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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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.
Reaction mass of Terpenes and Terpenoids, turpentine-oil, limonene fraction, 1-methyl-4-(1-methylethenyl)cyclohexene and turpentine-oil beta-pinene fraction terpenes, dimers and Terpenes and Terpenoids, turpentine-oil, limonene fraction, 1-methyl-4-(1-methylethenyl)cyclohexene and turpentine-oil beta-pinene fraction terpenes, trimers
EC number: 947-783-3 | 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
Water solubility
Administrative data
Link to relevant study record(s)
- Endpoint:
- water solubility
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 04 April - 11 December 2017
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.6 (Water Solubility)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 105 (Water Solubility)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 830.7840 (Water Solubility)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- flask method
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source: Provided by the Sponsor
- Batch No.of test material: AN-0400-113
- Expiration date of the lot/batch: 01 January 2019
- Purity: 100%
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: Frozen at approximately -20 °C, under nitrogen, in the dark - Key result
- Water solubility:
- ca. 0 g/L
- Temp.:
- 20 °C
- Remarks on result:
- other: Limit of detection
- Remarks:
- 2.0 x 10^-6 g/L
- Conclusions:
- The water solubility of the test substance, Terpenes and Terpenoids, turpentine-oil, limonene fraction, polymers with 1-methyl-4-(1-methylethenyl)cyclohexene and turpentine-oil β-pinene fraction terpenes, was determined to <4 x10^-6 g/L of solution at a temperature of 20.0°C ± 0.5C.
- Executive summary:
The water solubility of the test substane, Terpenes and Terpenoids, turpentine-oil, limonene fraction, polymers with 1 -methyl-4 -(1 -methylethenyl)cyclohexene and turpentine oil β-pinene fraction terpenes, was determined via the flask method in a process compatible with Method A6 Water Solubility of Commission Regulation (EC) No. 440/2008 (30 May 2008), Method 105 of the OECD Guidelines for Testing of Chemicals (27 July 1995) and Method 830.7840 of the OCSPP Guidelines (March 1998).
In preliminary test, the water solubility of the test material was estimated by specialised software WSKOW. The water solubility was initially carried out via the slow stir procedure, where samples were taken after an equilibration period of at least 30 days. A significant erroneous peak was seen in the chromatography of all the samples at the same retention time as the test substance, therefore it was considered that the test substance may have oxidised during testing. The test was subsequently performed via the flask method with slow shaking (100 rpm) for six days. Mixtures of test material and purified water were added to six separate flasks and then the test material was carefully added to the sufrace of the purified water and the headspace was purged with nitrogen. Once the equilibration period was completed, the samples were clear and colourless with excess test substance present on the surface. The solutions were sampled, whilst avoiding excess test substance prior to filitration through a 0.2 µm Nylon filter. The filtrates were also clear and colourless with no Tyndall beam effect. An instrument response was seen in the solvent blank (hexane) and sample matrix blank (procedural blank) at the approximate retention time of the test substance. The solvent blank response was included in the calibration as a zero concentration point and sample concentrations were corrected for concentration relating to the sample matrix blank. The concentration of the test material in the sample solutions was determined via gas chromatography-mass spectrometry.
The test material produced a spectrum with signficant fragments with a m/z 272, 229 and 119, which were present but not predominant in the mass spectrum of the multiplet. It is therefore thought that these species may have formed during testing via oxidation. The limit of detection was determined to be 2.0 x10^-6 g/L and the water solubility of the test substance was determined to 4 x10^-6 g/L over the concentration range 4.92 x10^-7 - 3.6 x 10^-6 g/L at a temperature of 20.0°C.
Reference
Preliminary test: estimate = 4.97 x 10^-7 g/L at 25°C
Validation
The linearity of the detector response regarding concentration was assessed over th the concentration range: 5.22 x 10^-2 - 10.4 mg/L.
The results were satisfactory with a first order correlation coefficient (r) of 0.999 being obtained.
Recovery of analysis of the sample procedure was assessed at a fortification level of nominally 0.05 mg/L and proved adequate for the test. Concentrations were not corrected for recovery of analysis (Figure 3).
Chromatographic review of the analysis of the flask method showed a broad multiplet peak n all the samples at the approximate retention times expected for the test material. This was seen to correlate with increasing shaking time from Samples 1 -6 and was thought to be due to oxidation of the test material. GC-MS spectral analysis of Sample 6 (Figure 4) was used to obtain a spectrum of this species, which showed a significant broad multiplet from approximately 5.6 -7.5 minutes. The complex spectrum produced has fragments with mass/charge (m/z) ratios of 318, 302, 287, 271, 257, 243 and many others.
Description of key information
The water solubility of the test substane, Terpenes and Terpenoids, turpentine-oil, limonene fraction, polymers with 1 -methyl-4 -(1 -methylethenyl)cyclohexene and turpentine oilβ-pinene fraction terpenes, was determined via the flask method in a process compatible with Method A6 Water Solubility of Commission Regulation (EC) No. 440/2008 (30 May 2008), Method 105 of the OECD Guidelines for Testing of Chemicals (27 July 1995) and Method 830.7840 of the OCSPP Guidelines (March 1998).
In preliminary test, the water solubility of the test material was estimated by specialised software WSKOW. The water solubility was initially carried out via the slow stir procedure, where samples were taken after an equilibration period of at least 30 days. A significant erroneous peak was seen in the chromatography of all the samples at the same retention time as the test substance, therefore it was considered that the test substance may have oxidised during testing. The test was subsequently performed via the flask method with slow shaking (100 rpm) for six days. Mixtures of test material and purified water were added to six separate flasks and then the test material was carefully added to the sufrace of the purified water and the headspace was purged with nitrogen. Once the equilibration period was completed, the samples were clear and colourless with excess test substance present on the surface. The solutions were sampled, whilst avoiding excess test substance prior to filitration through a 0.2 µm Nylon filter. The filtrates were also clear and colourless with no Tyndall beam effect. An instrument response was seen in the solvent blank (hexane) and sample matrix blank (procedural blank) at the approximate retention time of the test substance. The solvent blank response was included in the calibration as a zero concentration point and sample concentrations were corrected for concentration relating to the sample matrix blank. The concentration of the test material in the sample solutions was determined via gas chromatography-mass spectrometry.
The test material produced a spectrum with signficant fragments with a m/z 272, 229 and 119, which were present but not predominant in the mass spectrum of the multiplet. It is therefore thought that these species may have formed during testing via oxidation. The limit of detection was determined to be 2.0 x10^-6 g/L and the water solubility of the test substance was determined to 4 x10^-6 g/L over the concentration range 4.92 x10^-7 - 3.6 x 10^-6 g/L at a temperature of 20.0°C.
Key value for chemical safety assessment
- Water solubility:
- 0.004 mg/L
- at the temperature of:
- 20 °C
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.