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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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:
10.2 mg/m³
Most sensitive endpoint:
repeated dose toxicity
Route of original study:
By inhalation
DNEL related information
DNEL derivation method:
other: substance-specific, see discussion
Overall assessment factor (AF):
33
Dose descriptor starting point:
NOAEC
Value:
620 mg/m³
Modified dose descriptor starting point:
NOAEC
Value:
337.5 mg/m³
Explanation for the modification of the dose descriptor starting point:

The calculation of the DNEL is based on an inhalation NOAEL (600 mg/m³) observed in a repeated dose inhalation toxicity study with a read across substance (OECD 412; 1981).

To correct the interspecies difference between rat and human the no observed effect level has to be corrected as follows:

Corrected starting point for the inhalative route for workers:

= NOAEL(inhalation) * exposure condition rat/exposure condition human

= 620 mg/m³ * (6.5h/day / 8h/day) * (6.7 m³ (8h) / 10 m³ (8h) = 337.5 mg/m³.

AF for dose response relationship:
1
Justification:
study is based on a NOAEL
AF for differences in duration of exposure:
6
Justification:
based on a subacute study
AF for interspecies differences (allometric scaling):
1
Justification:
Interspecies differences were taken into account for the conversion of the rat oral NOAEL into a corrected inhalatory NOAEC considering allometric scaling for the respiratory volumes (modification of the dose descriptor starting point). Thus, no additional AF is applicable.
AF for other interspecies differences:
2.5
Justification:
default
AF for intraspecies differences:
2.2
Justification:
substance-specific, see discussion
AF for the quality of the whole database:
1
Justification:
based on a high-quality study
AF for remaining uncertainties:
1
Justification:
no remaining uncertainties
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:
0.42 mg/kg bw/day
Most sensitive endpoint:
repeated dose toxicity
Route of original study:
Oral
DNEL related information
DNEL derivation method:
other: substance-specific, see discussion
Overall assessment factor (AF):
132
Dose descriptor starting point:
NOAEL
Value:
40 mg/kg bw/day
Modified dose descriptor starting point:
NOAEL
Value:
56 mg/kg bw/day
Explanation for the modification of the dose descriptor starting point:

No data are available for the dermal route. However, reliable data are available for the oral route.

Corrected starting point for the dermal route for workers:

Dermal NOAEL = oral NOAEL*ABS(oral)/ABS(dermal) * (7 days exposure rat/5 days exposure worker) = 40 mg/kg bw/day *(1/1) * 1.4 = 56 mg/kg bw/day. It is assumed that oral and dermal absorption rates are equal.

AF for dose response relationship:
1
Justification:
based on a NOAEL
AF for differences in duration of exposure:
6
Justification:
based on a subacute study
AF for interspecies differences (allometric scaling):
4
Justification:
default value for rat
AF for other interspecies differences:
2.5
Justification:
ECHA default
AF for intraspecies differences:
2.2
Justification:
substance-specific (see discussion)
AF for the quality of the whole database:
1
Justification:
based on high-quality study
AF for remaining uncertainties:
1
Justification:
no remaining uncertainties
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:
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:
DNEL (Derived No Effect Level)
Value:
3.5 mg/m³
Most sensitive endpoint:
repeated dose toxicity
Route of original study:
By inhalation
DNEL related information
DNEL derivation method:
other: substance-specific, see discussion
Overall assessment factor (AF):
48
Dose descriptor starting point:
NOAEL
Value:
620 mg/m³
Modified dose descriptor starting point:
NOAEC
Value:
167.9 mg/m³
Explanation for the modification of the dose descriptor starting point:

The calculation of the DNEL is based on an inhalation NOAEL observed from a subacute repeated dose inhalation study (OECD 412) in rats.

To correct the interspecies difference between rat and human the no observed effect level has to be corrected as follows:

Corrected starting point for the inhalative route for general population:

= NOAELinhalation * exposure conditions rat / exposure conditions human

= 620 mg/m³ * (6.5h/day / 24h/day) = 167.9 mg/m³

AF for dose response relationship:
1
Justification:
The dose descriptor starting point is based on a NOAEL.
AF for differences in duration of exposure:
6
Justification:
based on a subacute study
AF for interspecies differences (allometric scaling):
1
Justification:
AF not used for inhalation route
AF for other interspecies differences:
2.5
Justification:
default
AF for intraspecies differences:
3.2
Justification:
substance-specific, see discussion
AF for the quality of the whole database:
1
Justification:
base on high-quality study
AF for remaining uncertainties:
1
Justification:
no remaining uncertainties
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:
DNEL (Derived No Effect Level)
Value:
0.21 mg/kg bw/day
Most sensitive endpoint:
repeated dose toxicity
Route of original study:
Oral
DNEL related information
DNEL derivation method:
other: substance-specific, see discussion
Overall assessment factor (AF):
192
Dose descriptor starting point:
NOAEL
Value:
40 mg/kg bw/day
Modified dose descriptor starting point:
NOAEL
Value:
40 mg/kg bw/day
Explanation for the modification of the dose descriptor starting point:

No data are available for the dermal route. However, reliable data are available for the oral route.

Corrected starting point for the dermal route for workers:

Dermal NOAEL = oral NOAEL*ABS(oral)/ABS(dermal) = 40 mg/kg bw/day *(1/1) = 40 mg/kg bw/day. It is assumed that oral and dermal absorption rates are equal.

AF for dose response relationship:
1
Justification:
based on a NOAEL
AF for differences in duration of exposure:
6
Justification:
based on a subacute study
AF for interspecies differences (allometric scaling):
4
Justification:
default for rat
AF for other interspecies differences:
2.5
Justification:
default
AF for intraspecies differences:
3.2
Justification:
substance-specific, see discussion
AF for the quality of the whole database:
1
Justification:
based on high-quality data
AF for remaining uncertainties:
1
Justification:
no remaining uncertainties
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:
no hazard identified
Most sensitive endpoint:
sensitisation (skin)
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
Most sensitive endpoint:
skin irritation/corrosion

General Population - Hazard via oral route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
0.21 mg/kg bw/day
Most sensitive endpoint:
repeated dose toxicity
Route of original study:
Oral
DNEL related information
DNEL derivation method:
other: substance-specific, see discussion
Overall assessment factor (AF):
192
Dose descriptor starting point:
NOAEL
Value:
40 mg/kg bw/day
AF for dose response relationship:
1
Justification:
based on a NOAEL
AF for differences in duration of exposure:
6
Justification:
based on a subacute study
AF for interspecies differences (allometric scaling):
4
Justification:
default for rat
AF for other interspecies differences:
2.5
Justification:
default
AF for intraspecies differences:
3.2
Justification:
substance-specific, see discussion
AF for the quality of the whole database:
1
Justification:
based on high quality data
AF for remaining uncertainties:
1
Justification:
no remaining uncertainties
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