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EC number: 945-883-1 | CAS number: 1379424-11-9
- 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
Hydrolysis
Administrative data
Link to relevant study record(s)
- Endpoint:
- hydrolysis
- Data waiving:
- study scientifically not necessary / other information available
- Justification for data waiving:
- the study does not need to be conducted because the substance is highly insoluble in water
- Justification for type of information:
- In accordance with Annex VIII, column 2, 9.2.2.1 of Regulation (EC) No 1907/2006, a study of Hydrolysis as a funtion of pH dues not need to be conducted as the sbstance is highly insoluble in water.
- Endpoint:
- hydrolysis
- Type of information:
- (Q)SAR
- Adequacy of study:
- supporting study
- Study period:
- December 2018
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model, but not (completely) falling into its applicability domain, with adequate and reliable documentation / justification
- Justification for type of information:
- 1. SOFTWARE
Program HYDROWIN included in EPISUITE (Estimation Programs Interface Suite™ for Microsoft® Windows, v 4.11)
2. MODEL (incl. version number)
The Aqueous Hydrolysis Rate Program (HYDROWIN) estimates aqueous hydrolysis rate constants for the following chemical classes: carboxylic acid esters, carbamates, epoxides, halomethanes, selected alkyl halides and phosphorus esters (under development). The simulated base- or acid-catalyzed rate constants are used to calculate hydrolysis half-lives at selected pHs.
The prediction methodology for esters, carbamates, epoxides, halomethanes and alkyl halides was developed for the Environmental Protection Agency and is outlined in the following document: Mill, T., Haag, W., Penwell, P., Pettit, T. and Johnson, H. "Environmental Fate and Exposure Studies Development of a PC-SAR for Hydrolysis: Esters, Alkyl Halides and Epoxides". EPA Contract No. 68-02-4254: SRI International (1987).
HYDROWIN uses linear free energy relationship (LFER) equations. The Taft equation is used in physical organic chemistry in the study of reaction mechanisms:
Log (ks/kCH3) = (ro*)(sigma*) + (delta)(Es),
where sigma* and Es are Taft constant and steric factor, respectively, ks/kCH3is the ratio of the rate of the substituted reaction compared to the reference reaction, ro* is the sensitivity factor for the reaction to polar effects and delta is the sensitivity factor for the reaction of steric effects. In the special case of benzoic acid derivatives with meta- and para- substituents, the reaction takes the form of the Hammett reaction: Log (ks/kCH3) = (roX)(sigmaX),
where sigmaX is the Hammet constant and roX is the reaction constant. In HYDROWIN, sigmaX-Meta and sigmaX-para Hammet values apply only to a phenyl ring that is attached directly to the ester or carbamate function.
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
DPE777777 (constituent #1): O=C(CCCCCC)OCC(COC(=O)CCCCCC)(COC(=O)CCCCCC)COCC(COC(=O)CCCCCC)(COC(=O)CCCCCC)COC(=O)CCCCCC
DPE777779 (constituent #2):
O=C(CCCCCC)OCC(COC(=O)CCCCCC)(COC(=O)CC(C)CC(C)(C)C)COCC(COC(=O)CCCCCC)(COC(=O)CCCCCC)COC(=O)CCCCCC
DPE777799 (constituent #3):
O=C(CCCCCC)OCC(COC(=O)CCCCCC)(COC(=O)CC(C)CC(C)(C)C)COCC(COC(=O)CCCCCC)(COC(=O)CC(C)CC(C)(C)C)COC(=O)CCCCCC
DPE777999 (constituen #4):
O=C(CCCCCC)OCC(COC(=O)CC(C)CC(C)(C)C)(COC(=O)CC(C)CC(C)(C)C)COCC(COC(=O)CCCCCC)(COC(=O)CC(C)CC(C)(C)C)COC(=O)CCCCCC
DPE779999 (constituent #5):
O=C(CCCCCC)OCC(COC(=O)CC(C)CC(C)(C)C)(COC(=O)CC(C)CC(C)(C)C)COCC(COC(=O)CC(C)CC(C)(C)C)(COC(=O)CC(C)CC(C)(C)C)COC(=O)CCCCCC
DPE799999 (constituent #6):
O=C(CCCCCC)OCC(COC(=O)CC(C)CC(C)(C)C)(COC(=O)CC(C)CC(C)(C)C)COCC(COC(=O)CC(C)CC(C)(C)C)(COC(=O)CC(C)CC(C)(C)C)COC(=O)CC(C)CC(C)(C)C
DPE999999 (constituent #7):
O=C(CC(C)CC(C)(C)C)OCC(COC(=O)CC(C)CC(C)(C)C)(COC(=O)CC(C)CC(C)(C)C)COCC(COC(=O)CC(C)CC(C)(C)C)(COC(=O)CC(C)CC(C)(C)C)COC(=O)CC(C)CC(C)(C)
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
1. Defined endpoint: log Kb – hydrolysis base-catalyzed rate constant
Epoxides: log Ka – hydrolysis acid-catalyzed rate constant.
For all classes: It is assumed that the calculated rate constant is the predominant rate constant and the other rate constants including the neutral rate constant are negligible.
2. Unambiguous algorithm.
Carboxylic acid esters R1-C(=O)-O-R2:
log Kb = 0.92 Es(R1) + 0.31 Es(R2) + 2.16 sigma*(R1) + 2.30 sigma*(R2) + 2.10 sigmaX(R1) + 1.25 sigmaX(R2) + 1.25 sigmaX(R2) + 2.67,
where Es – steric factor at the designated position (R1 or R2), sigma* the Taft constant at R1 or R2, sigmaX the Hammet constant at R1 or R2. A complete list of the parameters is available in the program documentation.
For all classes: HYDROWIN estimates a half-life based upon the total base- or acid-catalyzed rate constant. When a compound contains more than one hydrolysable group, individually estimated rate constants are summed to yield the total rate constant. The half-life for base-catalyzed rate constants is calculated at pH 8 from the following equation:
Half-life = 0.6931 / (Kb)(1.0E-6)
where 1.0E-6 is the concentration in water at pH 8. A half-life at pH 7 is also reported. The half-life for acid-catalyzed rate constants is calculated at pH 7 where both the and H+ concentrations are 1.0E-7. Half-lives at different pHs can be determined simply by moving the half-life decimal point one position right or left for each pH unit change.
3. Applicability domain: Currently there is no universally accepted definition of model domain. Users may wish to consider the possibility that aqueous hydrolysis estimates are less accurate for compounds that have a functional group(s) or other structural features not represented in the training set.
The underlying program methodology is dependent upon accurate values of Taft steric factors, Taft sigma star constants and Hammett sigma constants. HYDROWIN uses a library of 300 fragments for which corresponding values are available. The fragments and values are identified in HYDROWIN’s on-line user guide help file. The library consists primarily of common fragments such as linear alkyl, branched alkyl, cyclo-alkyl, halo-alkyls, phenyl, and common oxygen, nitrogen and sulfur derivatives (such as ethers, thioethers, and alkyl-amines). Realistically, three hundred fragments is only a small fraction of the possible variations of fragments that can exist in chemical structures.
When HYDROWIN identifies a fragment that does not occur in the fragment list, it uses an analogous fragment that is in the list. A warning message is provided. The substitute selected by the program is expected to be the best substitute selection.
4. Appropriate measures of goodness of fit, robustness and predictivity.
Carboxylic acid esters: N = 124 compounds, R2 = 0.965
As yet, the QSAR equations in HYDROWIN have not been rigorously tested with external validation datasets. Currently, the number of chemicals with evaluated hydrolysis rates is relatively small in number, and the available data have been used to train the QSAR regressions.
5. Mechanistic interpretation if possible: The model is developed based on profound knowledge of the different reaction pathways and assigns incremental values that are specific for the mechanism under consideration. The HYDROWIN model uses linear free energy relationship (LFER) equations.
5. APPLICABILITY DOMAIN
The functional groups present in the constituents of the substance (ester groups) are included in the model's dataset. Each constituent has the following generic structure: R1-C(=O)-O-R2
R1 = n-hexyl for the n-heptanoic esters. n-Hexyl fragment is included in the fragment library and therefore its contribution to the calculated log Koc is accurate within the model.
R1 = 3,5,5-trimethyloctyl for the 3,5,5-trimethylhexyl esters. This fragment is not included in the fragment library and iso-Butyl fragment is used instead. The substitute is a shorter carbon chain with less branching.
R2 = DPE pentaester. This fragment is not included in the fragment library and -CH2-(t-Bu) fragment is used instead, which contains the same structure than the DPE actual fragment up to the 3 closest carbon atoms. - Principles of method if other than guideline:
- Calculation based on HYDROWIN v2.00, Estimation Programs Interface Suite™ for Microsoft® Windows v 4.11. US EPA, United States Environmental Protection Agency, Washington, DC, USA.
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- 1.766 yr
- Remarks on result:
- other:
- Remarks:
- constituent #1
- pH:
- 8
- Temp.:
- 25 °C
- DT50:
- 64.5 d
- Remarks on result:
- other:
- Remarks:
- constituent #1
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- 2.011 yr
- Remarks on result:
- other:
- Remarks:
- constituent #2
- pH:
- 8
- Temp.:
- 25 °C
- DT50:
- 73.462 d
- Remarks on result:
- other:
- Remarks:
- constituent #2
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- 2.335 yr
- Remarks on result:
- other:
- Remarks:
- constituent #3
- pH:
- 8
- Temp.:
- 25 °C
- DT50:
- 85.297 d
- Remarks on result:
- other:
- Remarks:
- constituent #3
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- 2.784 yr
- Remarks on result:
- other:
- Remarks:
- constituent #4
- pH:
- 8
- Temp.:
- 25 °C
- DT50:
- 101.679 d
- Remarks on result:
- other:
- Remarks:
- constituent #4
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- 3.446 yr
- Remarks on result:
- other:
- Remarks:
- constitueny #5
- pH:
- 8
- Temp.:
- 25 °C
- DT50:
- 125.849 d
- Remarks on result:
- other:
- Remarks:
- constituent #5
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- 4.52 yr
- Remarks on result:
- other:
- Remarks:
- constituent #6
- pH:
- 8
- Temp.:
- 25 °C
- DT50:
- 165.092 d
- Remarks on result:
- other:
- Remarks:
- constituent #6
- pH:
- 7
- Temp.:
- 25 °C
- DT50:
- 6.568 yr
- Remarks on result:
- other:
- Remarks:
- constituent #7
- pH:
- 8
- Temp.:
- 25 °C
- DT50:
- 239.9 d
- Remarks on result:
- other:
- Remarks:
- constituent #7
- Details on results:
- - Total Kb for pH > 8: 31.244E-001 L/mol-sec
- Temperature for which rate constant was calculated: 25 °C
- Computer programme: HYDROWIN v2.00
- Fragments on this compound are not available from the fragment library. Substitute(s) have been used:
ESTER: R1-C(=O)-O-R2
R1: n-Hexyl-
R2: -CH2-(t-Bu)
Referenceopen allclose all
Description of key information
Due to the chemical structure and the low water solubility (< 0.1 mg/L) of the substance EC 945 -883 -1, hydrolysis does not contribute to abiotic degradation in the aquatic environment.
Key value for chemical safety assessment
Additional information
No experimental studies investigating the abiotic hydrolysis of Dipentaerythritol hexaesters of 3,5,5 -trimethylhexanoic and n-heptanoic acids are available. However, in accordance with Annex VIII, column 2, 9.2.2.1. of Regulation (EC) No 1907/2006, testing is not required since the substance is highly insoluble in water (< 0.1 mg/L).
A supporting QSAR calculation (HYDROWIN v2.00) indicates that hydrolysis is a negligible pathway for the environmental fate of Dipentaerythritol hexaesters of 3,5,5 -trimethylhexanoic and n-heptanoic acids in the environment (DT50 > 1 yr (pH 7).
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.