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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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:
38.5 mg/m³
Most sensitive endpoint:
repeated dose toxicity
DNEL related information
Overall assessment factor (AF):
50
Modified dose descriptor starting point:
NOAEC
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:
10.9 mg/kg bw/day
Most sensitive endpoint:
repeated dose toxicity
DNEL related information
Overall assessment factor (AF):
10
Modified dose descriptor starting point:
NOAEL
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
1.06 mg/cm²
Most sensitive endpoint:
repeated dose toxicity
DNEL related information
Overall assessment factor (AF):
12.5
Dose descriptor:
other: NOAEL
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified

Workers - Hazard for the eyes

Local effects

Hazard assessment conclusion:
no hazard identified

Additional information - workers

Calculation dermal DNEL long-term, systemic

The subchronic oral toxicity test (Bechtel, 1990) conducted in male and female Sprague-Dawley rats was used as a starting point for the DNEL derivation.

90d NOAEL (rat) = 1093 mg/kg bw.d

workers NOAEL - dermal (human): (1093 mg/kg bw.d : (4 * 25)) = 109.3 mg/kg bw.d

Assessment factors as described above. ECHA assessment factors were used.

Calculation inhalation DNEL long-term, systemic

The subchronic oral toxicity test (Bechtel, 1990) conducted in male and female Sprague-Dawley rats was used as a starting point for the DNEL derivation.

90d NOAEL (rat) = 1093 mg/kg bw.d

workers NOAEC - inhalation: (1093 mg/kg bw.d : 0.38 m3/kg bw)*(6.7 m3 : 10 m3) = 1927.1 mg/m3

Assessment factors as described above. ECHA assessment factors were used.

Calculation dermal DNEL long-term, local

The subacute dermal toxicity test (21d) conducted in male and female rabbits (read-across from TBBS) was used as a starting point for the DNEL derivation.

21d NOAEL (rabbit) = 500 mg / kg bw (read-across from TBBS)

correction to appropriate unit:

* mean weight (males and females, throughout whole study): ca. 2,650 kg

* exposed area: 10 x 10 cm = 100 cm2

corrected NOAEL = 13,25 mg/cm2

Assessment factors as described above. ECHA assessment factors were used.

No time-scaling nor assessment factor required for duration of exposure due to the fact that local skin effects typically are mainly concentration-driven. No allometric scaling required for local effects.

General Population - Hazard via inhalation route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
9.5 mg/m³
Most sensitive endpoint:
repeated dose toxicity
DNEL related information
Overall assessment factor (AF):
100
Modified dose descriptor starting point:
NOAEC
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:
5.47 mg/kg bw/day
Most sensitive endpoint:
repeated dose toxicity
DNEL related information
Overall assessment factor (AF):
20
Modified dose descriptor starting point:
NOAEL
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
0.53 mg/cm²
Most sensitive endpoint:
repeated dose toxicity
DNEL related information
Overall assessment factor (AF):
25
Dose descriptor:
other: NOAEL
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:
5.46 mg/kg bw/day
Most sensitive endpoint:
repeated dose toxicity
DNEL related information
Overall assessment factor (AF):
20
Modified dose descriptor starting point:
NOAEL
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

Calculation dermal DNEL long-term, systemic

The subchronic oral toxicity test (Bechtel, 1990) conducted in male and female Sprague-Dawley rats was used as a starting point for the DNEL derivation.

90d NOAEL (rat) = 1093 mg/kg bw.d

general population NOAEL - dermal (human): (1093 mg/kg bw.d : (4 * 2.5)) = 109.3 mg/kg bw.d

Assessment factors as described above. ECHA assessment factors were used.

Calculation inhalation DNEL long-term, systemic

The subchronic oral toxicity test (Bechtel, 1990) conducted in male and female Sprague-Dawley rats was used as a starting point for the DNEL derivation.

90d NOAEL (rat) = 1093 mg/kg bw.d

general population NOAEC - inhalation: (1093 mg/kg bw.d : 1.15 m3/kg bw) = 950.4 mg/m3

Assessment factors as described above. ECHA assessment factors were used.

Calculation oral DNEL long-term, systemic

The subchronic oral toxicity test (Bechtel, 1990) conducted in male and female Sprague-Dawley rats was used as a starting point for the DNEL derivation.

90d NOAEL (rat) = 1093 mg/kg bw.d

No modification of starting point required. Inter-species extrapolation: rat-human; (4 * 2.5 = 10)

general population NOAEL - oral (human): (1093 mg/ kg bw.d : (4 * 2,5)) = 109.3 mg/kg bw.d

Assessment factors as described above. ECHA assessment factors were used.

Calculation dermal DNEL long-term, local

The subacute dermal toxicity test (21d) conducted in male and female rabbits (read-across from TBBS) was used as a starting point for the DNEL derivation.

21d NOAEL (rabbit) = 500 mg / kg bw (read-across from TBBS)

correction to appropriate unit:

* mean weight (males and females, throughout whole study): ca. 2,650 kg

* exposed area: 10 x 10 cm = 100 cm2

corrected NOAEL = 13,25 mg/cm2

Assessment factors as described above. ECHA assessment factors were used.

No time-scaling nor assessment factor required for duration of exposure due to the fact that local skin effects typically are mainly concentration-driven. No allometric scaling required for local effects.