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EC number: 219-307-8 | CAS number: 2408-20-0
- 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
Toxicity to aquatic algae and cyanobacteria
Administrative data
Link to relevant study record(s)
- Endpoint:
- toxicity to aquatic algae and cyanobacteria
- 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 limited documentation / justification
- Justification for type of information:
- Prediction is done using QSAR Toolbox version 3.3 with log kow as the primary discriptors.
- Qualifier:
- according to guideline
- Guideline:
- other: Predicted data
- Principles of method if other than guideline:
- Prediction is done using QSAR Toolbox version 3.3 with log kow as the primary discriptors.
- GLP compliance:
- no
- Specific details on test material used for the study:
- - Name of the test material: 2-Propenyl Propanoate
- IUPAC name: 2-Propenyl Propanoate
- Molecular formula: C6H10O2
- Molecular weight: 114.143 g/mol
- Substance type: Organic
- Physical State: Liquid
- Smiles: CCC(=O)OCC=C
- InChI: 1S/C6H10O2/c1-3-5-8-6(7)4-2/h3H,1,4-5H2,2H3 - Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- Raphidocelis subcapitata (previous names: Pseudokirchneriella subcapitata, Selenastrum capricornutum)
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 72 h
- Key result
- Duration:
- 72 h
- Dose descriptor:
- EC50
- Effect conc.:
- 189.73 mg/L
- Nominal / measured:
- estimated
- Conc. based on:
- test mat.
- Basis for effect:
- growth rate
- Remarks on result:
- other: NOT TOXIC
- Conclusions:
- Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity on algae was predicted 2-Propenyl Propanoate (CAS: 2408-20-0). Effect concentration i.e EC50 value was estimated to be 189.73 mg/l for Pseudokirchneriella subcapitata for 72 hrs duration. It was concluded that the 2-Propenyl Propanoate (CAS: 2408-20-0) was likely to be not toxic to aquatic algae hence it can be considered to be “not Classified” as per the CLP classification criteria for aquatic environment.
- Executive summary:
Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity on algae was predicted 2-Propenyl Propanoate (CAS: 2408-20-0). Effect concentration i.e EC50 value was estimated to be 189.73 mg/l for Pseudokirchneriella subcapitata for 72 hrs duration. It was concluded that the 2-Propenyl Propanoate (CAS: 2408-20-0) was likely to be not toxic to aquatic algae hence it can be considered to be “not Classified” as per the CLP classification criteria for aquatic environment.
Reference
The
prediction was based on dataset comprised from the following
descriptors: EC50
Estimation method: Takes average value from the 5 nearest neighbours
Domain logical expression:Result: In Domain
(((((((((((("a"
or "b" or "c" or "d" )
and ("e"
and (
not "f")
)
)
and ("g"
and (
not "h")
)
)
and ("i"
and (
not "j")
)
)
and ("k"
and (
not "l")
)
)
and "m" )
and "n" )
and ("o"
and (
not "p")
)
)
and "q" )
and ("r"
and (
not "s")
)
)
and "t" )
and ("u"
and "v" )
)
Domain
logical expression index: "a"
Referential
boundary: The
target chemical should be classified as Esters (Acute toxicity) by
US-EPA New Chemical Categories
Domain
logical expression index: "b"
Referential
boundary: The
target chemical should be classified as SN2 AND SN2 >> SN2 Reaction at a
sp3 carbon atom AND SN2 >> SN2 Reaction at a sp3 carbon atom >>
Activated alkyl esters and thioesters by Protein binding by OASIS v1.3
Domain
logical expression index: "c"
Referential
boundary: The
target chemical should be classified as SN2 AND SN2 >> SN2 reaction at
sp3 carbon atom AND SN2 >> SN2 reaction at sp3 carbon atom >> Allyl
acetates and related chemicals by Protein binding by OECD
Domain
logical expression index: "d"
Referential
boundary: The
target chemical should be classified as Esters AND Vinyl/Allyl Esters by
Aquatic toxicity classification by ECOSAR
Domain
logical expression index: "e"
Referential
boundary: The
target chemical should be classified as No alert found by DNA binding by
OECD
Domain
logical expression index: "f"
Referential
boundary: The
target chemical should be classified as Acylation OR Acylation >>
Isocyanates and Isothiocyanates OR Acylation >> Isocyanates and
Isothiocyanates >> Isocyanates OR Michael addition OR Michael addition
>> P450 Mediated Activation to Quinones and Quinone-type Chemicals OR
Michael addition >> P450 Mediated Activation to Quinones and
Quinone-type Chemicals >> Arenes OR Michael addition >> Polarised
Alkenes-Michael addition OR Michael addition >> Polarised
Alkenes-Michael addition >> Alpha, beta- unsaturated esters OR SN1 OR
SN1 >> Carbenium Ion Formation OR SN1 >> Carbenium Ion Formation >>
Alpha halo ethers (including alpha halo thioethers) OR SN1 >> Iminium
Ion Formation OR SN1 >> Iminium Ion Formation >> Aliphatic tertiary
amines OR SN2 OR SN2 >> Direct Acting Epoxides and related OR SN2 >>
Direct Acting Epoxides and related >> Epoxides by DNA binding by OECD
Domain
logical expression index: "g"
Referential
boundary: The
target chemical should be classified as Not possible to classify
according to these rules by DPRA Cysteine peptide depletion
Domain
logical expression index: "h"
Referential
boundary: The
target chemical should be classified as High reactive OR High reactive
>> Activated haloarenes OR High reactive >> alpha,beta-carbonyl
compounds with polarized multiple bonds OR High reactive >> Thiols OR
Low reactive OR Low reactive >> Alicyclic ketones by DPRA Cysteine
peptide depletion
Domain
logical expression index: "i"
Referential
boundary: The
target chemical should be classified as Non binder, non cyclic structure
by Estrogen Receptor Binding
Domain
logical expression index: "j"
Referential
boundary: The
target chemical should be classified as Moderate binder, OH grooup OR
Non binder, impaired OH or NH2 group OR Non binder, MW>500 OR Non
binder, without OH or NH2 group OR Weak binder, OH group by Estrogen
Receptor Binding
Domain
logical expression index: "k"
Referential
boundary: The
target chemical should be classified as Not possible to classify
according to these rules (GSH) by Protein binding potency
Domain
logical expression index: "l"
Referential
boundary: The
target chemical should be classified as Highly reactive (GSH) OR Highly
reactive (GSH) >> Alkyl 2-chloroacetoacetates (SN2) OR Highly reactive
(GSH) >> Miscellaneous Alkyl 2-halo alkenoates (SN2) by Protein binding
potency
Domain
logical expression index: "m"
Referential
boundary: The
target chemical should be classified as No superfragment by
Superfragments ONLY
Domain
logical expression index: "n"
Referential
boundary: The
target chemical should be classified as Class 3 (unspecific reactivity)
by Acute aquatic toxicity classification by Verhaar (Modified) ONLY
Domain
logical expression index: "o"
Referential
boundary: The
target chemical should be classified as Esters AND Vinyl/Allyl Esters by
Aquatic toxicity classification by ECOSAR
Domain
logical expression index: "p"
Referential
boundary: The
target chemical should be classified as Halo Ester by Aquatic toxicity
classification by ECOSAR
Domain
logical expression index: "q"
Referential
boundary: The
target chemical should be classified as Very fast by Bioaccumulation -
metabolism half-lives ONLY
Domain
logical expression index: "r"
Referential
boundary: The
target chemical should be classified as No alert found by
Carcinogenicity (genotox and nongenotox) alerts by ISS
Domain
logical expression index: "s"
Referential
boundary: The
target chemical should be classified as alpha,beta-unsaturated aliphatic
alkoxy group (Genotox) OR Structural alert for genotoxic carcinogenicity
by Carcinogenicity (genotox and nongenotox) alerts by ISS
Domain
logical expression index: "t"
Similarity
boundary:Target:
CCC(=O)OCC=C
Threshold=20%,
Dice(Atom centered fragments)
Atom type; Count H attached; Hybridization
Domain
logical expression index: "u"
Parametric
boundary:The
target chemical should have a value of log Kow which is >= 1.01
Domain
logical expression index: "v"
Parametric
boundary:The
target chemical should have a value of log Kow which is <= 2.18
Description of key information
Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity on algae was predicted 2-Propenyl Propanoate (CAS: 2408-20-0). Effect concentration i.e EC50 value was estimated to be 189.73 mg/l for Pseudokirchneriella subcapitata for 72 hrs duration. It was concluded that the 2-Propenyl Propanoate (CAS: 2408-20-0) was likely to be not toxic to aquatic algae hence it can be considered to be “not Classified” as per the CLP classification criteria for aquatic environment.
Key value for chemical safety assessment
- EC50 for freshwater algae:
- 189.73 mg/L
Additional information
Following studies include the predicted data and experimental study for the target chemical and structurally similar read across to conclude the 2-Propenyl Propanoate (CAS: 2408-20-0) toxicity towards aquatic algae is summarized as follows:
Based on the prediction done using the OECD QSAR toolbox version 3.3 with log kow as the primary descriptor and considering the closest read across substances, the toxicity on algae was predicted 2-Propenyl Propanoate (CAS: 2408-20-0). Effect concentration i.e EC50 value was estimated to be 189.73 mg/l for Pseudokirchneriella subcapitata for 72 hrs duration. It was concluded that the 2-Propenyl Propanoate (CAS: 2408-20-0) was likely to be not toxic to aquatic algae.
The above predicted data is supported by the experimental study of structurally similar read across ethyl butyrate (CAS:105-54-4) from publication Water research, 1980 suggests that the Short term toxicity to Entosiphon Sulcatum study was carried out for 72 hrs. The study was based on the effects of the test compound Ethyl butyrate on Entosiphon Sulcatum in a static fresh water system. Test chemical of known concentration was prepared in sterile double distilled water. For maintenance of the test strain of Entosiphon sulcatum,continuously inoculate the expected required number of stock cultures at 72 h or 96 h intervals. For this, mix 8 ml of stock solution I and 8 ml of sterile double-distilled water in 300 -ml Erlenmeyer flasks stoppered with metal caps and add 2 ml of a stock culture and 2 ml of the adjusted bacterial suspension for Entosiphon stock cultures. Store stock cultures at 25°C. Before inoculation control the flasks containing the stock cultures by means of an inverse microscope. Escherichia coli was used as a feeding material of the test organism Entosiphon sulcatum.
Prepare two parallel dilution series in 300-ml Erlenmeyer flasks stoppered with metal caps. The dilutions will contain 1 part v/v each of pollutant solution in 20to 214partsv/vof mixture. Test vessel contain the known conc. of chemical and test organism. Leave the test culture at 25ᵒC for 72 hrs. Before measurement, control each flask by means of an inverse microscope. Add 10% of a 1.1% NaNO3 solution in double-distilled water filtered through a membrane filter (pore size 0.2/µm), and determine the number of protozoaby means of a cell counter. Pollutant concentrations at which the onset of inhibitory action was observed have been obtained by mathematical evaluation of counts. The term counts corresponds to impulses indicated by the coulter counter. Based on the onset of the inhibitory effect on population of the test organism Entosiphon Sulcatum, the 72 hr LOEC value was determined to be 236 mg/lIt can be conlcuded from the value that the ethyl butyrate is not toxic to the aquatic algae.
Similar experimental study for another structurally similar read across Methyl propionate(CAS; 554-12-1) from publication water research 1990, inidicates that In the Scenedesmus cell multiplication inhibition test, hazardous substances were examined to determine the effect concentrations (EC). The tests were conducted in accordance with the test procedure DIN 38 412, Part 9 (draft standard). The green alga Scenedesmus subspicatus CHODAT was cultivated as the test organism. Decreasing trend of Population changes effect were measured.
The Effective concentration EC50 to 50% of Scenedesmus subspicatus is 500 mg/l. It can be concluded that the Methyl propionate is not toxic to the aquatic algae.
Thus based on the effect concentrations which is in the range 189.73 mg/l to 500 mg/Lgive the conclusion that test substance 2-Propenyl Propanoate (CAS: 2408-20-0) was likely to be not toxic to aquatic algae at environmentally relevant concentrations and applying the weight of evidence approach it can be considered to be“not classified”as per the CLP classification criteria.
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