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EC number: 202-090-9 | CAS number: 91-68-9
- Life Cycle description
- Uses advised against
- Endpoint summary
- Appearance / physical state / colour
- Melting point / freezing point
- Boiling point
- Density
- Particle size distribution (Granulometry)
- Vapour pressure
- Partition coefficient
- Water solubility
- Solubility in organic solvents / fat solubility
- Surface tension
- Flash point
- Auto flammability
- Flammability
- Explosiveness
- Oxidising properties
- Oxidation reduction potential
- Stability in organic solvents and identity of relevant degradation products
- Storage stability and reactivity towards container material
- Stability: thermal, sunlight, metals
- pH
- Dissociation constant
- Viscosity
- Additional physico-chemical information
- Additional physico-chemical properties of nanomaterials
- Nanomaterial agglomeration / aggregation
- Nanomaterial crystalline phase
- Nanomaterial crystallite and grain size
- Nanomaterial aspect ratio / shape
- Nanomaterial specific surface area
- Nanomaterial Zeta potential
- Nanomaterial surface chemistry
- Nanomaterial dustiness
- Nanomaterial porosity
- Nanomaterial pour density
- Nanomaterial photocatalytic activity
- Nanomaterial radical formation potential
- Nanomaterial catalytic activity
- Endpoint summary
- Stability
- Biodegradation
- Bioaccumulation
- Transport and distribution
- Environmental data
- Additional information on environmental fate and behaviour
- Ecotoxicological Summary
- Aquatic toxicity
- Endpoint summary
- Short-term toxicity to fish
- Long-term toxicity to fish
- Short-term toxicity to aquatic invertebrates
- Long-term toxicity to aquatic invertebrates
- Toxicity to aquatic algae and cyanobacteria
- Toxicity to aquatic plants other than algae
- Toxicity to microorganisms
- Endocrine disrupter testing in aquatic vertebrates – in vivo
- Toxicity to other aquatic organisms
- Sediment toxicity
- Terrestrial toxicity
- Biological effects monitoring
- Biotransformation and kinetics
- Additional ecotoxological information
- Toxicological Summary
- Toxicokinetics, metabolism and distribution
- Acute Toxicity
- Irritation / corrosion
- Sensitisation
- Repeated dose toxicity
- Genetic toxicity
- Carcinogenicity
- Toxicity to reproduction
- Specific investigations
- Exposure related observations in humans
- Toxic effects on livestock and pets
- Additional toxicological data
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
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