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EC number: 202-213-6 | CAS number: 93-04-9
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- Experimental test result performed using standard test guidelines
- 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
- Type of method:
- HPLC estimation method
- Media:
- soil/sewage sludge
- Radiolabelling:
- no
- Test temperature:
- 30.0 °C
- Details on study design: HPLC method:
- HPLC Procedure
The solutions of the test substance and reference substances were prepared in solvent. After column saturation with the mobile phase, sequential analysis of thiourea (for dead time: t0), reference substances and test chemical were performed on HPLC at 254 nm. The solutions of the test substance and reference substances were prepared in solvent. In HPLC system, thiourea was injected first, the reference substances were injected, followed by the test chemical solution. All the HPLC runs were performed in duplicates. Retention time tR was measured to calculate the capacity factors k', it was then converted in log to obtain log k'. A standard curve between log k versus log Koc was plotted to obtain the value of log Koc of the test chemical.
EQUIPMENT
- Apparatus: HPLC equipped with Diode Array Detector
- Type, material and dimension of analytical (guard) column: CPS HYPERSIL (CN), 250 mm length x 4.6 mm inner diameter, 5μm particle size)
- Detection system: Diode Array Detector
- Wavelength: UV-254 nm
- Flow rate: 1.00 ml/min
-Injector: Autosampler
- Temperature: 30°C
MOBILE PHASES
- Experiments with additives carried out on separate columns: no
- Type: Methanol: Water, 55:45 (v/v)
- pH: since no additives added, so pH measurement not required for this mobile phase.
REFERENCE SUBSTANCES
- Identity: Acetanilide, Atrazine, Acetophenone, Naphthalene, Methyl Benzoate and Phenanthrene
DETERMINATION OF DEAD TIME
- Method: Dead time was determined by injecting about 100mg/L of thiourea solution in duplicate.
DETERMINATION OF RETENTION TIMES
- Quantity of test substance introduced in the column: 10 µl
- Quantity of reference substances: 10 µl
- Intervals of calibration: Not required
REPETITIONS
- Number of determinations: Duplicates
EVALUATION
- Calculation of capacity factors k': yes
- Calculation of retention times: yes
- Determination of the log Koc value: The adsorption coefficient (Koc) was calculated from the capacity factor (k’) using a calibration plot of log k’ versus log Koc of the selected reference items. - Analytical monitoring:
- not required
- Key result
- Sample No.:
- #1
- Type:
- log Koc
- Value:
- 3.06 dimensionless
- Temp.:
- 30 °C
- Remarks on result:
- other: Koc = 1148.15
- Details on results (HPLC method):
- - Retention times of reference substances used: Retention time of reference substance was determined to be 3.443, 3.520, 3.593, 3.61, 3.95, 4.44 for Acetanilide, Atrazine, Acetophenone, Naphthalene, Methyl Benzoate and Phenanthrene, respectively.
- Details of fitted regression line (log k' vs. log Koc): Log Koc = 3.8721(log k’) + 5.1986 with R2 = 0.977
- Graph of regression line attached: Graph has been attached with this template.
- Average retention data for test substance: 4.06 (retention time) of test chemical.
The Adsorption Coefficient of test chemical was determined as per the HPLC method (OECD Guideline-121). The Log Koc value was determined to be 3.06 dimensionless (Koc = 1148.15) at 30°C.
The Log Koc was calculated for the test item from the capacity factor (k’) using a calibration plot of log k’ versus log Koc of the selected six known reference items.
Regression equation for the compounds analysed was:
Log Koc = 3.8721(log k’) + 5.1986 with R2 = 0.977 - Transformation products:
- not specified
- Validity criteria fulfilled:
- yes
- Conclusions:
- The Adsorption Coefficient of test chemical was determined as per the HPLC method (OECD Guideline-121). The Log Koc value was determined to be 3.06 dimensionless (Koc = 1148.15) at 30°C.
- Executive summary:
The adsorption coefficient Koc in soil and in sewage sludge of test chemical was determined by the High Performance Liquid Chromatographic method according to OECD Guideline No. 121 for testing of Chemicals. The solutions of the test substance and reference substances were prepared in methanol solvent. For the preparation of test solution 10.37 mg of the test item was weighed and transferred into a 10 mL volumetric flask, dissolved and volume was made up to the mark with methanol. 100µl of this solution was pipetted out into vial and 900µl of methanol added to it was shaken well. The concentration of the test chemical solution was 103.7mg/L. After column saturation with the mobile phase, sequential analysis of thiourea (for dead time: t0), reference substances and test chemical were performed on HPLC at 254 nm. In HPLC system, thiourea was injected first, the reference substances were injected, followed by the test chemical solution. The 10ml volume of each was introduced in the column by using autosampler. All the HPLC runs were performed in duplicates. Retention time tR was measured to calculate the capacity factors k', it was then converted in log to obtain log k'. A standard curve between log k versus log Koc was plotted to obtain the value of log Koc of the test chemical. Reference substance taken for study includes Acetanilide, Atrazine, Methyl Benzoate, Naphthalene , Phenanthrene and Acetophenone having log Koc value ranging from 1.25 to 4.09 dimensionless. The Adsorption Coefficient of test chemical was determined as per the HPLC method (OECD Guideline-121). The Log Koc value was determined to be 3.06 dimensionless at 30°C. This log Koc value indicates that the test chemical has a moderate sorption to soil and sediment and therefore have slow migration potential to ground water.
Reference
Result: Determination of log Koc
Determination of Dead Time (t0) | ||||||
Name | Replicate | RT(to)min | Average RT(to)min |
|
|
|
Thiourea | R1 | 3.173 | 3.173 |
|
|
|
R2 | 3.173 |
|
|
| ||
Determination of Retention Time (tR) | ||||||
Name | Replicate | RT(tR)min | k' | log k' | Average | log Koc |
Acetanilide | R1 | 3.427 | 0.0801 | -1.0966 | -1.0858 | 1.25 |
R2 | 3.440 | 0.0841 | -1.0750 | |||
Acetophenone | R1 | 3.520 | 0.1094 | -0.9611 | -0.9611 | 1.26 |
R2 | 3.520 | 0.1094 | -0.9611 | |||
Methyl Benzoate | R1 | 3.593 | 0.1324 | -0.8782 | -0.8782 | 1.80 |
R2 | 3.593 | 0.1324 | -0.8782 | |||
Atrazine | R1 | 3.607 | 0.1368 | -0.8640 | -0.8610 | 1.81 |
R2 | 3.613 | 0.1387 | -0.8580 | |||
Naphthalene | R1 | 3.960 | 0.2480 | -0.6055 | -0.6074 | 2.75 |
R2 | 3.953 | 0.2458 | -0.6094 | |||
Phenanthrene | R1 | 4.707 | 0.4835 | -0.3156 | -0.3148 | 4.09 |
R2 | 4.713 | 0.4853 | -0.3139 | |||
Slope = | 3.8721 | |||||
Intercept = | 5.1986 | |||||
Name | Replicate | RT(tR)min | k' | log k' | log Koc | Average |
Test chemical | R1 | 4.067 | 0.2818 | -0.5501 | 3.07 | 3.06 |
R2 | 4.053 | 0.2773 | -0.5570 | 3.04 |
Description of key information
The adsorption coefficient Koc in soil and in sewage sludge of test chemical was determined by the High Performance Liquid Chromatographic method according to OECD Guideline No. 121 for testing of Chemicals. The solutions of the test substance and reference substances were prepared in methanol solvent. For the preparation of test solution 10.37 mg of the test item was weighed and transferred into a 10 mL volumetric flask, dissolved and volume was made up to the mark with methanol. 100µl of this solution was pipetted out into vial and 900µl of methanol added to it was shaken well. The concentration of the test chemical solution was 103.7mg/L. After column saturation with the mobile phase, sequential analysis of thiourea (for dead time: t0), reference substances and test chemical were performed on HPLC at 254 nm. In HPLC system, thiourea was injected first, the reference substances were injected, followed by the test chemical solution. The 10ml volume of each was introduced in the column by using autosampler. All the HPLC runs were performed in duplicates. Retention time tR was measured to calculate the capacity factors k', it was then converted in log to obtain log k'. A standard curve between log k versus log Koc was plotted to obtain the value of log Koc of the test chemical. Reference substance taken for study includes Acetanilide, Atrazine, Methyl Benzoate, Naphthalene , Phenanthrene and Acetophenone having log Koc value ranging from 1.25 to 4.09 dimensionless. The Adsorption Coefficient of test chemical was determined as per the HPLC method (OECD Guideline-121). The Log Koc value was determined to be 3.06 dimensionless at 30°C. This log Koc value indicates that the test chemical has a moderate sorption to soil and sediment and therefore have slow migration potential to ground water.
Key value for chemical safety assessment
- Koc at 20 °C:
- 1 148.15
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.
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