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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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: 211-779-3 | CAS number: 695-12-5
- 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:
- 2017-10-05 to 2017-12-04
- 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))
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- HPLC estimation method
- Media:
- soil/sewage sludge
- Specific details on test material used for the study:
- SOURCE OF TEST MATERIAL
- Source and lot/batch No. of test material: Vinylcyclohexane (Hydrotox: #17/5598; VUOS: VCH/7/17K1)
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: Fridge at 5°C ± 3°C - Radiolabelling:
- no
- Test temperature:
- HPLC conditions:
Temperature 40°C
Autosampler temperature 25°C - Details on study design: HPLC method:
- EQUIPMENT
- Apparatus: HPLC system Shimadzu LC 2010 (HPLC 11; lD 381) series with an UV-Vis-detector and for the chromatographical separation a Nucleosil 100 CN-column (250x4.6 mm, 5 pm) from Macherey-Nagel were used.
- Chemicals and Reagents: Water, HPLC Grade (18.2 pQ cm'1, Nanopure Diamond); Methanol, HPLC analyzed (J.T. Baker)
- HPLC-Conditions:
Mobile phase = Methanol / HPLC-water (40:60% v/v)
Column = Nucleosil 100 CN, 250x4.6 mm, 5pm
Flow rate = 1.0 mL/min
Temperature = 40 °C
Autosampler temperature = 25°C
Detector = 200 nm
Injection = 20 µl
Runtime = 10 min
DETERMINATION OF DEAD TIME
- Method: The dead time for the calculation was determined with urea
REFERENCE SUBSTANCES
- Identity: Due to the structural differentiation between test item and the reference substances listed in the OECD Guideline 121, six structurally heterogeneous substances were used for the study. The reference substances were prepared by weighing 15 mg of each reference substance in a separated 100 mL volume flask and dissolving in methanol. Accordingly, a 1:50 dilution of each stock solution was prepared with mobile phase.
Reference substances, batch/supplier, and nominal concentration:
> Urea, SZBEO650V/ Sigma Aldrich, 0.003 mg/mL
> Acetanilide, A033682 / Acros, 0.003 mg/mL
> N,N‘-Dimethylbenzamide, L2COP748 / J&K Scientific, 0.003 mg/mL
> lsoproturon, SZBD221XV / Sigma Aldrich, 0.003 mg/mL
> Linuron, BCBSS112V/ Sigma Aldrich, 0.003 mg/mL
> Naphthalene, 137241515 / Roth, 0.003 mg/mL
> Fenthion, BCBT4329 / Sigma Aldrich, 0.003 mg/mL
- Sample Preparation: The test item was prepared by weighing of 200 mg in a 20-mL volume flask, dissolving in methanol and a 1:20 dilution with mobile phase.
- Data Handling: All chromatographic data were collected by using LabSolutions chromatographic software, which enables conformity to 21 CFR Part 11 guidelines. The method and the sequence file were constructed and downloaded prior to the injection of the first sample. The capacity factors were calculated by the formula given in OECD Guideline 121. For calculation of the log Koc value of the test item a calibration curve of the logarithms of the adsorption coefficients over the logarithms of capacity factors of the reference substances was plotted and the linear regression (R220.95) assigned. The calculation of the sample adsorption coefficients was performed using Excel. The results for the adsorption coefficients of vinylcyclohexane are given with two decimal places.
The determinations should be run at least in duplicate. The values of log Koc derived from individual measurements should be within a range 0f 0.25 log unit. Reference substances may be injected as a mixed standard to determine their retention times, provided it has been confirmed that the retention time of each reference standard is unaffected by the presence of the other reference standards.
REPETITIONS
- Number of determinations: 2
EVALUATION
- Calculation of capacity factors k': The capacity factor k‘ was calculated by the formula given in OECD Guideline 121:
k’ =(tR —t0) / t0
k’ = capacity factor
tR = HPLC retention time of test and reference substance (minutes)
t0 = HPLC dead time (minutes)
- Determination of the log Koc value: For calculation of the log Koc value of the test item a calibration curve of the logarithms of the adsorption coefficients over the logarithms of capacity factors of the reference substances was plotted and the linear regression (R2 ≥ 0.95) was assigned.
From this follows:
log Koc = a * log k’+b
b = slope of the calibration curve
a = intercept with the axis
log KOC = logarithm of adsorption coefficient - Key result
- Type:
- log Koc
- Value:
- 2.29 dimensionless
- Matrix:
- soil
- Key result
- Type:
- log Koc
- Value:
- 2.55 dimensionless
- Matrix:
- Sewage sludge
- Details on results (HPLC method):
- - Retention times of reference substances used for calibration:
[substance: first measurement, second measurement]
Urea (dead time): 3.41 min, 3.40 min
Acetanilide: 4.19 min, 4.19 min
N,N'-Dimethylbenzamide: 4.38 min, 4.38 min
Isoproturon: 5.21 min, 5.21 min
Linuron: 5.71 min, 5.71 min
Naphthalene: 5.98 min, 5.98 min
Fenthion: 7.53 min, 7.53 min
- Details of fitted regression line (log k' vs. log Koc soil, 1st injection):
y = 2.858x + 3.012
R² = 0.951
- Details of fitted regression line (log k' vs. log Koc soil, 2nd injection):
Y = 2.858x + 3.012
R² = 0.951
- Details of fitted regression line (log k' vs. log Koc sewage sludge, 1st injection):
Y = 2.941x + 3.282
R² = 0.925
- Details of fitted regression line (log k' vs. log Koc sewage sludge, 2nd injection):
Y = 2.941x + 3.282
R² = 0.925
- Graph of regression line attached: yes
- Average retention data for test substance: 5.32 min (refer also to table 1: "Results of retention times, capacity factors k’, log k’ and adsorption coefficient for vinylcyclohexane" below) - Validity criteria fulfilled:
- yes
- Conclusions:
- Based on the OECD guideline 121, the adsorption coefficients (Koc) of vinylcyclohexane on soil and on sewage sludge were estimated by using high performance liquid chromatography (HPLC). Due to the structural differentiation between test item and the reference substances listed in the OECD Guideline 121, six structurally heterogeneous substances were used for the study. For the dead time determination urea was used. The proposed method is reproducible and specific. The estimated results for vinylcyclohexane are log Koc, soil = 2.29 and log Koc, sewage sludge = 2.55.
- Executive summary:
To estimate the adsorption of vinylcyclohexane on soil and sewage sludge, an GLP experiment was conducted in accordance with OECD guideline 121. The HPLC method for estimating the adsorption coefficient is carried out on an analytical separation column, which is filled with a commercial cyanophase. This stationary phase allows a similar interaction between polar and nonpolar groups of a molecule like organic matter in soil – sewage matrices. With the gained retention times a relationship between retention and the adsorption coefficient can be established. For each substance the capacity factor is calculated with the retention time. The logarithms of the capacity factors Koc are plotted against the logarithms of the capacity factors k 'and the calibration line is calculated by means of linear regression. The test item was prepared by weighing of 200 mg in a 20-mL volume flask, dissolving in methanol and a 1:20 dilution with mobile phase. The measurements were performed in duplicate.
Vinylcyclohexane was analysed with HPLC-UV/VIS. The adsorption parameters were calculated using the Freudlich adsorption isotherm.
The adsorption log Koc values were 2.29 for soil and 2.55 for sewage sludge.
Results Synopsis:
Soil type: soil and sewage sludge
Log Koc soil: 2.29
Log Koc sewage sludge: 2.55
Study Acceptability: This study is classified as acceptable and satisfies the guideline requirement for an adsorption/desorption study in soil.
Reference
Table 1: Results of retention times, capacity factors k’, log k’ and adsorption coefficient for vinylcyclohexane
Vinylcyclohexane | Retention time tr in min | Capacity factor k´ | log k' | Adsoption coefficient | |
log Koc, soil | log Koc, sewage sludge | ||||
First injection | 5.32 | 0.56 | -0.25 | 2.29 | 2.54 |
Second injection | 5.32 | 0.56 | -0.25 | 2.29 | 2.55 |
Description of key information
Based on the OECD guideline 121, the adsorption coefficients (Koc) of vinylcyclohexane on soil and on sewage sludge were estimated by using high performance liquid chromatography (HPLC). The estimated results for vinylcyclohexane are log Koc, soil = 2.29 and log Koc, sewage sludge = 2.55.
Key value for chemical safety assessment
- Koc at 20 °C:
- 195
Other adsorption coefficients
- Type:
- other: Log Koc, soil
- Value in L/kg:
- 2.29
- at the temperature of:
- 25 °C
Other adsorption coefficients
- Type:
- other: Log Koc, sewage sludge
- Value in L/kg:
- 2.55
- at the temperature of:
- 25 °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.