Registration Dossier

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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Administrative data

Workers - Hazard via inhalation route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
3.53 mg/m³
Most sensitive endpoint:
developmental toxicity / teratogenicity
Route of original study:
Oral
DNEL related information
DNEL derivation method:
ECHA REACH Guidance
Overall assessment factor (AF):
75
Dose descriptor starting point:
NOAEL
Value:
300 mg/kg bw/day
Modified dose descriptor starting point:
NOAEC
Value:
264.5 mg/m³
Explanation for the modification of the dose descriptor starting point:

The following correction was made to the NOAEL (oral): Correction respiratory volume rat (8 hour) 1/0.38 m³/kg bw/day, Correction for respiratory volume (worker): 6.7 m³/10 m³. Correction for oral to inhaled 1/2. Therefore the corrected NOAEC for repeated-dose systemic effects via the inhalation route is: 300*(1/0.38)*(6.7 m³/10 m³)*(1/2) = 264.5 mg/m³.

AF for dose response relationship:
1
Justification:
Default
AF for differences in duration of exposure:
6
Justification:
Default (subacute to chronic)
AF for interspecies differences (allometric scaling):
1
Justification:
Default (oral rat to inhaled human)
AF for other interspecies differences:
2.5
Justification:
Default
AF for intraspecies differences:
5
Justification:
Default (workers)
AF for the quality of the whole database:
1
Justification:
Default
AF for remaining uncertainties:
1
Justification:
Default
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
no hazard identified
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

Workers - Hazard via dermal route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
1 mg/kg bw/day
Most sensitive endpoint:
developmental toxicity / teratogenicity
Route of original study:
Oral
DNEL related information
DNEL derivation method:
ECHA REACH Guidance
Overall assessment factor (AF):
300
Dose descriptor starting point:
NOAEL
Value:
300 mg/kg bw/day
Explanation for the modification of the dose descriptor starting point:

No correction was required to dose descriptor starting point.

AF for dose response relationship:
1
Justification:
Default
AF for differences in duration of exposure:
6
Justification:
Default (subacute to chronic)
AF for interspecies differences (allometric scaling):
4
Justification:
Default (oral rat to dermal human)
AF for other interspecies differences:
2.5
Justification:
Default
AF for intraspecies differences:
5
Justification:
Default (workers)
AF for the quality of the whole database:
1
Justification:
Default
AF for remaining uncertainties:
1
Justification:
Default
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
no hazard identified
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified

Workers - Hazard for the eyes

Local effects

Hazard assessment conclusion:
low hazard (no threshold derived)

Additional information - workers

General Population - Hazard via inhalation route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
0.87 mg/m³
Most sensitive endpoint:
developmental toxicity / teratogenicity
Route of original study:
Oral
DNEL related information
DNEL derivation method:
ECHA REACH Guidance
Overall assessment factor (AF):
150
Dose descriptor starting point:
NOAEL
Value:
300 mg/kg bw/day
Modified dose descriptor starting point:
NOAEC
Value:
130.4 mg/m³
Explanation for the modification of the dose descriptor starting point:

The following correction was made to the NOAEL (oral): Correction respiratory volume rat (24 hour) 1/1.15 m³/kg bw. Correction for oral to inhaled 1/2. Therefore the corrected NOAEC for repeated-dose systemic effects via the inhalation route is: 300*(1/1.15)*(1/2) = 130.4 mg/m³.

AF for dose response relationship:
1
Justification:
Default
AF for differences in duration of exposure:
6
Justification:
Default (subacute to chronic)
AF for interspecies differences (allometric scaling):
1
Justification:
Default (oral rat to inhaled human)
AF for other interspecies differences:
2.5
Justification:
Default
AF for intraspecies differences:
10
Justification:
Default (general population)
AF for the quality of the whole database:
1
Justification:
Default
AF for remaining uncertainties:
1
Justification:
Default
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
no hazard identified
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

General Population - Hazard via dermal route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
0.5 mg/kg bw/day
Most sensitive endpoint:
developmental toxicity / teratogenicity
Route of original study:
Oral
DNEL related information
DNEL derivation method:
ECHA REACH Guidance
Overall assessment factor (AF):
600
Dose descriptor starting point:
NOAEL
Value:
300 mg/kg bw/day
Explanation for the modification of the dose descriptor starting point:

No correction was required to dose descriptor starting point.

AF for dose response relationship:
1
Justification:
Default
AF for differences in duration of exposure:
6
Justification:
Default (subacute to chronic)
AF for interspecies differences (allometric scaling):
4
Justification:
Default (oral rat to dermal human)
AF for other interspecies differences:
2.5
Justification:
Default
AF for intraspecies differences:
10
Justification:
Default (general population)
AF for the quality of the whole database:
1
Justification:
Default
AF for remaining uncertainties:
1
Justification:
Default
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
no hazard identified
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified

General Population - Hazard via oral route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
0.5 mg/kg bw/day
Most sensitive endpoint:
developmental toxicity / teratogenicity
Route of original study:
Oral
DNEL related information
DNEL derivation method:
ECHA REACH Guidance
Overall assessment factor (AF):
600
Dose descriptor starting point:
NOAEL
Value:
300 mg/kg bw/day
Explanation for the modification of the dose descriptor starting point:

No correction was required to dose descriptor starting point.

AF for dose response relationship:
1
Justification:
Default
AF for differences in duration of exposure:
6
Justification:
Default (subacute to chronic)
AF for interspecies differences (allometric scaling):
4
Justification:
Default (oral rat to oral human)
AF for other interspecies differences:
2.5
Justification:
Default
AF for intraspecies differences:
10
Justification:
Default (general population)
AF for the quality of the whole database:
1
Justification:
Default
AF for remaining uncertainties:
1
Justification:
Default
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

General Population - Hazard for the eyes

Local effects

Hazard assessment conclusion:
low hazard (no threshold derived)

Additional information - General Population

When CyreneTM is in aqueous solution, the keto group (C=O) gains water (H2O) to form the corresponding Gem Diol {(1S,5R)-6,8-dioxabicyclo[3.2.1]octane-4,4-diol}. An equilibrium is established rapidly (meaning that the reaction is rapidly reversible).The ratio of the two forms depends upon the amount of water present. Further information is available in the Physical and chemical properties endpoint summary (IUCLID Section 4).

 

For the human health chemical safety assessment, external exposure will largely be to the CyreneTM form (although some hydration to Gem Diol is probable in moist air). Hence, the Assessment Entity refers to CyreneTM and the physicochemical properties (vapour pressure and molecular weight) of this species are used in the assessment. After absorption, concentrations of the substance in vivo will be low and the Gem Diol will be rapidly formed due to the presence of water. This applies to both the available experimental data and human internal exposure.