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EC number: 208-031-3 | CAS number: 506-30-9
- 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 weight of evidence approach the no.of studies were reviewed for short-term toxicity to fish from reliable sources having Klimish rating 2 and 4.
The summary of the results are presented below
Sr. No |
Endpoint |
Value |
Duration |
Basis of effect |
Species |
Sources |
1. |
LC50 |
4.67 mg/L |
96 hr. |
Mortality |
Carassius auratus |
Predicted data from QSAR for CAS : 506-30-9 |
2. |
LC50 |
12 mg/L |
96 hr. |
Mortality |
Oncorhynchus kisutch |
Experimental data for RA CAS : 57-11-4 |
3. |
LC50 |
>5 mg/L |
96 hr. |
Mortality |
Oryzias latipes |
Experimental data from study report for RA CAS : 112-85-6 |
4. |
LC50 |
40 mg/L |
48 hr |
Mortality |
Oryzias latipes |
Experimental data for RA CAS : 8002-13-9 |
Based on the studies summarized in the above table for the target substance Eicosanoic acid and the read across substance,the endpoint value was found to vary between lethal concentration (LC50) = 4.67 mg/L to 40 mg/L in a 48 hrs. to 96 hrs.study on the basis of mortality effect. Based on the LC50 values, the substance may qualify for the aquatic classification.But after compairing with other CLP criteria for BCF and biodegradation it is concluded that Eicosanoic acid does not exhibit short term toxicity to fish (Carassius auratus, Oncorhynchus kisutch and Oryzias latipes) i.e. it is non hazardous to the aquatic environment.
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 to be waived.
Short-term toxicity to aquatic invertebrates
Based on weight of evidence approach the no.of studies were reviewed for short-term toxicity to aquatic invertebrates from reliable sources having Klimish rating 2 and 4.
The summary of the results are presented below
Sr. No |
Endpoint |
Value |
Duration |
Basis of effect |
Species |
Sources |
1. |
LC50 |
5.7 mg/L |
48 hr. |
Mortality |
Daphnia magna |
Predicted data from QSAR for CAS : 506-30-9 |
2. |
EC50 |
1.22 mg/L |
48 hr. |
Immobilization |
Daphnia magna |
Predicted data from QSAR for CAS : 506-30-9 |
3. |
EC50 |
>5 mg/L |
48 hr. |
Immobilization |
Daphnia magna |
Experimental data from study report for RA CAS : 112-85-6 |
4. |
LC50 |
40 mg/L |
3 hr |
Mortality |
Daphnia pulex |
Experimental data for RA CAS : 8002-13-9 |
Based on the studies summarized in the above table for the target substance Eicosanoic acid and the read across substance,the endpoint value was found to vary between lethal concentration (LC50) = 5.7 mg/L to 40 mg/L and effective concentration (EC50) = 1.22 mg/L to >5 mg/L in a 3 hrs. to 48 hrs.study on the basis of mortality and immobilization effect. Based on the LC50 and EC50 values, ,the substance may qualify for the aquatic classification.But after compairing with other CLP criteria for BCF and biodegradation it is concluded that Eicosanoic acid does not exhibit toxicity to aquatic invertebrate (Daphnia magna and Daphnia pulex ) i.e. it is non hazardous to the aquatic environment.
Long-term toxicity to aquatic invertebrates
According to column I of annex IX ; Long-term toxicity testing on invertebrate (species : Daphnia magna) need not to be conducted as it is already provided as a part of Annex VII requirements.Therefore this end point was considered for waiver.
Toxicity to aquatic algae and cyanobacteria
No. of studies were reviewed for toxicity to aquatic algae and cyanobacteria from reliable sources having Klimisch rating 2 and 4.
The summary of the results are presented below
Sr.No |
Endpoint |
Effect values |
Basis for effects |
Duration |
Species |
Sources |
1 |
EC50 |
3.806 mg/L |
Population |
96 hrs. |
Pseudokirchnerella subcapitata |
Predicted data from QSAR for target CAS : 506-30-9 |
2 |
EC50 and |
5 mg/L |
Growth rate |
72 hrs. |
Selenastrum capricornutum (new name: Pseudokirchnerella subcapitata) |
Experimental data from the study report for RA CAS : 112-85-6 |
NOEC |
5 mg/L |
Growth rate |
72 hrs. |
Selenastrum capricornutum (new name: Pseudokirchnerella subcapitata) |
Experimental data from the study report for RA CAS : 112-85-6 |
|
3 |
NOEC |
4.1 mg/L |
Growth rate |
72 hrs. |
Pseudokirchnerella subcapitata |
Experimental data from the study report for RA CAS : 112-85-6 |
Based on the studies summarized in the above table for the target substance Eicosanoic acid and the read across substance,the endpoint value was found to vary between EC50 = 3.806 mg/L to 5 mg/L and NOEC = 4.1 mg/L to 5 mg/L in a 72 hrs. to 96 hrs. study on the basis of growth rate and population effect. Based on the EC50 values ranging from 3.806 mg/L to 5 mg/L,the substance may qualify for the aquatic classification.But after compairing with other CLP criteria for BCF and biodegradation it is concluded that Eicosanoic acid does not exhibit toxicity to algae (Pseudokirchnerella subcapitata) i.e. it is non hazardous to the aquatic environment.
Toxicity to microorganisms
No. of studies were reviewed for toxicity to microorganisms from reliable sources having Klimisch rating 2.
The summary of the results are presented below
Sr.No |
Endpoint |
Effect values |
Basis for effects |
Duration |
Species |
Sources |
1 |
EC50 |
5.85 mg/L |
Population |
24 hr. |
Tetrahymena pyriformis |
Predicted data from QSAR for target CAS : 506-30-9 |
2 |
EC50 |
75.387 mg/L |
- |
15 min. |
Vibrio fisheri |
Experimental data from Environmental Toxicology and Water Quality for RA CAS : 57-10-3 |
Based on the studies summarized in the above table for the target substance Eicosanoic acid and the read across substance, in microorganisms (Tetrahymena pyriformis and Vibrio fisheri),the endpoint value was found to vary between EC50 = 5.85 mg/L to 75.387 mg/L in a 15 min. to 24 hr. study on the basis of population effect.
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