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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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:
no hazard identified
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
Route of original study:
By inhalation
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
0.308 mg/m³
Most sensitive endpoint:
irritation (respiratory tract)
DNEL related information
DNEL derivation method:
ECHA REACH Guidance
Overall assessment factor (AF):
5
Dose descriptor:
NOAEC
AF for dose response relationship:
1
Justification:
This factor is applied because the dose-descriptor starting point is a NOAEC.
AF for differences in duration of exposure:
1
Justification:
Local effects on the respiratory tract are related to the deposited dose per unit of surface area. Below a certain concentration the clearance capacity of the lungs is not overwhelmed and the lungs retain the ability to clear the deposited substance. Therefore, the lung effects are not suspected to worsen with increasing exposure duration.
AF for interspecies differences (allometric scaling):
1
Justification:
AF not used for inhalation.
AF for other interspecies differences:
1
Justification:
No additional assessment factor is added for interspecies extrapolation from rodent to human, since the respiratory rate of rats (0.29 m3/kg-day according to Pauluhn (2010)) leads to a greater lung tract burden compared to humans (0.14 m3/kg-day), thus the effects observed in rats are exaggerated and provide a “built in” safety margin. 
AF for intraspecies differences:
5
Justification:
A factor of 5 is applied for worker DNELs.
AF for the quality of the whole database:
1
Justification:
The key study is considered as a reliable study with a klimisch score of 1.
AF for remaining uncertainties:
1
Justification:
No other assessment factor is applied.
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:
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:
medium hazard (no threshold derived)
Most sensitive endpoint:
sensitisation (skin)

Workers - Hazard for the eyes

Local effects

Hazard assessment conclusion:
no hazard identified

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
Route of original study:
By inhalation
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
0.055 mg/m³
Most sensitive endpoint:
irritation (respiratory tract)
DNEL related information
DNEL derivation method:
ECHA REACH Guidance
Overall assessment factor (AF):
10
Dose descriptor:
NOAEC
AF for dose response relationship:
1
Justification:
This factor is applied because the dose-descriptor starting point is a NOAEC.
AF for differences in duration of exposure:
1
Justification:
Local effects on the respiratory tract are related to the deposited dose per unit of surface area. Below a certain concentration the clearance capacity of the lungs is not overwhelmed and the lungs retain the ability to clear the deposited substance. Therefore, the lung effects are not suspected to worsen with increasing exposure duration.
AF for interspecies differences (allometric scaling):
1
Justification:
AF not used for inhalation.
AF for other interspecies differences:
1
Justification:
No additional assessment factor is added for interspecies extrapolation from rodent to human, since the respiratory rate of rats (0.29 m3/kg-day according to Pauluhn (2010)) leads to a greater lung tract burden when compared to humans (0.14 m3/kg-day); thus the effects observed in rats are exaggerated and provide a “built in” safety margin. 
AF for intraspecies differences:
10
Justification:
A factor of 10 is applied for the general population DNELs.
AF for the quality of the whole database:
1
Justification:
The key study is considered as a reliable study with a klimisch score of 1.
AF for remaining uncertainties:
1
Justification:
No other assessment factor is applied.
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:
medium hazard (no threshold derived)
Most sensitive endpoint:
sensitisation (skin)

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
Route of original study:
Oral
DNEL related information

General Population - Hazard for the eyes

Local effects

Hazard assessment conclusion:
no hazard identified

Additional information - General Population