Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 937-158-3 | CAS number: -
- 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: fish
- 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:
- The substance is a hydrocarbon UVCB. Standard tests for this endpoint are intended for single substances and are not appropriate for this complex substance. However, this endpoint is fulfilled using quantitative structure property relationships for representative hydrocarbon structures. The BCFBAF 3.01 model is a well characterised and generally accepted bioaccumulation prediction model, used by the USEPA, the OECD and recommended by ECHA. The SMILES input data for the BCFBAF 3.01 model is obtained from the PETRORISK Product Library (see OECD QSAR Toolbox report in 'Attached full study report' and PETRORISK report attached in IUCLID section 13).
- Qualifier:
- no guideline required
- Principles of method if other than guideline:
- Software tool(s) used including version: OECD QSAR Toolbox Version 4.4.1
Model(s) used: BCFBAF v3.01 – Arnot-Gobas model which was corrected to 5% lipid content in fish.
The SMILES input data for the BFBAF3.01 model is obtained from the PETRORISK Product Library (see OECD QSAR Toolbox report in ‘Attached full study report’ and PETRORISK report attached in IUCLID section 13). - GLP compliance:
- no
- Remarks:
- (Q)SAR
- Type:
- BCF
- Value:
- >= 4.33 - <= 5 614.57 L/kg
- Remarks on result:
- other: normalized to a 5% lipid content in fish
- Validity criteria fulfilled:
- not applicable
- Conclusions:
- The calculated BCF of this substance ranges from 4.33 - 5614.57 L/kg.
- Executive summary:
The substance is a hydrocarbon UVCB. Standard tests for this endpoint are intended for single substances and are not appropriate for this complex substance. However, this endpoint is fulfilled using quantitative structure property relationships for representative hydrocarbon structures. The BCFBAF 3.01 model is a well characterised and generally accepted bioaccumulation prediction model, used by the USEPA, the OECD and recommended by ECHA. The SMILES input data for the BCFBAF 3.01 model is obtained from the PETRORISK Product Library (see OECD QSAR Toolbox report in 'Attached full study report' and PETRORISK report attached in IUCLID section 13).
The calculated BCF of this substance ranges from 4.33 - 5614.57 L/kg.
- Endpoint:
- bioaccumulation in aquatic species: fish
- Type of information:
- (Q)SAR
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Calculation of bioconcentration factors to determine the potential for bioaccumulation of chemicals is acceptable provided that a recognised and scientifically robust method is used. The TGD includes two methods for calculation of a BCF QSAR depending on the molecular weight and log Kow. This approach is considered to be acceptable with restrictions.
- Justification for type of information:
- A discussion and report on the read across strategy is given as an attachment in IUCLID Section 13.
- Reason / purpose for cross-reference:
- read-across: supporting information
- Principles of method if other than guideline:
- BCFBAF v3.00 in EPI Suite™ (Estimation Program Interface for Windows, version 4.0. Syracuse Research Corporation, Syracuse, NY, USA) U.S. Environmental Protection Agency, OPPT)
- GLP compliance:
- no
- Remarks:
- Calculation
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
No surrogate or analogue material - Radiolabelling:
- no
- Details on sampling:
- Not applicable (calculated data)
- Vehicle:
- no
- Details on preparation of test solutions, spiked fish food or sediment:
- Not applicable (calculated data)
- Test organisms (species):
- other: calculated
- Details on test organisms:
- Not applicable (calculated data)
- Route of exposure:
- other: calculated
- Test type:
- other: calculated
- Hardness:
- Not applicable (calculated data)
- Test temperature:
- Not applicable (calculated data)
- pH:
- Not applicable (calculated data)
- Dissolved oxygen:
- Not applicable (calculated data)
- TOC:
- Not applicable (calculated data)
- Salinity:
- Not applicable (calculated data)
- Details on test conditions:
- Not applicable (calculated data)
- Nominal and measured concentrations:
- Not applicable (calculated data)
- Reference substance (positive control):
- not required
- Details on estimation of bioconcentration:
- BASIS FOR CALCULATION OF BCF
_ Estimation software: BCFBAF v.3.00
_ log Kow used : 11.46 (Petrorisk) - Type:
- BCF
- Value:
- 22 L/kg
- Basis:
- other: calculated
- Details on kinetic parameters:
- Not applicable (calculated data)
- Metabolites:
- Not applicable (calculated data)
- Results with reference substance (positive control):
- Not applicable (calculated data)
- Details on results:
- Log Kow (estimated) : 10.16
Log Kow (experimental): not available from database
Log Kow used by BCF estimates: 11.46 (user entered)
Equation Used to Make BCF estimate:
Log BCF = -0.49 log Kow + 7.554 + Correction
Correction(s): Value
Alkyl chains (8+ -CH2- groups) -0.596
Estimated Log BCF = 1.342 (BCF = 21.98 L/kg wet-wt) - Validity criteria fulfilled:
- not applicable
- Remarks:
- This is a calculated value
- Conclusions:
- The calculated BCF of icosane is 22 L/kg. This value indicates that icosane is not to be considered as a bioaccumulable substance.
- Executive summary:
The QSAR used to calculated the BCF of icosane followed the Reach guidance indications (R7.10.3.2) and so is deemed suitable for the assessment of icosane bioconcentration. The calculated BCF of 22 L/kg indicates that icosane does not belong to bioaccumulable substances.
Referenceopen allclose all
Whole Body Primary Biotransformation Rate Estimate for Fish:
===========================================================
------+-----+--------------------------------------------+---------+---------
TYPE | NUM | LOG BIOTRANSFORMATION FRAGMENT DESCRIPTION | COEFF | VALUE
------+-----+--------------------------------------------+---------+---------
Frag | 2 | Linear C4 terminal chain [CCC-CH3] | 0.0341 | 0.0682
Frag | 2 | Methyl [-CH3] | 0.2451 | 0.4902
Frag | 18 | -CH2- [linear] | 0.0242 | 0.4354
Frag | 1 | N-Alkane (linear) ... < C22 | 0.0000 | 0.0000
L Kow| * | Log Kow = 11.46 (user-entered ) | 0.3073 | 3.5221
MolWt| * | Molecular Weight Parameter | | -0.7246
Const| * | Equation Constant | | -1.5058
============+============================================+=========+=========
RESULT | LOG Bio Half-Life (days) | | 2.2543
RESULT | Bio Half-Life (days) | | 179.6
NOTE | Bio Half-Life Normalized to 10 g fish at 15 deg C |
============+============================================+=========+=========
Biotransformation Rate Constant:
kM (Rate Constant): 0.003859 /day (10 gram fish)
kM (Rate Constant): 0.00217 /day (100 gram fish)
kM (Rate Constant): 0.00122 /day (1 kg fish)
kM (Rate Constant): 0.0006863 /day (10 kg fish)
Arnot-Gobas BCF & BAF Methods (including biotransformation rate estimates):
Estimated Log BCF (upper trophic) = 0.247 (BCF = 1.766 L/kg wet-wt)
Estimated Log BAF (upper trophic) = 3.443 (BAF = 2771 L/kg wet-wt)
Estimated Log BCF (mid trophic) = 0.336 (BCF = 2.168 L/kg wet-wt)
Estimated Log BAF (mid trophic) = 3.138 (BAF = 1375 L/kg wet-wt)
Estimated Log BCF (lower trophic) = 0.365 (BCF = 2.315 L/kg wet-wt)
Estimated Log BAF (lower trophic) = 2.920 (BAF = 831.8 L/kg wet-wt)
Arnot-Gobas BCF & BAF Methods (assuming a biotransformation rate of zero):
Estimated Log BCF (upper trophic) = 0.585 (BCF = 3.842 L/kg wet-wt)
Estimated Log BAF (upper trophic) = 4.176 (BAF = 1.499e+004 L/kg wet-wt)
Description of key information
Hydrocarbons, C17 -C19, n-alkanes, <2% aromatics are hydrocarbon UVCBs. Standard tests for this endpoint are intended for single substances and are not appropriate for this complex substance. However, this endpoint is fulfilled using quantitative structure property relationships for representative hydrocarbon structures. The BCFBAF 3.01 model is a well characterised and generally accepted bioaccumulation prediction model, used by the USEPA, the OECD and recommended by ECHA. The SMILES input data for the BCFBAF 3.01 model is obtained from the PETRORISK Product Library (see OECD QSAR Toolbox report in 'Attached full study report' and PETRORISK report attached in IUCLID section 13).
The calculated BCF of Hydrocarbons, C17 -C19, n-alkanes, <2% aromatics ranges from 4.33 - 5614.57 L/kg.
The BCFWIN v2.16 model within EPISuite 3.12 has been used to estimate the bioaccumulation potential of a number of representative substances. This data is used as a weight of evidence alongside the data reported above.
The calculated BCF of the representative substance icosane is 22 L/kg cacluated by using the BCFWIN v2.16 model within EPISuite 3.12. This value indicates that icosane is not considered a bioaccumulative substance.
Key value for chemical safety assessment
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.
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.