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EC number: 814-155-4 | CAS number: 13188-82-4
- 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
Adsorption / desorption
Administrative data
- Endpoint:
- adsorption / desorption, other
- Remarks:
- adsorption
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Accepted calculation method, substance within applicability domain (or: Accepted calculation method, but substance not within applicability domain of model)
- Justification for type of information:
- 1. SOFTWARE
Estimation Programs Interface (EPI) Suite for Microsoft Windows, v4.11 (US EPA, 2012)
2. MODEL (incl. version number)
KOCWIN v2.00
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
See section 'Test Material'.
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
See section "overall remarks, attachements" for QMRF
5. APPLICABILITY DOMAIN
See field "Executive summary" for QPRF
6. ADEQUACY OF THE RESULT
- The model is scientifically valid (see QMRF).
- The model estimates the KOC for the uncharged molecule at 25 °C; screening information on adsorption (and desorption) is required for substances manufactured or imported in quantities of 10 t/y or more (see also QPRF).
- See QPRF for reliability assessment.
Data source
Referenceopen allclose all
- Reference Type:
- other: EPIWIN calculation
- Title:
- Unnamed
- Year:
- 2 019
- Report date:
- 2019
- Reference Type:
- other: Estimation software
- Title:
- Estimation Programs Interface Suite for Microsoft Windows, v4.11
- Author:
- US-EPA
- Year:
- 2 012
- Bibliographic source:
- United States Environmental Protection Agency, Washington, DC, USA
Materials and methods
- Principles of method if other than guideline:
- KOCWIN (v2.00): estimation using first-order Molecular Connectivity Index (MCI)
- GLP compliance:
- no
- Type of method:
- other: QSAR estimation: KOCWIN v2.00: Koc estimate from MCI
Test material
- Reference substance name:
- (2,2-dimethyl-1,3-dioxolan-4-yl)methyl prop-2-enoate
- EC Number:
- 814-155-4
- Cas Number:
- 13188-82-4
- Molecular formula:
- C9H14O4
- IUPAC Name:
- (2,2-dimethyl-1,3-dioxolan-4-yl)methyl prop-2-enoate
- Test material form:
- liquid
Constituent 1
Study design
- Test temperature:
- 25 °C
Results and discussion
Adsorption coefficientopen allclose all
- Type:
- Koc
- Value:
- 10
- Temp.:
- 25 °C
- Type:
- log Koc
- Value:
- 0.7
- Temp.:
- 25 °C
Any other information on results incl. tables
Copy & paste table with detailed results from KOCWIN output.
Applicant's summary and conclusion
- Executive summary:
QPRF: KOCWIN v2.00 (18 Nov. 2013)
1.
Substance
See “Test material identity”
2.
General information
2.1
Date of QPRF
See “Data Source (Reference)”
2.2
QPRF author and contact details
See “Data Source (Reference)”
3.
Prediction
3.1
Endpoint
(OECD Principle 1)Endpoint
Adsorption to solid phase of soils etc.
Dependent variable
Organic carbon normalised adsorption coefficient (Koc)
3.2
Algorithm
(OECD Principle 2)Model or submodel name
KOCWIN
Model version
v. 2.00
Reference to QMRF
QMRF: Estimation of Soil Adsorption Coefficient using KOCWIN v2.00 (EPI Suite v4.11): MCI methodology
Predicted value (model result)
See “Results and discussion”
Input for prediction
- Chemical structure via CAS number or SMILES
Descriptor values
- MCI (first order molecular connectivity index)
- Correction factors
3.3
Applicability domain
(OECD principle 3)Domains:
1) Molecular weight
(range of test data set: 32.04 to 665.02 g/mol; On-Line KOCWIN User’s Guide, Ch. 6.2.4 Domain)Substance within range (186.21 g/mol)
2) Correction factors: Number of instances of the identified correction factor does not exceed the maximum number as listed in Appendix D (On-Line KOCWIN User’s Guide)
Fulfilled.
3.4
The uncertainty of the prediction
(OECD principle 4)Statistical accuracy for training dataset:
n = 516, r² = 0.916, std. dev. = 0.330, average dev. = 0.263
3.5
The chemical mechanisms according to the model underpinning the predicted result
(OECD principle 5)Adsorption is caused by temporary (reversible) or permanent bonding between the substance and a surface (e.g. due to van der Waals interactions, hydrogen bonding to hydroxyl groups, ionic interactions, covalent bonding, etc.). The organic carbon normalized adsorption coefficient (Koc) is the ratio of a substance concentration sorbed in the organic matter component of soil or sediment to that in the aqueous phase at equilibrium.
MCI methodology: The first-order molecular connectivity index is a measure to describe a variety of properties of chemicals. According to Sabljic (1984; cited in Meylan et al., 1992), the soil sorption potential is highly correlated with the first order MCI. Therefore, it has been used to derive the adsorption coefficient.
References
- US EPA (2012). On-Line KOCWIN User’s Guide.
- Meylan, W., P.H. Howard and R.S. Boethling. 1992. Molecular topology/fragment contribution method for predicting soil sorption coefficients. Environ. Sci. Technol. 26: 1560-1567.
Assessment of estimation domain (molecular weight, fragments, correction factors):
Model: KOCWIN v2.00 MCI & Log Kow method Substance: 2-Propenoic acid, (2,2-dimethyl-1,3-dioxolan-4-yl)methyl ester CAS-#: 13188-82-4 SMILES: CC1(C)OCC(COC(=O)C=C)O1 Molecular weight (g/mol): 186 Log Kow (experimental data): 1,5 Reference: Molecular weight (g/mol) log Kow Minimum Maximum Average Minimum Maximum Training set 32,04 665,02 224,4 -2,11 8,12 Validation set 73,14 504,12 277,8 -5,98 8,68 Assessment of molecular weight Molecular weight within range of training and validation set. Assessment of log Kow (only relevant for log Kow method) Log Kow within range of training and validation set. Appendix D. MCI & Log Kow Correction Factors for 447 Compound Training Set Correction Factor Descriptor Coefficient for Molecular Connectivity Index (MCI) Regression Methodology Coefficient for log Kow Regression Methodology Occurrence No. of instances
of each bond
found for the
current substance(new model) Remark (number of compounds (max per structure) Ether, aliphatic (-C-O-C-) -0,871597 -0,090599 20 2 2 Ester (-C-CO-O-C-) or (HCO-O-C) -1,296957 (a) -0,065594 50 2 1 . (a) Counted up to twice per structure, regardless of number of occurrences. . (b) Either one or both carbons aromatic; if both carbons aromatic, can not be cyclic. . (c) Any nitrogen attached to double bond is not counted; also, carbonyl and thiocarbonyl are not counted as carbons. . (d) This is the only fragment counted, even if other fragments occur. . (e) Not included in regression derivation; estimated from other carbonyl fragments. . (f) Counted only once per structure, regardless of number of occurrences. .
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