Registration Dossier

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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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:
2.96 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):
250
Dose descriptor starting point:
NOAEL
Value:
300 mg/kg bw/day
Modified dose descriptor starting point:
NOAEC
Value:
740 mg/m³
Explanation for the modification of the dose descriptor starting point:

DNEL derivation is based on a 13-week toxicity study by oral administration (7 days per week) to rats (Bentz, 2015). The starting dose for DNEL calculation is a NOAEL of 300 mg/kg/day.

As the MW of BMTP is less than 500 g/mol and the log Kow is between 0 and 4, absorption by the oral and inhalation route was assumed to be equivalent (100%).

The NAEC (8h) derived for workers is 740.1 mg/m3 (300 mg/kg/d x 1/0.38 m3/kg x 6.7 m3/10 m3 x 7/5) after correction for difference between respiratory rates under standard conditions and under conditions of light activity and for workers exposure (5 days per week).

AF for dose response relationship:
1
Justification:
Default (DNEL calculator)
AF for differences in duration of exposure:
2
Justification:
Default (DNEL calculator)
AF for interspecies differences (allometric scaling):
1
Justification:
Default (DNEL calculator)
AF for other interspecies differences:
2.5
Justification:
Default (DNEL calculator)
AF for intraspecies differences:
5
Justification:
Default (DNEL calculator)
AF for the quality of the whole database:
10
Justification:
An additional AF of 10 is used to take into account the difference of sensitivity of a repeated dose toxicity study compared to an EOGRTS (OECD 443) to assess for the reproductive / developmental toxicity
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:
0.84 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):
1 000
Dose descriptor starting point:
NOAEL
Value:
300 mg/kg bw/day
Modified dose descriptor starting point:
NOAEL
Value:
840 mg/kg bw/day
Explanation for the modification of the dose descriptor starting point:

DNEL derivation is based on a 13-week toxicity study by oral administration (7 days per week) to rats (Bentz, 2015). The starting dose for DNEL calculation is a NOAEL of 300 mg/kg/day.

According to the available toxocological data, the dermal absorption of BMTP seems lower than the oral absorption. For the purpose of the DNEL derivation, the dermal absorption is estimated to be 50% of the oral absorption.

After correction for dermal absorption and for workers exposure (5 days per week) the NAEC is 840 mg/kg/d (300 mg/kg/d x 100/50 x 7/5).

AF for dose response relationship:
1
Justification:
Default (DNEL calculator)
AF for differences in duration of exposure:
2
Justification:
Default (DNEL calculator)
AF for interspecies differences (allometric scaling):
4
Justification:
Default (DNEL calculator)
AF for other interspecies differences:
2.5
Justification:
Default (DNEL calculator)
AF for intraspecies differences:
5
Justification:
Default (DNEL calculator)
AF for the quality of the whole database:
10
Justification:
An additional AF of 10 is used to take into account the difference of sensitivity of a repeated dose toxicity study compared to an EOGRTS (OECD 443) to assess for the reproductive / developmental toxicity
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:
low hazard (no threshold derived)

Additional information - workers

General Population - Hazard via inhalation route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
0.522 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):
500
Dose descriptor starting point:
NOAEL
Value:
300 mg/kg bw/day
Modified dose descriptor starting point:
NOAEC
Value:
261 mg/m³
Explanation for the modification of the dose descriptor starting point:

DNEL derivation is based on a 13-week toxicity study by oral administration (7 days per week) to rats (Bentz, 2015). The starting dose for DNEL calculation is a NOAEL of 300 mg/kg/day.

As the MW of BMTP is less than 500 g/mol and the log Kow is between 0 and 4, absorption by the oral and inhalation route was assumed to be equivalent.

The NAEC (8h) derived for the general population is 260.9 mg/m3 (300 mg/kg x 1/1.15 m3/kg).

AF for dose response relationship:
1
Justification:
Default (DNEL calculator)
AF for differences in duration of exposure:
2
Justification:
Default (DNEL calculator)
AF for interspecies differences (allometric scaling):
1
Justification:
Default (DNEL calculator)
AF for other interspecies differences:
2.5
Justification:
Default (DNEL calculator)
AF for intraspecies differences:
10
Justification:
Default (DNEL calculator)
AF for the quality of the whole database:
10
Justification:
An additional AF of 10 is used to take into account the difference of sensitivity of a repeated dose toxicity study compared to an EOGRTS (OECD 443) to assess for the reproductive / developmental toxicity
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:
0.3 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):
2 000
Dose descriptor starting point:
NOAEL
Value:
300 mg/kg bw/day
Modified dose descriptor starting point:
NOAEL
Value:
600 mg/kg bw/day
Explanation for the modification of the dose descriptor starting point:

DNEL derivation is based on a 13-week toxicity study by oral administration (7 days per week) to rats (Bentz, 2015). The starting dose for DNEL calculation is a NOAEL of 300 mg/kg/day.

According to the available toxocological data, the dermal absorption of BMTP seems lower than the oral absorption. For the purpose of the DNEL derivation, the dermal absorption is estimated to be 50% of the oral absorption.

After correction for dermal absorption and for workers exposure (5 days per week) the NAEC is 600 mg/kg/d (300 mg/kg/d x 100/50).

AF for dose response relationship:
1
Justification:
Default (DNEL calculator)
AF for differences in duration of exposure:
2
Justification:
Default (DNEL calculator)
AF for interspecies differences (allometric scaling):
4
Justification:
Default (DNEL calculator)
AF for other interspecies differences:
2.5
Justification:
Default (DNEL calculator)
AF for intraspecies differences:
10
Justification:
Default (DNEL calculator)
AF for the quality of the whole database:
10
Justification:
An additional AF of 10 is used to take into account the difference of sensitivity of a repeated dose toxicity study compared to an EOGRTS (OECD 443) to assess for the reproductive / developmental toxicity
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:
0.15 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):
2 000
Dose descriptor starting point:
NOAEL
Value:
300 mg/kg bw/day
Modified dose descriptor starting point:
NOAEL
Value:
300 mg/kg bw/day
Explanation for the modification of the dose descriptor starting point:

DNEL derivation is based on a 13-week toxicity study by oral administration (7 days per week) to rats (Bentz, 2015). The starting dose for DNEL calculation is a NOAEL of 300 mg/kg/day.

AF for dose response relationship:
1
Justification:
Default (DNEL calculator)
AF for differences in duration of exposure:
2
Justification:
Default (DNEL calculator)
AF for interspecies differences (allometric scaling):
4
Justification:
Default (DNEL calculator)
AF for other interspecies differences:
2.5
Justification:
Default (DNEL calculator)
AF for intraspecies differences:
10
Justification:
Default (DNEL calculator)
AF for the quality of the whole database:
10
Justification:
An additional AF of 10 is used to take into account the difference of sensitivity of a repeated dose toxicity study compared to an EOGRTS (OECD 443) to assess for the reproductive / developmental toxicity
Acute/short term exposure
Hazard assessment conclusion:
no hazard identified
DNEL related information

General Population - Hazard for the eyes

Local effects

Hazard assessment conclusion:
low hazard (no threshold derived)

Additional information - General Population