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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Toxicological information

Repeated dose toxicity: oral

Currently viewing:

Administrative data

Endpoint:
sub-chronic toxicity: oral
Type of information:
calculation (if not (Q)SAR)
Adequacy of study:
key study
Study period:
2021-2022
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
accepted calculation method
Cross-reference
Reason / purpose for cross-reference:
reference to same study
Reference
Endpoint:
screening for reproductive / developmental toxicity
Type of information:
calculation (if not (Q)SAR)
Adequacy of study:
key study
Study period:
2021-2022
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
accepted calculation method
Reason / purpose for cross-reference:
reference to same study
Qualifier:
no guideline followed
Principles of method if other than guideline:
The dose addition model and the toxicity information of component chemicals in sample
GLP compliance:
no
Species:
rat
Key result
Dose descriptor:
NOAEL
Effect level:
37 mg/kg bw/day (nominal)
Based on:
other: Typical concentration of the 10 most present constituents
Sex:
male/female
Basis for effect level:
other: Critical effects identified in toxicological studies
Critical effects observed:
no
Key result
Dose descriptor:
NOAEL
Generation:
F1
Effect level:
37 mg/kg bw/day (nominal)
Based on:
other: Typical concentration of the 10 most present constituents
Sex:
male/female
Basis for effect level:
other: Critical effects identified in toxicological studies
Critical effects observed:
no
Reproductive effects observed:
no
Conclusions:
Therefore, based on the dose addition model and the toxicological data of the 10 most present constituents, representing 96.9% of the registered substance, the NOAEL for reproduction/developmental toxicity of the sample are calculated as 37 mg/kg bw/day for rats.
Executive summary:

In this document designed to address a reproductive/developmental toxicity and a repeated dose toxicity assessment of the Star Anise Oil, initial information concerning the determination of oral toxicity after repeated doses administration and possible effects on male and female reproductive performance using the individual toxicity of each constituent of the complex substance are generated.


It allows to fulfil the standard information requirements requested under Annex VIII to the Regulation (EC) No 1907/2006 (i.e. the short-term repeated dose toxicity (28 days) and the screening for reproductive/developmental toxicity data).


 


 


The Reproduction/Developmental toxicity and subchronic oral toxicity information on individual constituents of the Star Anise Oil (i.e. the NOAEL) are collected from public data on the ECHA disseminated dossiers and/or on articles from scientific literature. In a conservative approach, if more than one study is available, the lowest No-Observed-Adverse-Effect-Level (NOAEL) is retained for the assessment.


 


For the toxicity assessment, in the absence of data on the whole mixture or a similar mixture, the risk assessment was based on the toxic properties of the 10 most present constituents, representing 96.9% of the registered substance. In this purpose, the mechanism of toxicity of the chemicals concerned is simulated from a computer predictive model. Although some structural alert for DNA and protein binding models were found, the lack of reactivity of the chemicals is confirmed from the predictions on the Cramer rules and the Verhaar system models, and the mode of action of these chemicals is expected to be similar for almost all of them. Therefore, the toxicologically similar chemicals approach is used for toxicity assessment of the mixture and corresponds to the most conservative dose addition model of the exposure level of the mixture, using the Hazard Index method. The formula used represents dose addition as a sum of exposures scaled by each chemical’s relative toxicity. This method of calculation includes uncertainties but is very conservative.


From the equation and the toxicity information of component chemicals in sample, the reproduction/developmental and subchronic oral toxicity of the sample are calculated at 37 and 236 mg/kg bw/day for rats, respectively.


 


 


Therefore, based on the dose addition model and the toxicological data of the 10 most present constituents, representing 96.9% of the registered substance, the NOAEL for reproduction/developmental toxicity and subchronic oral toxicity of the sample are calculated as 37 and 236 mg/kg bw/day for rats, respectively.

Data source

Reference
Reference Type:
other: Position paper
Title:
Unnamed
Year:
2022
Report date:
2022

Materials and methods

Test guideline
Qualifier:
no guideline followed
Principles of method if other than guideline:
The dose addition model and the toxicity information of component chemicals in sample
GLP compliance:
no

Test material

Constituent 1
Reference substance name:
Star anise, Illicium verum, ext.
EC Number:
283-518-1
EC Name:
Star anise, Illicium verum, ext.
Cas Number:
84650-59-9
Molecular formula:
NA
IUPAC Name:
1-methoxy-4-[(1E)-prop-1-en-1-yl]benzene
Test material form:
liquid

Test animals

Species:
rat

Results and discussion

Effect levels

Key result
Dose descriptor:
NOAEL
Effect level:
236 mg/kg bw/day (nominal)
Based on:
other: Typical concentration of the 10 most present constituents
Sex:
male/female
Basis for effect level:
other: Critical effects identified in toxicological studies

Target system / organ toxicity

Critical effects observed:
no

Applicant's summary and conclusion

Conclusions:
Therefore, based on the dose addition model and the toxicological data of the 10 most present constituents, representing 96.9% of the registered substance, the NOAEL for subchronic oral toxicity of the sample are calculated as 236 mg/kg bw/day for rats.
Executive summary:

In this document designed to address a reproductive/developmental toxicity and a repeated dose toxicity assessment of the Star Anise Oil, initial information concerning the determination of oral toxicity after repeated doses administration and possible effects on male and female reproductive performance using the individual toxicity of each constituent of the complex substance are generated.


It allows to fulfil the standard information requirements requested under Annex VIII to the Regulation (EC) No 1907/2006 (i.e. the short-term repeated dose toxicity (28 days) and the screening for reproductive/developmental toxicity data).


 


 


The Reproduction/Developmental toxicity and subchronic oral toxicity information on individual constituents of the Star Anise Oil (i.e. the NOAEL) are collected from public data on the ECHA disseminated dossiers and/or on articles from scientific literature. In a conservative approach, if more than one study is available, the lowest No-Observed-Adverse-Effect-Level (NOAEL) is retained for the assessment.


 


For the toxicity assessment, in the absence of data on the whole mixture or a similar mixture, the risk assessment was based on the toxic properties of the 10 most present constituents, representing 96.9% of the registered substance. In this purpose, the mechanism of toxicity of the chemicals concerned is simulated from a computer predictive model. Although some structural alert for DNA and protein binding models were found, the lack of reactivity of the chemicals is confirmed from the predictions on the Cramer rules and the Verhaar system models, and the mode of action of these chemicals is expected to be similar for almost all of them. Therefore, the toxicologically similar chemicals approach is used for toxicity assessment of the mixture and corresponds to the most conservative dose addition model of the exposure level of the mixture, using the Hazard Index method. The formula used represents dose addition as a sum of exposures scaled by each chemical’s relative toxicity. This method of calculation includes uncertainties but is very conservative.


From the equation and the toxicity information of component chemicals in sample, the reproduction/developmental and subchronic oral toxicity of the sample are calculated at 37 and 236 mg/kg bw/day for rats, respectively.


 


 


Therefore, based on the dose addition model and the toxicological data of the 10 most present constituents, representing 96.9% of the registered substance, the NOAEL for reproduction/developmental toxicity and subchronic oral toxicity of the sample are calculated as 37 and 236 mg/kg bw/day for rats, respectively.