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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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:
0.82 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):
75
Dose descriptor starting point:
NOAEL
Value:
25 mg/kg bw/day
Modified dose descriptor starting point:
NOAEC
Value:
61.71 mg/m³
Explanation for the modification of the dose descriptor starting point:

The calculation of the DNEL is based on an oral NOAEL observed in a subacute (28-day) repeated dose oral toxicity study in rats with the test substance (OECD 407; 2007).

To take into account the interspecies difference between the rat and human the no observed adverse effect level (NOAEL) has to be corrected as follows:

Corrected starting point for the inhalative route for workers:

= NOAEL(oral) * (1/0.38 m³/kg bw/day) * (ABSoral-rat/ABSinh-human) * 6.7 m³ (8h) /10 m³ (8h) * (days of exposure per week in rats / days of exposure per week worker)

= 25 mg/kg bw/day * (1/0.38 m³/kg bw/day) * (1/1) * 0.67 m³ * (7/5) = 61.71 mg/m³

(ABSoral-rat = oral absorption in rats, ABSinh-human = inhalation absorption rate in humans)

Correction for relative absorption oral vs. inhalation: 1

In contrast to the recommendations of the ECHA Guidance, a factor of 1 (equal absorption of 100% assumed for the oral and the inhalative route for animals and humans) was included for the extrapolation from oral to inhalation absorption, as there is no valid data suggesting that inhalation leads to higher absorption than oral ingestion (recommendation of the VCI Working group "Toxicology", 2008). Molecules with a molecular weight <500 and a log Kow between 0 and 4 can be assumed to be well absorbed equivalently by the oral and inhalation route. Oral absorption may be reduced for acids and bases depending on their pKa value and their electric charge in the GI tract. More lipophilic substances may be better absorbed in the GI tract due to solubilisation with bile acids, and thus oral absorption may be higher than inhalation absorption (VCI Working group "Toxicology", 2008). Unless valid data suggest that inhalation leads to higher absorption than oral ingestion, equal absorption will be assumed when extrapolating from oral to inhalation route.

Thus, the corrected starting point for workers was 61.71 mg/m³ for inhalation.

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:
The DNEL is 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
AF for intraspecies differences:
5
Justification:
Default AF for workers
AF for the quality of the whole database:
1
Justification:
DNEL is 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:
0.23 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):
300
Dose descriptor starting point:
NOAEL
Value:
25 mg/kg bw/day
Modified dose descriptor starting point:
NOAEL
Value:
70 mg/kg bw/day
Explanation for the modification of the dose descriptor starting point:

The calculation of the DNEL is based on an oral NOAEL observed in a subacute (28-day) repeated dose oral toxicity study in rats with the test substance (OECD 407; 2007).

To take into account the interspecies difference between the rat and human the no observed adverse effect level (NOAEL) has to be corrected as follows:

Corrected starting point for the dermal route for workers:

NOAELcorr = NOAELoral * (ABSoral-rat/ABSdermal-human) * (days of exposure per week in rats / days of exposure per week worker)

= (25 mg/kg bw/day) * (1/0.5) * (7/5) = 70 mg/kg bw/day.

The dermal absorption potential is assumed to be 50%, based on the prediction of low dermal absorption potential.

ABSoral-rat=oral absorption rate in rats, ABSdermal-human=dermal absorption rate in humans.

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:
The DNEL is based on a subacute study
AF for interspecies differences (allometric scaling):
4
Justification:
Default AF for rats
AF for other interspecies differences:
2.5
Justification:
Default AF
AF for intraspecies differences:
5
Justification:
Default AF for workers
AF for the quality of the whole database:
1
Justification:
DNEL is based on a high-quality study
AF for remaining uncertainties:
1
Justification:
No remaining uncertainties
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

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
DNEL related information
Explanation for the modification of the dose descriptor starting point:

There is no potential for exposure of 3,3,4,4,5,5,6,6,7,7,8,8,8-tridecafluorooct-1-ene to consumers and therefore DNELs for consumers were not set.

Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information
Explanation for the modification of the dose descriptor starting point:

There is no potential for exposure of 3,3,4,4,5,5,6,6,7,7,8,8,8-tridecafluorooct-1-ene to consumers and therefore DNELs for consumers were not set.

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
DNEL related information
Explanation for the modification of the dose descriptor starting point:

There is no potential for exposure of 3,3,4,4,5,5,6,6,7,7,8,8,8-tridecafluorooct-1-ene to consumers and therefore DNELs for consumers were not set.

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