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EC number: 279-420-3 | CAS number: 80206-82-2
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- QSAR prediction:US EPA accepted QSAR method for chemicals properties assessment.
- Qualifier:
- according to guideline
- Guideline:
- other: QSAR model
- Principles of method if other than guideline:
- EPI Suite v 4.0/ECOSARv1.00
- GLP compliance:
- no
- Remarks:
- not applicable. QSAR model
- Analytical monitoring:
- not required
- Vehicle:
- no
- Test organisms (species):
- other: Daphnid species
- Test type:
- other: QSAR model
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Hardness:
- not applicable. QSAR model
- Test temperature:
- not applicable. QSAR model
- pH:
- not applicable. QSAR model
- Dissolved oxygen:
- not applicable. QSAR model
- Salinity:
- not applicable. QSAR model
- Nominal and measured concentrations:
- not applicable. QSAR model
- Details on test conditions:
- CAS Number:80206-82-2
SMILES : CCCCCCCCCCCCO
CHEM : Alcohols, C12-14
MOL FOR: C12 H26 O1
MOL WT : 186.34
Log Kow: 4.77 (KowWin estimate)
Wat Sol: 4 mg/L (experimental database) - Reference substance (positive control):
- not required
- Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 0.446 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: (Q)SAR prediction
- Remarks on result:
- other: non-toxic at the limit of solubility, as determined by (Q)SAR
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 111.5 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: (Q)SAR prediction
- Remarks on result:
- other: Predicted, at an water solubility loading rates of 1000 mg/L
- Details on results:
- The ECOSAR QSAR model predicts that LC50 for fresh water species Daphnid would to be 0.446 mg/l .This result signifies that the test substance is not expected to be toxic at the limit of solubility.This result is above the LoS (limit of solubility), therefore the substance is non-toxic at the limit of LoS and LC50 is >LoS.This is about 250 times the water solubility of the test substance.
A reliable 48 h EC50 value of 111.5 mg/L has been calculated for the effects of the test substance towards Daphnia magna. Therefore the test substance has been predicted to be non toxic at the limit of solubility, so the EC50 is 0.446 mg/L.
The water solubility of the Alcohols, C12-14 is 4.0 mg/l at 1000 mg/L loading rate at 25 degC (experimental database). This is about 250 times the water solubility of the test substance. - Validity criteria fulfilled:
- yes
- Remarks:
- US EPA accepted QSAR method for chemicals properties assessment.
- Conclusions:
- The ECOSAR QSAR model predicts that LC50 for fresh water species Daphnid would to be 0.446 mg/l .This result signifies that the test substance is not expected to be toxic at the limit of solubility.This result is above the LoS (limit of solubility), therefore the substance is non-toxic at the limit of LoS and LC50 is >LoS.This is about 250 times the water solubility of the test substance.
A reliable 48 h EC50 value of 111.5 mg/L has been calculated for the effects of the test substance towards Daphnia magna. Therefore the test substance has been predicted to be non toxic at the limit of solubility, so the EC50 is 0.446 mg/L.
The water solubility of the Alcohols, C12-14 is 4.0 mg/l at 1000 mg/L loading rate at 25 degC (experimental database). This is about 250 times the water solubility of the test substance. - Executive summary:
The ECOSAR QSAR model predicts that LC50 for fresh water species Daphnid would to be 0.446 mg/l .This result signifies that the test substance is not expected to be toxic at the limit of solubility.This result is above the LoS (limit of solubility), therefore the substance is non-toxic at the limit of LoS and LC50 is >LoS.This is about 250 times the water solubility of the test substance.
A reliable 48 h EC50 value of 111.5 mg/L has been calculated for the effects of the test substance towards Daphnia magna. Therefore the test substance has been predicted to be non toxic at the limit of solubility, so the EC50 is 0.446 mg/L.
The water solubility of the Alcohols, C12-14 is 4.0 mg/l at 1000 mg/L loading rate at 25 degC (experimental database). This is about 250 times the water solubility of the test substance.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- QSAR prediction:US EPA accepted QSAR method for chemicals properties assessment.
- Qualifier:
- according to guideline
- Guideline:
- other: QSAR model
- Principles of method if other than guideline:
- EPI Suite v 4.0/ECOSARv1.00
- GLP compliance:
- no
- Remarks:
- not applicable. QSAR model
- Analytical monitoring:
- not required
- Vehicle:
- no
- Test organisms (species):
- other: Mysid shrimp
- Details on test organisms:
- Scientific name: Americamysis bahia
Common name: Opossum shrimp, Mysid shrimp, Mysids - Test type:
- other: QSAR model
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 96 h
- Hardness:
- not applicable. QSAR model
- Test temperature:
- not applicable. QSAR model
- pH:
- not applicable. QSAR model
- Dissolved oxygen:
- not applicable. QSAR model
- Salinity:
- not applicable. QSAR model
- Nominal and measured concentrations:
- not applicable. QSAR model
- Details on test conditions:
- -Name of test material (as cited in study report:Alcohols, C12-14
CAS Number:80206-82-2
SMILES : CCCCCCCCCCCCO
CHEM : Alcohols, C12-14
MOL FOR: C12 H26 O1
MOL WT : 186.34
Log Kow: 4.77 (KowWin estimate)
Wat Sol: 4 mg/L (experimental database) - Reference substance (positive control):
- not required
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 0.073 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: (Q)SAR prediction
- Remarks on result:
- other: non-toxic at the limit of solubility, as determined by (Q)SAR
- Duration:
- 96 h
- Dose descriptor:
- LC50
- Effect conc.:
- 18.25 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: (Q)SAR prediction
- Remarks on result:
- other: Predicted, at water solubility loading rates of 1000 mg/L
- Details on results:
- The ECOSAR QSAR model predicts that LC50 for fresh water species Mysid shrimp would to be 0.073 mg/l .This result signifies that the test substance is not expected to be toxic at the limit of solubility. This result is above the LoS (limit of solubility), therefore the substance is non-toxic at the limit of LoS and LC50 is >LoS.
A 96 h LC50 value of 0.073 mg/L has been calculated for the effects of the test substance on the mortality of the Mysid shrimp. This result signifies that the test substance is not expected to be toxic at the limit of solubility. This result is above the LoS (limit of solubility), therefore the substance is non-toxic at the limit of LoS and LC50 is >LoS.
A reliable 96 h LC50 value of 18,25 mg/L has been calculated for the effects of the test substance towards Mysid shrimp. Therefore the test substance has been predicted to be non toxic at the limit of solubility, so the LC50 is 0.073 mg/L. Predicted to be non-toxic at the limit of solubility. - Validity criteria fulfilled:
- yes
- Remarks:
- US EPA accepted QSAR method for chemicals properties assessment.
- Conclusions:
- The ECOSAR QSAR model predicts that LC50 for fresh water species Mysid shrimp would to be 0.073 mg/l .This result signifies that the test substance is not expected to be toxic at the limit of solubility. This result is above the LoS (limit of solubility), therefore the substance is non-toxic at the limit of LoS and LC50 is >LoS.
A 96 h LC50 value of 0.073 mg/L has been calculated for the effects of the test substance on the mortality of the Mysid shrimp. This result signifies that the test substance is not expected to be toxic at the limit of solubility. This result is above the LoS (limit of solubility), therefore the substance is non-toxic at the limit of LoS and LC50 is >LoS.
A reliable 96 h LC50 value of 18.25 mg/L has been calculated for the effects of the test substance towards Mysid shrimp. Therefore the test substance has been predicted to be non toxic at the limit of solubility, so the LC50 is 0.073 mg/L. Predicted to be non-toxic at the limit of solubility. - Executive summary:
- The ECOSAR QSAR model predicts that LC50 for fresh water species Mysid
shrimp would to be 0.073 mg/l .This result signifies that the test
substance is not expected to be toxic at the limit of solubility. This
result is above the LoS (limit of solubility), therefore the substance is
non-toxic at the limit of LoS and LC50 is >LoS. A 96 h LC50 value of 0.073
mg/L has been calculated for the effects of the test substance on the
mortality of the Mysid shrimp. This result signifies that the test
substance is not expected to be toxic at the limit of solubility. This
result is above the LoS (limit of solubility), therefore the substance is
non-toxic at the limit of LoS and LC50 is >LoS. A reliable 96 h LC50 value
of 18,25 mg/L has been calculated for the effects of the test substance
towards Mysid shrimp. Therefore the test substance has been predicted to
be non toxic at the limit of solubility, so the LC50 is 0.073 mg/L.
Predicted to be non-toxic at the limit of solubility.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Qualifier:
- according to guideline
- Guideline:
- other: EU guideline 92/69/EWG
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Details on sampling:
- MONITORING OF TEST SUBSTANCE CONCENTRATION:
Yes (fluid chromatography of dichloromethane extract)
Measured concentrations of C12-FA and C14-FA were between
0.003 and 0.011 mg/l at 48 hours for 10 and 100 mg/l dose groups. - Vehicle:
- not specified
- Details on test solutions:
- STOCK AND TEST SOLUTION AND THEIR PREPARATION
Test medium: Water accommodated fractions
Vehicle, solvent: Not reported
DILUTION WATER
Source: Not reported
Alkalinity: Not reported
Hardness: Not reported
Conductance: Not reported - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISMS
Strain: Daphnia magna
Supplier: BioInternational B.V., NJ Horn, NL
Age: 6-24 hours old
Feeding: Green algae 6hours prior to testing
Pretreatment: M4 medium / 20oC / 16h light - 8h dark
Feeding during test: No feeding according to EU guideline - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Test temperature:
- 20.8-20.9 degC
- pH:
- pH mean: 7.9
- Dissolved oxygen:
- Dissolved oxygen: 98.8%
- Nominal and measured concentrations:
- Measured concentrations of C12-FA and C14-FA were between 0.003 and 0.011 mg/l at 48 hours for 10 and 100 mg/l dose groups.
Nominal test concentrations were 1, 3, 10, 30, and 100 mg/L. - Details on test conditions:
- TEST SYSTEM
Loading rates: 0, 1, 3, 10, 30, and 100 mg/l
Exposure vessel type: 100 ml flasks
Number of replicates: 2
Invertebrate per replicate: 10
Test temperature: 20.8-20.9 C
Dissolved oxygen: 98.8%
pH mean: 7.9
Intensity of irradiation: approx. 900 lux
Photoperiod: 16 hours light/ 8 hours darkness
TEST PARAMETER: Immobilization - Reference substance (positive control):
- no
- Duration:
- 48 h
- Dose descriptor:
- EL50
- Effect conc.:
- 63 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: non-toxic at the limit of solubility
- Duration:
- 48 h
- Dose descriptor:
- EL0
- Effect conc.:
- 30 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: non-toxic at the limit of solubility
- Duration:
- 48 h
- Dose descriptor:
- EL100
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Remarks on result:
- other: non-toxic at the limit of solubility
- Details on results:
- RESULTS: EXPOSED
EL0 30 mg/l
EL50 63 mg/l
EL100 >100 mg/l
Based on nominal loading rates
RESULTS: CONTROL
Number/% showing adverse effects: 0 - Validity criteria fulfilled:
- yes
- Conclusions:
- A 48h EL50 value of 63 mg/L has been determined for the effects of Alcohols, C12-14 on the mobility of Daphnia magna. The EL50 was obtained at a concentration above the Limit of Solubility (LoS) . The water solubility of Alcohols, C12-14 is 4.0 mg/L at 25oC .Therefore the EL50 value is >4.0 mg/L (>LoS), i.e. the test substance was not toxic at the LoS.
- Executive summary:
A 48h EL50 value of 63 mg/L has been determined for the effects of Alcohols, C12-14 on the mobility of Daphnia magna. The EL50 was obtained at a concentration above the Limit of Solubility (LoS) . The water solubility of Alcohols, C12-14 is 4.0 mg/L at 25oC . Therefore the EL50 value is >4.0 mg/L (>LoS), i.e. the test substance was not toxic at the LoS.
Referenceopen allclose all
Overview of QSARs estimations on short-term aquatic toxicity of Alcohols, C12-14
to Daphnid
Method
|
Results |
Remarks |
Reference |
QSAR estimate |
Daphnid , 48-hr LC50 =0.446 mg/L (ppm)
Daphnid, 30-day, ChV (chronic value) = 0.080 mg/L (ppm)
|
Reliable with restrictions, QSAR estimated data |
ECOSAR Program (v1.00) |
Using the EPIWIN ECOSAR QSAR model aLC50 for fresh water Daphnid of 0.446mg/l was established.
Daphnid , 48-hr LC50 =0.446 mg/L (ppm)
Daphnid, 30-day, ChV (chronic value) = 0.080 mg/L (ppm
This result signifies that the test substance is not expected to be toxic at the limit of solubility.This result is above the LoS (limit of solubility), therefore the substance is non-toxic at the limit of LoS and LC50 is >LoS.This is about 250 times the water solubility of the test substance.
Overview of QSARs estimations on short-term aquatic toxicity of Alcohols, C12 –14 to Mysid shrimp
Method
|
Results |
Remarks |
Reference |
QSAR estimate |
Mysid Shrimp, 96 -hr, LC50= 0.073 mg/L (ppm) Mysid Shrimp (SW), 30-day, ChV (chronic value) = 0.03 mg/L (ppm)
|
Reliable with restrictions, QSAR estimated data |
ECOSAR Program (v1.00) |
Mysid Shrimp, 96 -hr, LC50= 0.073 mg/L (ppm)
Mysid Shrimp (SW), 30-day, ChV (chronic value) = 0.03 mg/L (ppm)
Description of key information
The ECOSAR QSAR model predicts that LC50 for fresh water species Daphnid would to be 0.446 mg/l .This result signifies that the test substance is not expected to be toxic at the limit of solubility.This result is above the LoS (limit of solubility), therefore the substance is non-toxic at the limit of LoS and LC50 is >LoS.This is about 250 times the water solubility of the test substance.
A reliable 48 h EC50 value of 111.5 mg/L has been calculated for the effects of the test substance towards Daphnia magna. Therefore the test substance has been predicted to be non toxic at the limit of solubility, so the EC50 is 0.446 mg/L.
The water solubility of the Alcohols, C12-14 is 4.0 mg/l at 1000 mg/L loading rate at 25 degC (experimental database). This is about 250 times the water solubility of the test substance.
The available data for marine water short-term to aquatic invertebrate are limited and to obtaine the value for PNECs for saltwaters is taken account a assesment factor 10 to extrapolate to LC50 following the “Guidance on Information Requirement and Chemical Safety Assessment R.10: Characterisation of dose [concentration]- response for environment”and “Table R.10-5 Assessment factors proposed for deriving PNEC water for saltwater for different data sets”, to account for the possibility that greater taxonomic diversity in the marine environment makes it likely that some marine taxa may be more sensitive than the most sensitive freshwater taxa.
48-hr LC50(Salt water) = 11.15 mg/L (ppm)
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 111.5 mg/L
Marine water invertebrates
Marine water invertebrates
- Effect concentration:
- 11.15 mg/L
Additional information
The ECOSAR QSAR model predicts that LC50 for fresh water species Daphnid would to be 0.446 mg/l .This result signifies that the test substance is not expected to be toxic at the limit of solubility.This result is above the LoS (limit of solubility), therefore the substance is non-toxic at the limit of LoS and LC50 is >LoS.This is about 250 times the water solubility of the test substance.
A reliable 48 h EC50 value of 111.5 mg/L has been calculated for the effects of the test substance towards Daphnia magna. Therefore the test substance has been predicted to be non toxic at the limit of solubility, so the EC50 is 0.446 mg/L.
The water solubility of the Alcohols, C12-14 is 4.0 mg/l at 1000 mg/L loading rate at 25 degC (experimental database). This is about 250 times the water solubility of the test substance.
The available data for marine water short-term to aquatic invertebrate are limited and to obtaine the value for PNECs for saltwaters is taken account a assesment factor 10 to extrapolate to LC50 following the “Guidance on Information Requirement and Chemical Safety Assessment R.10: Characterisation of dose [concentration]- response for environment”and “Table R.10-5 Assessment factors proposed for deriving PNEC water for saltwater for different data sets”, to account for the possibility that greater taxonomic diversity in the marine environment makes it likely that some marine taxa may be more sensitive than the most sensitive freshwater taxa.
48-hr LC50(Salt water) = 11.15 mg/L (ppm)
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