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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Ecotoxicological information

Endpoint summary

Administrative data

Description of key information

Additional information

Short-term toxicity to fish :

Based on the various studies available with Klimish rating 2 for the target substance CAS NO 91-68-9 and read across substances and based on the category approach of organic functional group along with similar mechanistic approach and having structural similarities defined by QSAR toolbox. The results is summarized as follows

 

Sr.No

Endpoint

Effect values

Basis for effects

Duration

Species

Remarks

1

LC50

34.03607mg/l

mortality

48 hrs

Oryzias latipes

Predicted data for target chemical

2

LC50

32.13076mg/l

mortality

48hrs

Pimephales promelas

Predicted data for target chemical

3

LC50

24.43437 mg/l

mortality

96 hrs

Oncorhynchus mykiss

Predicted data for target chemical

4

LC50

17.07mg/l

mortality

96 hrs

Pimephales promelas

Predicted data for target chemical

5

LC50

56.5 mg/l

72.6 mg/l

88.6 mg/l

 

 

mortality

96 hrs

48 hrs

24 hrs

Pimephales promelas

Data from publication for CAS NO 108-46-3

6

LC50

60 mg/l

 

 

mortality

96 hrs

 

Pimephales promelas

Data from publication for CAS NO 108-46-3

 

By applying weight of evidence approach to the studies summarized in the above table it can be observed that the LC50 values was found to be in range of 17.07 to 88.6 mg/l in 96, 48 and 24 hrs on the basis of mortality effect .

But the BCF value of 3-diethylaminophenol reported was not >= 2000 as well as the substance was found to be rapidly degradable

Thus considering the CLP Criteria for aquatic classification of the substance, it is concluded that 3-diethylaminophenol does not exhibit short term toxicity to fish (Oryzias latipes,Pimephales promelas and Oncorhynchus mykiss)

Long-term toxicity to fish :

According to annex IX of column I,Long-term toxicity testing on fish need not to be conducted as it is already provided as part of Annex VIII requirements.Therefore this study was considered for waiver.

Short-term toxicity to aquatic invertebrates :

Based on the various studies available with Klimish rating 2 for target chemical CAS NO 91-68-9 and the read across substances and based on the category approach of organic functional group along with similar mechanistic approach and having structural similarities defined by QSAR toolbox. The results is summarized as follows

 

Sr.No

Endpoint

Effect values

Basis for effects

Duration

Species

Remarks

1

EC50

30.87743 mg/l

mortality

24 hrs

Daphnia magna

Predicted data for target chemical

2

EC50

12.68779mg/L.

 

mortality

48 hrs

Daphnia magna

Predicted data for target chemical

3

LC50

42.2 mg/L.

 

mortality

96 hrs

Palaemonetes pugio

Data from publication for CAS no 108-46-3

4

LT50

>56 mg/L.

 

mortality

96 hrs

Crangon septemspinosa

Data from publication for CAS 108-46-3

 

By applying weight of evidence approach to the studies summarized in the above table it can be observed that EC50 value is expected to be in range of 12 to 42 mg/l and LT50 value was found to be >56 mg/l in a 24 to 96hrs study on the basis of mortality effect. But the BCF value of 3-diethylaminophenol reported was not >= 2000 as well as the substance was found to be rapidly degradable.Thus considering the CLP Criteria for aquatic classification of the substance it is concluded that the substance 3-diethylaminophenol is not toxic to aquatic invertebrate (Daphnia magna, Palaemonetes pugio and Crangon septemspinosa)

Long-term toxicity to aquatic invertebrates :

According to column 1 of Annex IX;Long-term toxicity testing on invertebrate was considered for waiver since the information on acute toxicity has already been provided as a part of Annex VII requirements.

Toxicity to aquatic algae and cyanobacteria :

Based on the various studies available with Klimish rating 2 for the target substance CAS NO 91-68-9 based on the category approach of organic functional group along with similar mechanistic approach and having structural similarities defined by QSAR toolbox. The results is summarized as follows

 

Sr.No

Endpoint

Effect values

Basis for effects

Duration

Species

Remarks

1

EC50

15.0057 mg/l

growth rate

72 hrs

Pseudokirchnerella subcapitata

Predicted data for target chemical

2

EC50

10.75694 mg/l

Cell changes

72 hrs

Pseudokirchnerella subcapitata

Predicted data for target chemical

3

EC50

19.86983mg/l

growth inhibition

N/A

Pseudokirchnerella subcapitata

Data from DEPA

4

EC50

25.321mg/l

no data

96 hrs

green algae

Data from publication form ECOSAR

 

By applying weight of evidence approach to the studies summarized in the above table it can be observed that EC50 value is expected to be in range of10.75694 to25.321 mg/l in 72 hrs to 96 hrs study.

But the BCF value of 3-diethylaminophenol reported was not >= 2000 as well as the substance was found to be rapidly degradable.

Thus considering the CLP Criteria for aquatic classification of the substance , it is concluded that 3-diethylaminophenol does not exhibit toxicity to aquatic algae (green algae, Pseudokirchnerella subcapitata)

Toxicity to microorganisms :

Based on the various studies available with Klimish rating 2 for the target substance CAS NO 91-68-9 and read across substances and based on the category approach of organic functional group along with similar mechanistic approach and having structural similarities defined by QSAR toolbox. The results is summarized as follows

 

Sr.No

Endpoint

Effect values

Basis for effects

Duration

Species

Remarks

1

EC50

187.1003mg/l

growth

12 hrs

Escherichia coli

Predicted data for target chemical

2

IGC50

41.6021 mg/l

growth inhibition

46 hrs

Tetrahymena pyriformis

Data is from DEPA

3

EC50

7.8 mg/l

no data

24 hrs

Nitrosomonas sp.

Data from publication for CAS 108-46-3

4

IC50

1600 mg/l

no data

96 hrs

methanogens

Data from publication for CAS 108-46-3

 

By applying weight of evidence approach to the studies summarized in the above table it can be observed that IC50 value is expected to be in 41.6021 –1600 mg/l and EC50 value was found to be in the range of 7.8 to 187.1003 mg/l in 12 to 96 hrs study