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Diss Factsheets
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EC number: 686-241-8 | CAS number: 81058-27-7
- 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
Bioaccumulation: aquatic / sediment
Administrative data
Link to relevant study record(s)
- Endpoint:
- bioaccumulation in aquatic species, other
- Type of information:
- (Q)SAR
- Adequacy of study:
- key study
- Study period:
- 2017
- 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:
- 1. SOFTWARE
On-Line EPI Suite™ User's Guide (v4.00 - v4.11).
2. MODEL (incl. version number)
BCFBAF v3.01. The BCFBAF Program is an update and expansion of the previous BCFWIN Program that was part of the EPI Suite version 3.20.
3. SMILES OR OTHER IDENTIFIERS USED AS INPUT FOR THE MODEL
CC(C)(C)C(=O)OCC1C(C(C(C(O1)Br)OC(=O)C(C)(C)C)OC(=O)C(C)(C)C)OC(=O)C(C)(C)C
4. SCIENTIFIC VALIDITY OF THE (Q)SAR MODEL
- The original estimation methodology used by the original BCFWIN program is described in a document prepared for the U.S. Environmental Protection Agency (Meylan et al., 1997). The estimation methodology was then published in journal article (Meylan et al, 1999).
- The methodology is described in the Bioconcentration Factor Estimation section.
- BCFBAF has been expanded to include estimation of the Biotransformation Rate (kM) in fish and estimation of Bioaccumulation Factor (BAF) by the Arnot-Gobas method (Arnot and Gobas, 2003).
- The measured BCF values used in the revised regressions were selected from a quality reviewed BCF database (Arnot and Gobas, 2006); details of the data quality review methods are described in Arnot and Gobas (2006). Single BCF values were selected for each compound (median values were generally selected for compounds with multiple values).
- The BCF values selected for the BCFBAF training and validation datasets are available in Appendix G and via Internet download at:
http://esc.syrres.com/interkow/EpiSuiteData.htm
A substructure searchable version of the data can be downloaded at: http://esc.syrres.com/interkow/EpiSuiteData_ISIS_SDF.htm
5. APPLICABILITY DOMAIN
see QPRF
6. ADEQUACY OF THE RESULT
see QPRF - Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Meylan WM, Howard PH, Boethling RS, Aronson D, Printup H, Gouchie S. Improved Method for Estimating Bioconcentration/Bioaccumulation Factor from Octanol/Water Partition Coefficient. Environ Toxicol Chem. 1999;18:664–672
- GLP compliance:
- no
- Specific details on test material used for the study:
- SMILES: CC(C)(C)C(=O)OCC1C(C(C(C(O1)Br)OC(=O)C(C)(C)C)OC(=O)C(C)(C)C)OC(=O)C(C)(C)C
- Key result
- Type:
- other: log BCF
- Value:
- 4.03 dimensionless
- Basis:
- whole body w.w.
- Calculation basis:
- other: Regression-based method
- Remarks on result:
- other:
- Remarks:
- QSAR predicted value
- Key result
- Type:
- BCF
- Value:
- 10 600 L/kg
- Basis:
- whole body w.w.
- Calculation basis:
- other: Regression-based method
- Remarks on result:
- other:
- Remarks:
- QSAR predicted value
- Details on results:
- For detailed description on the model and its applicability, see QPRF
- Validity criteria fulfilled:
- yes
- Conclusions:
- The BCF for the test substance was estimated using the regression-based method implemented within the BCF/BAF v3.01 of EPI-Suite. The highest BCF value estimated from the Log Kow of 7.2 was 1.06E04 L/kg w/w (BCFBAF v3.01, regression-based method).
Reference
SMILES : CC(C)(C)C(=O)OCC1C(C(C(C(O1)Br)OC(=O)C(C)(C)C)OC(=O)C(C)(C)C)OC(=O)C(
C)(C)C
CHEM :
MOL FOR: C26 H43 Br1 O9
MOL WT : 579.53
--------------------------------- BCFBAF v3.01 --------------------------------
Summary Results:
Log BCF (regression-based estimate): 4.03 (BCF = 1.06e+004 L/kg wet-wt)
Biotransformation Half-Life (days) : 0.0171 (normalized to 10 g fish)
Log BAF (Arnot-Gobas upper trophic): 0.55 (BAF = 3.59 L/kg wet-wt)
=============================
BCF (Bioconcentration Factor):
=============================
Log Kow (estimated) : 5.51
Log Kow (experimental): not available from database
Log Kow used by BCF estimates: 7.20 (user entered)
Equation Used to Make BCF estimate:
Log BCF = -0.49 log Kow + 7.554 + Correction
Correction(s): Value
No Applicable Correction Factors
Estimated Log BCF = 4.026 (BCF = 1.062e+004 L/kg wet-wt)
===========================================================
Whole Body Primary Biotransformation Rate Estimate for Fish:
===========================================================
------+-----+--------------------------------------------+---------+---------
TYPE | NUM | LOG BIOTRANSFORMATION FRAGMENT DESCRIPTION | COEFF | VALUE
------+-----+--------------------------------------------+---------+---------
Frag | 4 | Ester [-C(=O)-O-C] | -0.7605 | -3.0421
Frag | 1 | Aliphatic bromide [-Br] | 0.2734 | 0.2734
Frag | 4 | Carbon with 4 single bonds & no hydrogens | -0.2984 | -1.1937
Frag | 1 | Aliphatic ether [C-O-C] | -0.0232 | -0.0232
Frag | 12 | Methyl [-CH3] | 0.2451 | 2.9413
Frag | 1 | -CH2- [linear] | 0.0242 | 0.0242
Frag | 5 | -CH - [cyclic] | 0.0126 | 0.0630
L Kow| * | Log Kow = 7.20 (user-entered ) | 0.3073 | 2.2129
MolWt| * | Molecular Weight Parameter | | -1.4861
Const| * | Equation Constant | | -1.5371
============+============================================+=========+=========
RESULT | LOG Bio Half-Life (days) | | -1.7675
RESULT | Bio Half-Life (days) | | 0.01708
NOTE | Bio Half-Life Normalized to 10 g fish at 15 deg C |
============+============================================+=========+=========
Biotransformation Rate Constant:
kM (Rate Constant): 25 /day (10 gram fish) **
kM (Rate Constant): 14.06 /day (100 gram fish) **
kM (Rate Constant): 7.906 /day (1 kg fish) **
kM (Rate Constant): 4.446 /day (10 kg fish) **
** Predicted value exceeds theoretical whole body maximum value.
kM (Rate Constant) of 25 /day is recommended/applied for 10 g fish
Arnot-Gobas BCF & BAF Methods (including biotransformation rate estimates):
Estimated Log BCF (upper trophic) = 0.554 (BCF = 3.585 L/kg wet-wt)
Estimated Log BAF (upper trophic) = 0.555 (BAF = 3.586 L/kg wet-wt)
Estimated Log BCF (mid trophic) = 0.666 (BCF = 4.63 L/kg wet-wt)
Estimated Log BAF (mid trophic) = 0.734 (BAF = 5.424 L/kg wet-wt)
Estimated Log BCF (lower trophic) = 0.701 (BCF = 5.018 L/kg wet-wt)
Estimated Log BAF (lower trophic) = 1.442 (BAF = 27.68 L/kg wet-wt)
Arnot-Gobas BCF & BAF Methods (assuming a biotransformation rate of zero):
Estimated Log BCF (upper trophic) = 3.972 (BCF = 9377 L/kg wet-wt)
Estimated Log BAF (upper trophic) = 7.131 (BAF = 1.353e+007 L/kg wet-wt)
Description of key information
The BCF for the test substance was estimated using the regression-based method implemented within the BCF/BAF v3.01 of EPI-Suite. The highest BCF value estimated from the Log Kow of 7.2 was 1.06 E04 L/kg w/w (BCFBAF v3.01, regression-based method).
Key value for chemical safety assessment
- BCF (aquatic species):
- 10 600 L/kg ww
Additional information
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.
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