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EC number: 277-225-8 | CAS number: 73018-51-6 The complex combination of hydrocarbons obtained by the acid isomerization of linalool. It consists primarily of monoterpenes, terpene alcohols and oxygenated cyclic compounds.
- 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

Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- June-October 2014
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 121 (Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC))
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- HPLC estimation method
- Media:
- soil
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
Not appliable - Radiolabelling:
- no
- Test temperature:
- 30°C
- Details on study design: HPLC method:
- The test system utilized a high performance liquid chromatograph and a cyanopropyl reverse phase HPLC column containing lipophilic and polar moieties. Test item (0.1010 g) was diluted to 100 mL with methanol to give a concentration of 1.01 e3 mg/L. The dead time was determined by measuring the retention time of formamide (purity* 99%, 1.34 x 103 mg/L solution in mobile phase). Solutions of reference standards (see following table) were prepared in either mobile phase (acetanilide to linuron inclusive) or methanol (naphthalene to DDT inclusive).
The HPLC system used was an Agilent Technologies 1200, incorporating autosampler and workstation. The column used was a Waters Xselect HSS Cyano 5 μm (150 x 4.6 mm id). The mobile phase was methanol: water (55:45 v/v). The flow rate was 1.0 mL/min and te injection volume was 25 μL. - Analytical monitoring:
- not required
- Details on sampling:
- Not applicable
- Details on matrix:
- Not applicable
- Details on test conditions:
- Not applicable
- Computational methods:
- Not applicable
- Type:
- log Koc
- Value:
- 2.1 - 3.45
- Temp.:
- 30 °C
- Type:
- Koc
- Value:
- 127 - 2 840
- Temp.:
- 30 °C
- Details on results (HPLC method):
- On analysis, two distinct groups of test item were observed at retention times of approximately 4 and 7.5 minutes. Based on compositional information, these can be tentatively attributed to the cyclic monoterpene ethers and hydrocarbon monoterpenes respectively, due to the more hydrophilic nature of the ether functional groups promoting aqueous solubility and thus mobility in soils.
Based on this tentative assignment, the adsorption coefficient values for the two chemical classes are an adsorption coefficient (Koc) value in the range 127 to 203, log10 Koc 2.10 to 2.31, for the cyclic monoterpene ethers and an adsorption coefficient (Koc) value of 2.84 e3, log10 Koc 3.45, for the hydrocarbon monoterpenes. - Adsorption and desorption constants:
- Not applicable
- Recovery of test material:
- Not applicable
- Concentration of test substance at end of adsorption equilibration period:
- Not applicable
- Concentration of test substance at end of desorption equilibration period:
- Not applicable
- Details on results (Batch equilibrium method):
- Not applicable
- Statistics:
- A calibration curve was constructed from the retention time data of the dead time and reference standard solutions.
The adsorption coefficient log10 Koc values were calculated using the equation below, with reference to the calibration curve.
Log10Koc = (Log10k' - A)/B
where:
Koc = adsorption coefficient
k' = capacity factor
A = intercept of calibration curve
B = slope of the calibration curve - Validity criteria fulfilled:
- yes
- Conclusions:
- The adsorption coefficient values for the two chemical classes are an adsorption coefficient (Koc) value in the range 127 to 203, log10 Koc 2.10 to 2.31, for the cyclic monoterpene ethers and an adsorption coefficient (Koc) value of 2.84 e3, log10 Koc 3.45, for the hydrocarbon monoterpenes.
- Executive summary:
An OECD 121 HPLC test was conducted in order to determine the adsorption coefficient of Lime Oxide.
The test system utilized a high performance liquid chromatograph and a cyanopropyl reverse phase HPLC column containing lipophilic and polar moieties. Test item (0.1010 g) was diluted to 100 mL with methanol to give a concentration of 1.01 x103 mg/L.
On analysis, two distinct groups of test item were observed at retention times of approximately 4 and 7.5 minutes. Based on compositional information, these can be tentatively attributed to the cyclic monoterpene ethers and hydrocarbon monoterpenes respectively, due to the more hydrophilic nature of the ether functional groups promoting aqueous solubility and thus mobility in soils. Based on this tentative assignment, the adsorption coefficient values for the two chemical classes are an adsorption coefficient (Koc) value in the range 127 to 203, log10 Koc 2.10 to 2.31, for the cyclic monoterpene ethers and an adsorption coefficient (Koc) value of 2.84 x103, log10 Koc 3.45, for the hydrocarbon monoterpenes.
Reference
Table 1: HPLC results for test substance
Peak |
Injection |
Retention Time (mins) |
Capacity Factor (k’) |
Log10k’ |
Log10Koc |
Mean Log10Koc |
Adsorption Coefficient |
1 |
1 |
4.010 |
0.888 |
-5.15 x10-2 |
2.11 |
2.10 |
127 |
2 |
4.003 |
0.885 |
-5.32 x10-2 |
2.10 |
|||
2 |
1 |
4.334 |
1.04 |
1.73 x10-2 |
2.31 |
2.31 |
203 |
2 |
4.327 |
1.04 |
1.59 x10-2 |
2.31 |
|||
3 |
1 |
7.466 |
2.52 |
0.401 |
3.45 |
3.45 |
2.84 x103 |
2 |
7.459 |
2.51 |
0.400 |
3.45 |
Description of key information
Key value for chemical safety assessment
- Koc at 20 °C:
- 2 840
Additional information
An OECD 121 HPLC test was conducted in order to determine the adsorption coefficient of Lime Oxide. Two distinct groups of test item were observed at retention times of approximately 4 and 7.5 minutes. Based on compositional information, these can be attributed to the cyclic monoterpene ethers and hydrocarbon monoterpenes respectively. Based on this assignment, the adsorption coefficient (Koc) value for the unsaturated monoterpene hydrocarbons is 2840 (Log Koc 3.445). This value has been assigned to the assessment entity "unsaturated monoterpene hydrocarbons" for the purpose of environmental exposure assessment. It has also been used in the calculation of PNECsediment and soil using the equilibrium partitioning method for this constituent group.
[LogKoc: 3.45]
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