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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 810-260-4 | CAS number: 1115251-57-4
- 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
Partition coefficient
Administrative data
- Endpoint:
- partition coefficient
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- from 10 to 12 July 2012
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The study was reliable with restrictions. Indeed, this study was showed that the alkyl(C10 -13)phenyl)iodonium-ion did not give of signal in the HPLC method, therefore,it was supposed that the result is superior than the range of values obtained.
Cross-referenceopen allclose all
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 012
- Report date:
- 2013
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 117 (Partition Coefficient (n-octanol / water), HPLC Method)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.8 (Partition Coefficient)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- HPLC method
- Partition coefficient type:
- octanol-water
Test material
- Reference substance name:
- 4,4’-Bis[sec-alkyl(C10-C13)phenyl]iodonium tetrakis(pentafluorophenyl)borate
- EC Number:
- 810-260-4
- Cas Number:
- 1115251-57-4
- IUPAC Name:
- 4,4’-Bis[sec-alkyl(C10-C13)phenyl]iodonium tetrakis(pentafluorophenyl)borate
- Test material form:
- other: viscous liquid
- Details on test material:
- - Name of test material (as cited in study report): Bis(alkyl(C10-C13)phenyl)iodonium tetrakis(pentafluorophenyl)borate
- Physical state: clear amber high viscous liquid
- Batch: 11GP0077
- Date of Receipt: 13 February 2012
- Expiration date of the lot/batch: January 2014
- Storage condition of test material: Room temperature, keep away from light
Constituent 1
Study design
- Analytical method:
- high-performance liquid chromatography
Results and discussion
Partition coefficient
- Type:
- log Pow
- Partition coefficient:
- >= 5.241 - <= 6.493
- Temp.:
- 25 °C
- pH:
- >= 5 - <= 6
- Remarks on result:
- other: The log Pow was calculated using peak start and peak end.
- Details on results:
- The test item PI2080 gave one broad peak.. Because of the high peak width, the log Pow of the test item is calculated using peak start and peak end. The log Pow should be regarded as 5.241- 6.493. The peak end lies outside the retention times of the reference items of the reference items, but is used for calculation, because the peak maximum lies in the range of the reference items.
Any other information on results incl. tables
Results:
Reference items:
The retention times which were recorded for the reference items are presented in the following table:
Retention times reference items:
Compound | Retention time mean | K | log Pow | |||
min. | min. | min. | ||||
thio urea | 1.265 | 0 | 0 | |||
Acethophenone | 1.635 | 0.2930 | 1.7 | |||
Naphtalene | 2.694 | 1.1301 | 3.6 | |||
diphenylether | 3.065 | 1.4237 | 4.20 | |||
phenanthrene | 3.905 | 2.0879 | 4.50 | |||
fluoranthene | 4.827 | 2.8171 | 4.70 | |||
thriphenylamine | 6.532 | 4.1650 | 5.70 | |||
DDT | 7.391 | 4.8438 | 6.20 |
Test item PI2080:
Measurement | Retention time (RT) | K | log K | Log Pow | |
peak start | measurement 1 | 5.158 | 3.0785 | 0.4883 | 5.228 |
measurement 2 | 5.220 | 3.1276 | 0.4952 | 5.252 | |
measurement 3 | 5.197 | 3.1094 | 0.4927 | 5.243 | |
mean | 5.241 | ||||
standard deviation | 0.012 | ||||
peak end | measurement 1 | 10.182 | 7.0511 | 0.8483 | 6.519 |
measurement 2 | 9.837 | 6.7783 | 0.8311 | 6.457 | |
measurement 3 | 10.093 | 6.9808 | 0.8439 | 6.503 | |
mean | 10.037 | 6.493 | |||
standard deviation | 0.179 | 0.032 |
log Pow was calculated from the capacity factor as follow: log Pow= (log K + 0.9689)/0.2787
equation of the regression: log k=0.2787 * log Pow-0.9689 with a coefficient of determination r²= 0.9781
Result and validity:
result:
using the correlation log K/ log Pow, the log Pow of the peak of test item PI2080 was calculated as 5.241 -6.493 (peak start and peak end).
Validity:
the validity criteria and results are presented in the following table:
Peak | parameter | Criterion | Found | Assessment |
peak start | range (Max-Min. log Pow) | <0.1 | 0.025 | valid |
value within range of Ref. Items | 1.70 -6.20 | 5.241 | valid | |
peak end | range (Max-Min. log Pow) | <0.1 | 0.061 | valid |
Value within Range of Ref. items | 1.70 -6.20 | 6.493 | not valid* |
* The peak end lies outside the rentention times of the reference times, but is used for evaluation, because the peak maximum lies within the range of the reference items.
Discussion:
Variations in the retention times of reference items and test are very small. Therefore a stable configuration of the HPLC-column can be assumed.
The correlation log K/Log Pow is good: the coefficient of determination r² was calculated with 0.9781. This value was considered as sufficiently high to use the calibration function for the determination of the log Pow of the test item PI2080.
The test item PI2080 gave one broad peak.Because of the high peak width, the log Pow of the test item is calculated using peak start and peak end. The log Pow should be regarded as 5.241- 6.493. The peak end lies outside the retention times of the reference items, but is used for calculation, because the peak maximum lies in the range of the reference items.
It is assumed, that the alkyl(C10 -13)phenyl)iodonium-ion did not give a signal, because this ion was not eluted from several HPLC-columns, filled with C 18 material, using mobile phases 95 % and 100% acetonitrile and 20% tetrahydrofurane/80% methanol, during validation. Therefore the log Pow of this ion should be stated as > 6.2.
Applicant's summary and conclusion
- Conclusions:
- The test item PI2080 gave one broad peak.Because of the high peak width, the loh Pow of the test item is calculated using peak start and peak end. The log Pow should be regarded as 5.241- 6.493.
It is assumed, that the alkyl(C10 -13)phenyl)iodonium-ion did not give a signal, because this ion was not eluted from several HPLC-columns, filled with C 18 material, using mobile phases 95 % and 100% acetonotrile and 20% tetrahydrofurane/80% methanol, during validation. Therefore the log Pow of this ion should be stated as > 6.2. - Executive summary:
This study was performed in order to determine the partition coefficient of the etst item PI2080 using the HPLC method according to OECD 117 and EU A.8 method.
The partition coefficient Pow is defined as the ratio of the equilibrium concentrations of a dissolved substance in a two phase system consisting of two largely immiscible solvents (n-octanol and water). The log Pow is a key parameter in studies of the environnemental fate of chemical substances. A highly significant relationship between the Pow of non-ionised form of substances and their bioaccumulation in fish has been shown. It has also been shown that Pow is a useful parameter in the prediction of adsorption on soil and sediments and for establishing quantitative structure-activity relationships for a wide range of biological effects.
The HPLC method covers log Pow in the range of 0 to 6. Reverse phase HPLC is performed on analytical columns packed with a commercially available solid phase containing long hydrocarbon chains (e;g C8,C18) chemically bound onto silica.
A test item injected on such a column partitions between the mobile solvent phase and the hydrocarbon stationary phase as it is transported along the column by the mobile phase. The test items are retained in proportion to their hydrocarbon-water partition coefficient, with hydrophilic chemicals eluted first and lipophilic chemicals tests. The retention times of the peaks of the test item are compared with retention times of reference substances with khnow hydrocarbon-water partition coefficients.
he test item PI2080 gave one broad peak.Because of the high peak width, the log Pow of the test item is calculated using peak start and peak end. The log Pow should be regarded as 5.241- 6.493.
It is assumed, that the alkyl(C10 -13)phenyl)iodonium-ion did not give a signal, because this ion was not eluted from several HPLC-columns, filled with C 18 material, using mobile phases 95 % and 100% acetonotrile and 20% tetrahydrofurane/80% methanol, during validation. Therefore the log Pow of this ion should be stated as > 6.2.
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.