox with log kow as the primary descriptor, the acute inhalation toxicity was estimated for (5S)-2-methyl-5-(prop-1-en-2-yl)cyclohex-2-en-1-one (cas no:2244-16-8). The LC50 was estimated to be 22.07 mg/L in air when Sprague-Dawley male and female rats were exposed with (5S)-2-methyl-5-(prop-1-en-2-yl)cyclohex-2-en-1-one (cas no:2244-16-8) by inahaltion for 4 hours.
The above study is supported by European Chemicals Agency (ECHA) (Proposal for Harmonised Classification and Labelling – Carvone, European Chemicals Agency (ECHA), 21 September 2012);COMMISSIONHEALTH & CONSUMER PROTECTION DIRECTORATE-GENERAL,Standing Committee on the Food Chain and Animal Health (Review report for the active substance carvone Finalised in the Standing Committee on the Food Chain and Animal Health, in view of the inclusion of carvone in Annex I of Directive 91/414/EEC,22 January 2008);Committee for Risk Assessment RAC –ECHA (Annex 1 Background document to the Opinion proposing harmonised classification and labelling at Community level of carvone , Committee for Risk Assessment RAC -ECHA ,adopted on 4 june,2013) andEuropean Food Safety Authority (EFSA) (EFSA Journal 2014;12(7):3806) for the structurally similar read across substances 2-Methyl-5-(1-methylethenyl)-2-cyclohexenone (99-49-0).
In acute inhalation toxicity study, rats were exposed to 2-Methyl-5-(1-methylethenyl)-2-cyclohexenone(99-49-0)in the concentration of 5.66 mg/l in air (5660 mg/m3) inhaled as a Single dose. One female died the day after the exposure. During exposure a decreased breathing frequency, and less frequently, post-inspiratory apnoea and superficial breathing were observed. After exposure and increased breathing frequency, post-inspiratory apnoea and dyspnoea were seen. Clinical signs during exposure were restlessness and stress and in coordination and tremors. A dirty and wet fur was observed 24-48h after treatment. Alopecia was observed in a few rats at days 7-13. Body weight gain was impaired in most rats during the first week after treatment. Normal body weight gain was observed in the second week, except for two females that showed only marginal body weight gain.GrossPathology revealed no abnormalities, except in the female that died the day after exposure: dark foamy lungs, light coloured liver and air-filled stomach and intestines were observed. Therefore, LC50 value was considered to be >5.66 mg/l in air (5660 mg/m3), when rats were exposed with 2-Methyl-5-(1-methylethenyl)-2-cyclohexenone (99-49-0) by inhalation according to OECD Guideline 403 (Acute Inhalation Toxicity).
These results are further supported by European Food Safety Authority (EFSA) (Spearmint Oil - DAR - Vol. 1 of the fourth stage of the review programme referred to in Article 8(2) of Council Directive 91/414/EEC, European Food Safety Authority (EFSA), August 2008) and AGRITOX (AGRITOX - Plant Protection Phentopharmaceuticals Database,2017) for the Spearmint Oil (8008-79-5). In acute inhalation toxicity study, male and female rats were exposed to Spearmint Oil(8008-79-5)in the concentration of 5430 mg/ m3 inhaled as a Single dose for 4 hour. No mortality was observed at dose 5.43 mg/L (5430 mg/m3) in treated rats. Therefore, LC50 value was considered to be >5430 mg/m3 (5.43 mg/L),when both male and female rats were exposed with Spearmint Oil(8008-79-5)by inhalation for 4 hours.
Thus, based on the above studies on d-Carvone(2244-16-8) and it’s structurally similar read across substances 2-Methyl-5-(1-methylethenyl)-2-cyclohexenone (99-49-0) and Spearmint Oil(8008-79-5), it can be concluded that LC50 value is greater than 5 mg/L air. Thus, comparing this value with the criteria of CLP regulation, d-Carvone(2244-16-8) cannot be classified for acute inhalation toxicity.
Acute Dermal Toxicity:
In different studies, d-Carvone(2244-16-8) has been investigated for acute dermal toxicity to a greater or lesser extent. Often the studies are based on in vivo experimental data in rodents, i.e. most commonly in rabbits for d-Carvone(2244-16-8). The studies are summarized as below –
In experimental study conducted by D. L. J. Opdyke (Food and Cosmetics Toxicology,Vol. 16, Pg. 673, 1978); U.S. National Library of Medicine (Chemidplus Database,U.S. National Library of Medicine,2017) andRTECS (RTECS (registry of toxic effect of chemical substance data base ), 2017) for the target substance d-Carvone(2244-16-8).In acute dermal toxicity study,rabbits were treated with d-Carvone(2244-16-8)in the concentration of 4000 mg/kg bw by dermal application.50% mortality was observed at dose 4000 mg/kg bw in treated rabbits.After systemic exposure,Skin dermatitis and changes in appendages were observed.Therefore, LD50 value was considered to be 4000 mg/kg bw,when rabbits were treated with d-Carvone (2244-16-8) by dermal application.
This study is further supported by US EPA. Office of Pesticide Programs (Technical Document for l-Carvone also referred to as a BRAD, US EPA. Office of Pesticide Programs,31-august-2009)for the target substance d-Carvone(2244-16-8).In acute dermal toxicity study,rabbits were treated with d-Carvone(2244-16-8)in the concentration of 3860 mg/kg bw by dermal application.50% mortality was observed at dose 3860 mg/kg bw in treated rabbits.Therefore, LD50 value was considered to be 3860 mg/kg bw,when rabbits were treated with d-Carvone(2244-16-8)by dermal application.
The above study was further supported by IFA GESTIS (Gestis Substance Database ,2017)for the target substance d-Carvone(2244-16-8).In acute dermal toxicity study,rabbits were treated with d-Carvone(2244-16-8)in the concentration of 3840mg/kg bw by dermal application.50% mortality was observed at dose 3840 mg/kg bw in treated rabbits.Therefore, LD50 value was considered to be 3840 mg/kg bw,when rabbits were treated with d-Carvone(2244-16-8)by dermal application.
Thus, based on the above studies on d-Carvone (2244-16-8), it can be concluded that LD50 value is greater than 2000 mg/kg bw. Thus, comparing this value with the criteria of CLP regulation, d-Carvone (2244-16-8) cannot be classified for acute dermal toxicity.
Justification for classification or non-classification
Based on the above experimental studies and prediction on d-Carvone (2244-16-8),and it’s structurally similar read across substances, it can be concluded that LD50 value is greater than 2000 mg/kg bw. Thus, comparing this value with the criteria of CLP regulation, d-Carvone (2244-16-8) cannot be classified for acute oral,acute inhalation and acute dermal toxicity.
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