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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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:
97.95 mg/m³
DNEL related information
Overall assessment factor (AF):
18
Acute/short term exposure
DNEL related information

Local effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
3 mg/m³
Acute/short term exposure
DNEL related information

Workers - Hazard via dermal route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
27.78 mg/kg bw/day
DNEL related information
Overall assessment factor (AF):
72
Modified dose descriptor starting point:
NOAEL
Acute/short term exposure
DNEL related information

Local effects

Acute/short term exposure
Hazard assessment conclusion:
no-threshold effect and/or no dose-response information available

Workers - Hazard for the eyes

Additional information - workers

Long-term exposure - systemic effects

An oral subacute toxicity gavage study of CIBA-GEIGY (1986) with a NOAEL of > 1000 mg/kg/day was available.

 

- Dermal DNEL for long-term exposure - systemic effects

 

For the determination of the dermal DNEL, the NOAEL of 1000 mg/kg bw/day of the rat oral subacute repeated dose study (CIBA-GEIGY, 1986) was used.

 

Due to the very low water solubility below 1 mg/L (< 0.499 mg/L at 20 °C) and the absence of skin irritating and sensitizing effects as well as the dermal toxicity data did indicate very low dermal absorption. Therefore, absorption difference was assessed to 50 % comparing the dermal to the oral route. Accordingly, for dermal exposure the corrected starting point was calculated as 2000 mg/kg body weight / day. Using the overall assessment factor of 72, including assessment factors for interspecies extrapolation of 4 (allometric scaling rat to human), intraspecies extrapolation of 3 for worker according to ECETOC 2003, exposure duration of 6 (sub-acute to chronic) and for remaining factors, dose response and quality of database of 1, respectively, the DNEL (Worker) for dermal exposure was calculated as follows: 2000 mg/kg/day/ (4*3*6*1*1*1) = 27.78 mg/kg body weight /day.

 

- Inhalation DNEL for short-term exposure - systemic effects

 

Based on the same oral subacute study, the endpoint specific DNEL for inhalation repeated-dose toxicity for workers was calculated using a route to route extrapolation.

 

The conversion of the rat oral NOAEL of 1000 mg/kg bw/day to a corrected inhalatory human NOAEL was based on the different respiratory volume of the rat (0.38 m³/kg/day and the different rate during light activity at work (10 m³) and standard conditions (6.7 m³).

 

Corrected NOAEL = 1000 mg/kg * 1/0.38 m³/kg/day * 6.7 m³ (8h) / 10 m³ (8h) = 1763.2 mg/m³/day. Using the overall assessment factor of 18, including assessment factors for intraspecies extrapolation of 3 for worker according to ECETOC 2003, exposure duration of 6 (sub-acute to chronic) and for remaining factors, dose response and quality of database of 1, respectively, the DNEL (Worker) for inhalative exposure was calculated as follows: 1763.2 mg/m³/ (3*6*1*1*1) = 97.95 mg/m³.

The general exposure limit for inhalable dust is applied for local effects.

General Population - Hazard via inhalation route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
20.7 mg/m³
DNEL related information
Overall assessment factor (AF):
30
Acute/short term exposure
DNEL related information

Local effects

Acute/short term exposure
DNEL related information

General Population - Hazard via dermal route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
11.91 mg/kg bw/day
DNEL related information
Overall assessment factor (AF):
120
Modified dose descriptor starting point:
NOAEL
Acute/short term exposure
DNEL related information

General Population - Hazard via oral route

Systemic effects

Long term exposure
Hazard assessment conclusion:
DNEL (Derived No Effect Level)
Value:
5.95 mg/kg bw/day
DNEL related information
Overall assessment factor (AF):
120
Modified dose descriptor starting point:
NOAEL
Acute/short term exposure
DNEL related information

General Population - Hazard for the eyes

Additional information - General Population

Long-term exposure - systemic effects

 

No adverse effects were observed in any study. Based on the available data for 3,6-bis(4-chlorophenyl)-2,5-dihydropyrrolo[3,4-c]pyrrole-1,4-dione (Cas No. 84632-65-5), the endpoint-specific dermal DNEL was calculated using a No-(Adverse)-Effect-Level of > 1000 mg/kg/day determined in an oral subacute toxicity gavage study (CIBA-GEIGY, 1986)

 

- Oral DNEL for long-term exposure - systemic effects

 

Based on the NOAEL of 1000 mg/kg bw/day of the rat oral subacute study, the endpoint specific DNEL for oral repeated-dose toxicity for general population was calculated using the overall assessment factor of 120, including assessment factors for interspecies extrapolation of 4 (allometric scaling rat to human), intraspecies extrapolation of 5 for general polpulation according to ECETOC 2003, exposure duration of 6 (sub-acute to chronic) and for remaining factors, dose response and quality of database of 1, respectively, the DNEL (General population) for oral exposure as follows: 1000 mg/kg/day/ (4*5*6*1*1*1) = 8.33 mg/kg body weight /day.

 

 

- Dermal DNEL for long-term exposure - systemic effects

 

For the determination of the dermal DNEL, the NOAEL of 1000 mg/kg bw/day of the same rat oral subacute repeated dose study (CIBA-GEIGY, 1986) was used.

 

Due to the very low water solubility below 1 mg/L (< 0.499 mg/L at 20 °C) and the failure of skin irritating and sensitizing effects as well as the dermal toxicity data did indicate very low dermal absorption. Therefore, absorption difference was assessed to 50 % comparing the dermal to the oral route. Accordingly, for dermal exposure the corrected starting point was calculated as 2000 mg/kg body weight / day. Using the overall assessment factor of 120, including assessment factors for interspecies extrapolation of 4 (allometric scaling rat to human), intraspecies extrapolation of 5 for general population according to ECETOC 2003, exposure duration of 6 (sub-acute to chronic) and for remaining factors, dose response and quality of database of 1, respectively, the DNEL (general population) for dermal exposure was calculated as follows: 2000 mg/kg/day/ (4*5*6*1*1*1) = 16.67 mg/kg body weight /day.

 

 - Inhalation DNEL for short-term exposure - systemic effects

 

Based on the same oral subacute study, the endpoint specific DNEL for inhalation repeated-dose toxicity for workers was calculated using a route to route extrapolation.

 

The conversion of the rat oral NOAEL of 1000 mg/kg bw/day to a corrected inhalatory human NOAEL was based on the different respiratory volume of the rat (0.38 m³/kg/day and the different rate during light activity at work (10 m³) and standard conditions (6.7 m³).

 

Corrected NOAEL = 1000 mg/kg * 1/0.38 m³/kg/day * 6.7 m³ (8h) / 10 m³ (8h) = 869.6 mg/m³/day. Using the overall assessment factor of 30, including assessment factors for intraspecies extrapolation of 5 for general population according to ECETOC 2003, exposure duration of 6 (sub-acute to chronic) and for remaining factors, dose response and quality of database of 1, respectively, the DNEL (general population) for inhalative exposure was calculated as follows: 869.6 mg/m³/ (5*6*1*1*1) = 28.99 mg/m³.

The general exposure limit for inhalable dust of 3mg/m3 for the respirable fraction is applied to prevent from dust overload effects.