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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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:
0.025 mg/m³
Most sensitive endpoint:
effect on fertility
Route of original study:
Oral
DNEL related information
DNEL derivation method:
ECHA REACH Guidance
Overall assessment factor (AF):
60
Dose descriptor starting point:
NOAEL
Value:
3 mg/kg bw/day
Modified dose descriptor starting point:
NOAEC
Value:
1.5 mg/m³
Explanation for the modification of the dose descriptor starting point:

NOAEL applied based on the results of a two week prelimininary range finding study. 

No similar, significant, effects were seen on the main study, where male animals were dosed for two weeks pre-paring (total of 10 weeks dosing) or with 10 weeks pre-pairing (18 weeks total treatment).

The lack of discernible difference in the sperm analysis conducted with 2 weeks prepairing, 10 week treatment, from control animal data contradicts the findings seen on the preliminary, range finding studies. This may indicate that the effects seen on sperm within the first two weeks of dosing are a transient phenomenon associated with adaptation to early toxicological conflict or dosing procedures.However, this risk assessment has been performed based on the conservative value taken from the preliminary study.

According to Chapter R.8 of REACH Guidance on information requirements and chemical safety assessment, it is proposed in the absence of route-specific information on the starting route, to include a default factor of 2 in the case of oral-to-inhalation extrapolation.

Assessment factors:

Interspecies AF of 4

Allometric scaling default AF (4) to allow for differences in metabolic rate. Species specific information is available therefore a further AF for remaining differences is not relevant as according to Section R.8.4.3.3 of the REACH guidance on information requirements and chemical safety assessment

Intraspecies AF of 5

Default assessment factor workers for threshold effects based on the fact that this sub-population does not include the very young, very old or very ill

Exposure duration AF of 3

Assessment factor selected due extrapolation to chronic based on Extended OGRTs not currently covered in ECHA guidance

AF for dose response relationship:
1
AF for differences in duration of exposure:
3
Justification:
Assessment factor selected due extrapolation to chronic based on Extended OGRTs not currently covered in ECHA guidance
AF for interspecies differences (allometric scaling):
4
Justification:
Allometric scaling default AF (4) to allow for differences in metabolic rate.
AF for intraspecies differences:
5
Justification:
default value for workers
AF for the quality of the whole database:
1
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
hazard unknown (no further information necessary)
Acute/short term exposure
Hazard assessment conclusion:
hazard unknown (no further information necessary)
DNEL related information

Workers - Hazard via dermal route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
0.05 mg/kg bw/day
Most sensitive endpoint:
effect on fertility
Route of original study:
Oral
DNEL related information
DNEL derivation method:
ECHA REACH Guidance
Overall assessment factor (AF):
60
Dose descriptor starting point:
NOAEL
Value:
3 mg/kg bw/day
Modified dose descriptor starting point:
NOAEL
Value:
3 mg/kg bw/day
Explanation for the modification of the dose descriptor starting point:
No direct data for dermal route are available.
AF for dose response relationship:
1
AF for differences in duration of exposure:
3
Justification:
Based on the results of a preliminary EOGRTs study
AF for interspecies differences (allometric scaling):
4
Justification:
rats are used in the animal test
AF for intraspecies differences:
5
Justification:
default factor for workers
AF for the quality of the whole database:
1
AF for remaining uncertainties:
1
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
medium hazard (no threshold derived)
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified

Workers - Hazard for the eyes

Local effects

Hazard assessment conclusion:
high hazard (no threshold derived)

Additional information - workers

General Population - Hazard via inhalation route

Systemic effects

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

General Population - Hazard for the eyes

Local effects

Hazard assessment conclusion:
no hazard identified

Additional information - General Population