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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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:
2.47 mg/m³
Most sensitive endpoint:
repeated dose toxicity
Route of original study:
Oral
DNEL related information
DNEL derivation method:
ECHA REACH Guidance
Overall assessment factor (AF):
50
Dose descriptor starting point:
NOAEL
Value:
100 mg/kg bw/day
Modified dose descriptor starting point:
NOAEC
Value:
123.4 mg/m³
Explanation for the modification of the dose descriptor starting point:

inhalation NOAEC = NOAELoral*(1/0.38 m³/kg bw/day)*(ABSoral-rat/ABSinh-human)*(6.7 m³ (8h)/10 m³ (8h))*(fexpo,rat/fexpo,worker) = 100 mg/kg bw/day*(1/0.38 m³/kg bw/day)*(0.5/1)*0.67*(7/5) = 123.4 mg/m³

ABSoral-rat = oral absorption rate in rats

ABSinh-human = inhalation absorption rate in humans

fexpo,rat = exposure frequency rats = 7 days/week

fexpo,worker = exposure frequency worker = 5 days/week

In a worst case approach the default oral absorption rate of 50% for the rat was used in the calculations (default 0.5/1 according to ECHA Guidance on Information Requirements and Chemical Safety Assessment - Chapter R.8: Characterisation of dose [concentration]-response for human health)

AF for dose response relationship:
1
Justification:
NOAEL is starting point
AF for differences in duration of exposure:
4
Justification:
An assessment factor of 4 is used. According to the ECHA Guidance on Information Requirements and Chemical Safety Assessment - Chapter R.8: Characterisation of dose [concentration]-response for human health), the default value for subacute (28-day) to chronic conversion is 6 and the default assessment factor for subchronic (90-day) to chronic conversion is 2. Since the oral NOAEL used to derive the inhalation NOAEC was determined in an oral combined repeated dose toxicity study with the reproduction/developmental toxicity screening test (according to OECD TG 422) based on effects observed in female rats which have been dosed for 50 - 60 days, an assessment factor of 6 (reflecting 28-day exposure) is considered too conservative. Due to the fact that the real exposure time of the rats is approx. 61% of that of a subchronic (90-day) study, an assessment factor of 4 is considered to reflect the exposure situation in the combined repeated dose toxicity study with the reproduction/developmental toxicity screening test (according to OECD TG 422) in a more realistic way.
AF for interspecies differences (allometric scaling):
1
Justification:
AF for allometric scaling already included in starting point derivation method; no further factor required.
AF for other interspecies differences:
2.5
Justification:
Default value
AF for intraspecies differences:
5
Justification:
Default value (worker)
AF for the quality of the whole database:
1
AF for remaining uncertainties:
1
Acute/short term exposure
Hazard assessment conclusion:
hazard unknown but no further hazard information necessary as no exposure expected
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
hazard unknown but no further hazard information necessary as no exposure expected
Acute/short term exposure
Hazard assessment conclusion:
hazard unknown but no further hazard information necessary as no exposure expected
DNEL related information

Workers - Hazard via dermal route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
0.7 mg/kg bw/day
Most sensitive endpoint:
repeated dose toxicity
Route of original study:
Oral
DNEL related information
DNEL derivation method:
ECHA REACH Guidance
Overall assessment factor (AF):
200
Dose descriptor starting point:
NOAEL
Value:
100 mg/kg bw/day
Modified dose descriptor starting point:
NOAEL
Value:
140 mg/kg bw/day
Explanation for the modification of the dose descriptor starting point:

Dermal NOAEL=NOAELoral*(ABSoral-rat/ABSdermal-human)*(fexpo,rat/fexpo,worker) = 100 mg/kg bw/day*(1/1)*(7/5) = 140 mg/kg bw/day

ABSoral-rat = oral absorption rate in rats,

ABSdermal-human = dermal absorption rate in humans

fexpo,rat = exposure frequency rats = 7 days/week

fexpo,worker = exposure frequency worker = 5 days/week

AF for dose response relationship:
1
Justification:
NOAEL is starting point
AF for differences in duration of exposure:
4
Justification:
An assessment factor of 4 is used. According to the ECHA Guidance on Information Requirements and Chemical Safety Assessment - Chapter R.8: Characterisation of dose [concentration]-response for human health), the default value for subacute (28-day) to chronic conversion is 6 and the default assessment factor for subchronic (90-day) to chronic conversion is 2. Since the oral NOAEL used to derive the inhalation NOAEC was determined in an oral combined repeated dose toxicity study with the reproduction/developmental toxicity screening test (according to OECD TG 422) based on effects observed in female rats which have been dosed for 50 - 60 days, an assessment factor of 6 (reflecting 28-day exposure) is considered too conservative. Due to the fact that the real exposure time of the rats is approx. 61% of that of a subchronic (90-day) study, an assessment factor of 4 is considered to reflect the exposure situation in the combined repeated dose toxicity study with the reproduction/developmental toxicity screening test (according to OECD TG 422) in a more realistic way.
AF for interspecies differences (allometric scaling):
4
Justification:
Default value (rat -> human)
AF for other interspecies differences:
2.5
Justification:
Default value
AF for intraspecies differences:
5
Justification:
Default value (worker)
AF for the quality of the whole database:
1
AF for remaining uncertainties:
1
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
Most sensitive endpoint:
acute toxicity
Route of original study:
Dermal
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
no hazard identified
Most sensitive endpoint:
sensitisation (skin)
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
Most sensitive endpoint:
skin irritation/corrosion

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:
hazard unknown but no further hazard information necessary as no exposure expected
Acute/short term exposure
Hazard assessment conclusion:
hazard unknown but no further hazard information necessary as no exposure expected
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
hazard unknown but no further hazard information necessary as no exposure expected
Acute/short term exposure
Hazard assessment conclusion:
hazard unknown but no further hazard information necessary as no exposure expected
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:
hazard unknown but no further hazard information necessary as no exposure expected
Acute/short term exposure
Hazard assessment conclusion:
hazard unknown but no further hazard information necessary as no exposure expected
DNEL related information

General Population - Hazard for the eyes

Local effects

Hazard assessment conclusion:
no hazard identified

Additional information - General Population