Sulfonic acids, petroleum, magnesium salts

Toxicological Summary

Workers - Hazard via inhalation route

Systemic effects

Long term exposure

Hazard assessment conclusion:

DNEL (Derived No Effect Level)

Value:

11.75 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

Modified dose descriptor starting point:

NOAEC

Value:

881.58 mg/m³

Explanation for the modification of the dose descriptor starting point:

Justification for NOAEC ( mg/m3) calculation attached to technical dossier

AF for dose response relationship:

1

Justification:

Table R8-6

AF for differences in duration of exposure:

6

Justification:

Table R8-6

AF for interspecies differences (allometric scaling):

1

Justification:

Allometric scaling is accounted for in NOAEL extrapolation.

AF for intraspecies differences:

5

Justification:

intraspecies – workers Table R8-6

AF for the quality of the whole database:

1

Justification:

Table R8-6

AF for remaining uncertainties:

2.5

Justification:

Table R8-6

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:

3.33 mg/kg bw/day

Most sensitive endpoint:

repeated dose toxicity

Route of original study:

Dermal

DNEL related information

DNEL derivation method:

ECHA REACH Guidance

Overall assessment factor (AF):

300

Modified dose descriptor starting point:

NOAEL

Value:

1 000 mg/kg bw/day

AF for dose response relationship:

1

Justification:

Table R8-6

AF for differences in duration of exposure:

6

Justification:

Table R8-6

AF for interspecies differences (allometric scaling):

4

Justification:

Table R8-3

AF for intraspecies differences:

5

Justification:

Table R8-6

AF for the quality of the whole database:

1

Justification:

Table R8-6

AF for remaining uncertainties:

2.5

Justification:

Table R8-6

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

The long term exposure DNELs have all be derived based upon the NOAEL(C) values observed from repeated dose exposure with Assessment Factor based adjustment to make the DNELs appropriate to workers, based on Table R. 8 -6. The dermal DNEL is estimated directly from the available 28 -day repeated dose dermal toxicity data. As the inhlataion data are considered unsafe, however, due to a high proportion of mineral oil mist in the exposure concentration the NOAEL(C) is calculated from the 28 -day repeated dose oral toxicity data.

 

Based on formulae in R. 8-3, as a worst case it is assumed 100% adsorption orally to rats and by inhalation to human. Due to the presence of mineral oil changing the physical state of the substance, granulometry data are not available and deposition in the lungs cannot be determined. Target endpoints are also assumed to be equivalent.

 

For workers (8h exposure/d)

NOAEC (inhal) = 500 * 1/0.38 m3/kg/d * 100/100 * 6.7m3/10m3

NOAEC (inhal) = 881.58 mg/m3

General Population - Hazard via inhalation route

Systemic effects

Long term exposure

Hazard assessment conclusion:

DNEL (Derived No Effect Level)

Value:

2.9 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):

150

Modified dose descriptor starting point:

NOAEC

Value:

434.78 mg/m³

Explanation for the modification of the dose descriptor starting point:

Justification for NOAEC (434.78 mg/m3) calculation attached to technical dossier.

AF for dose response relationship:

1

Justification:

Table R8-6

AF for differences in duration of exposure:

6

Justification:

Table R8-6 subacute to chronic

AF for interspecies differences (allometric scaling):

1

Justification:

Allometric scaling is accounted for in NOAEL extrapolation

AF for intraspecies differences:

10

Justification:

Table R8-6 general population

AF for the quality of the whole database:

1

Justification:

Table R8-6

AF for remaining uncertainties:

2.5

Justification:

Table R8-6

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:

1.667 mg/kg bw/day

Most sensitive endpoint:

repeated dose toxicity

Route of original study:

Dermal

DNEL related information

DNEL derivation method:

ECHA REACH Guidance

Overall assessment factor (AF):

600

Modified dose descriptor starting point:

NOAEL

Value:

1 000 mg/kg bw/day

AF for dose response relationship:

1

Justification:

Table R8-6

AF for differences in duration of exposure:

6

Justification:

Table R8-6

AF for interspecies differences (allometric scaling):

4

Justification:

Table R8-3

AF for intraspecies differences:

10

Justification:

Table R8-6 general population

AF for the quality of the whole database:

1

Justification:

Table R8-6

AF for remaining uncertainties:

2.5

Justification:

Table R8-6

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:

DNEL (Derived No Effect Level)

Value:

0.833 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):

600

Modified dose descriptor starting point:

NOAEL

Value:

500 mg/kg bw/day

AF for dose response relationship:

1

Justification:

Table R8-6

AF for differences in duration of exposure:

6

Justification:

Table R8-6

AF for interspecies differences (allometric scaling):

4

Justification:

Table R8-3

AF for intraspecies differences:

10

Justification:

Table R8-6 general population

AF for the quality of the whole database:

1

Justification:

Table R8-6

AF for remaining uncertainties:

2.5

Justification:

Table R8-6

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

The long term exposure DNELs have all be derived based upon the NOAEL(C) values observed from repeated dose exposure with Assessment Factor based adjustment to make the DNELs appropriate to workers, based on Table R. 8 -6. The dermal DNEL is estimated directly from the available 28 -day repeated dose dermal toxicity data. As the inhlataion data are considered unsafe, however, due to a high proportion of mineral oil mist in the exposure concentration the NOAEL(C) is calculated from the 28 -day repeated dose oral toxicity data.

Based on formulae in R. 8-3, as a worst case it is assumed 100% adsorption orally to rats and by inhalation to human. Due to the presence of mineral oil changing the physical state of the substance, granulometry data are not available and deposition in the lungs cannot be determined. Target endpoints are also assumed to be equivalent.

For general population (24h exposure/d)

NOAEC (inhal) = 500 * 1/1.15 m³/kg/d * 100/100

NOAEC (inhal) = 434.78 mg/m³