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EC number: 807-612-4 | CAS number: 1393645-32-3
- 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:
- 23-07-2018 to 24-07-2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Guideline study performed under GLP. All relevant validity criteria were met.
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.19 (Estimation of the Adsorption Coefficient (KOC) on Soil and Sewage Sludge Using High Performance Liquid Chromatography (HPLC))
- Deviations:
- no
- 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
- Type of method:
- HPLC estimation method
- Media:
- soil/sewage sludge
- Radiolabelling:
- no
- Test temperature:
- 35 °C
- Details on study design: HPLC method:
- EQUIPMENT
- Apparatus: Acquity UPLC system.
- Type: Acquity UPLC HSS Cyano, 100 mm x 2.1 mm i.d., dp = 1.8 µm
- Type, material and dimension of analytical (guard) column: None reported.
- Detection system: UV-diode array detection, 210 nm wavelength
MOBILE PHASES
- Type: Methanol : purified water (55:45 v/v) with flow rate 0.4 mL per minute at 35 °C.
- Experiments with additives carried out on separate columns: No
- pH: mobile phase: pH = approximately neutral.
- Solutes for dissolving test and reference substances: None.
DETERMINATION OF DEAD TIME
- Method: The dead time was determined by measuring the retention time of formamide (purity: 99.2%, as certified by supplier), 5 g/L stock solution in methanol diluted into methanol:purified water (55:45 v/v). Determined in duplicate.
REFERENCE SUBSTANCES
- Identity: Acetanilide, CAS 103-84-4, Purity > 99.9%, log Koc 1.26 (OECD Guideline 121)
- Identity: Monuron, CAS 150-68-5, Purity 99.9%, log Koc 1.99 (OECD Guideline 121)
- Identity: 2,5-Dichloroaniline, CAS 95-82-9, Purity 99.9%, log Koc 2.55 (OECD Guideline 121)
- Identity: Naphthalene, CAS 91-20-3, Purity 99.5%, log Koc 2.75 (OECD Guideline 121)
- Identity: Benzoic acid phenylester, CAS 93-99-2, Purity 99.9%, log Koc 2.87 (OECD Guideline 121)
- Identity: Fenthion, CAS 55-38-9, Purity 96.2%, log Koc 3.31 (OECD Guideline 121)
- Identity: Phenanthrene, CAS 85-01-8, Purity 98.1%, log Koc 4.09 (OECD Guideline 121)
- Identity: DDT, CAS 50-29-3, Purity 98.2%, log Koc 5.63 (OECD Guideline 121)
DETERMINATION OF RETENTION TIMES
- Quantity of test substance introduced in the column: 5 μL per injection; an aliquot of test item (13.2 mg/L final concentration) was introduced in duplicate..
- Quantity of reference substances: 5 μL per injection; the concentration of each reference substance injected in duplicate was not reported.
- Intervals of calibration: The calibration was performed once specific for the study; with a range of log Koc suitable for the test item estimation of adsorption to sewage sludge and soil under EU Method C.11 and OECD TG 121 guidelines.
REPETITIONS
- Number of determinations: Two.
EVALUATION
- Calculation of capacity factors k': Calculated as a ratio of retention time of retained compounds relative to unretained substances after determination of the column dead time.
- Calculation of retention times: Determined empirically relative to the known column dead time.
- Determination of the log Koc value: Capacity factors (log k') for reference substances were plotted against absorption coefficients (log Koc). The log Koc for the test item was then calculated using the resultant equation for the calibration curve and the experimentally determined log k'. - Type:
- log Koc
- Value:
- ca. 3.8 dimensionless
- pH:
- 7
- Temp.:
- 35 °C
- Type:
- Koc
- Value:
- ca. 7 000 L/kg
- pH:
- 7
- Temp.:
- 35 °C
- Details on results (HPLC method):
- EVALUATION
- Calculation of capacity factors k': Calculated as a ratio of retention time of retained compounds relative to unretained substances after determination of the column dead time.
- Calculation of retention times: Determined empirically relative to the known column dead time.
- Determination of the log Koc value: Capacity factors (log k') for reference substances were plotted against absorption coefficients (log Koc). The log Koc for the test item was then calculated using the resultant equation for the calibration curve and the experimentally determined log k'.
- Calculation of capacity factors k': Calculated as a ratio of retention time of retained compounds relative to unretained substances after determination of the column dead time.
- Calculation of retention times: Determined empirically relative to the known column dead time.
- Determination of the log Koc value: Capacity factors (log k') for reference substances were plotted against absorption coefficients (log Koc). The log Koc for the test item was then calculated using the resultant equation for the calibration curve and the experimentally determined log k'.
- Retention times of reference substances used for calibration: Reference sample injections completed in duplicate.
- Identity: Acetanilide, CAS 103-84-4, ca. 0.90 min
- Identity: Munuron, CAS 150-68-5, ca. 1.11 min
- Identity: 2,5-Dichloroaniline, CAS 95-829, ca. 1.26 min
- Identity: Naphthalene, CAS 91-20-3, ca. 1.46 min
- Identity: Benzoic acid phenylester, CAS 93-99-2, ca. 1.72min
- Identity: Fenthion, CAS 55-38-9, ca. 2.31 min
- Identity: Phenanthrene, CAS 85-01-8, ca. 2.54 min
- Identity: DDT, CAS 50-29-3, ca. 6.34 min
- Dead-Time: 0.693 minutes
- Details of fitted regression line (log k' vs. log Koc): Linear regression of all reference substances; y = 0.324x – 0.853 , (R = 0.98, n = 16)
- Retention data for test substance: Single peak (main constituent). The average retention time; peak 3: 2.399 minutes (Log Koc = 3.84) - Validity criteria fulfilled:
- yes
- Conclusions:
- The test item adsorption coefficient (log Koc) for soil/sewage sludge according to EU Method C.19 and OECD Guideline 121 was estimated to be log Koc = 3.84 at 35°C by HPLC analysis.
- Executive summary:
The study was performed to EU Method C.19 and OECD TG 121 to assess the adsorption coefficient (Koc) of the test item in accordance with GLP using a high performance chromatography system. The retention times of the test substance and selected reference items were accurately measured using UPLC fitted with a cyanopropyl column. The retention times were consistent over the course of the study. The dead time of the instrument was also measured, and capacity factors were calculated for each reference substance. Calibration curves were constructed by plotting the capacity factor (log k') for the reference substances against their adsorption coefficients (log Koc). Linear regression analysis was performed, and this showed a good relationship between the capacity factors and the adsorption coefficients. The test was performed at a singular approximately neutral pH as the test item does not possess ionisable moieties in an environmentally relevant pH range. The adsorption coefficient of the test item was estimated using the calibration curve constructed from all reference items. Under the conditions of this study, the test item adsorption coefficient (log Koc) for soil/sewage sludge was estimated to be log Koc 3.84 at 35°C and pH 7.0 by UPLC analysis.
Reference
Description of key information
log Koc = 3.84 (Koc 7000 L/kg), 35 °C, ca. pH 7 and 1 atm, EU Method C.19, 2015
Key value for chemical safety assessment
Additional information
Key Study : EU Method C.19, 2015 : The study was performed to EU Method C.19 and OECD TG 121 to assess the adsorption coefficient (Koc) of the test item in accordance with GLP using a high performance chromatography system. The retention times of the test substance and selected reference items were accurately measured using UPLC fitted with a cyanopropyl column. The retention times were consistent over the course of the study. The dead time of the instrument was also measured, and capacity factors were calculated for each reference substance. Calibration curves were constructed by plotting the capacity factor (log k') for the reference substances against their adsorption coefficients (log Koc). Linear regression analysis was performed, and this showed a good relationship between the capacity factors and the adsorption coefficients. The test was performed at a singular approximately neutral pH as the test item does not possess ionisable moieties in an environmentally relevant pH range. The adsorption coefficient of the test item was estimated using the calibration curve constructed from all reference items. Under the conditions of this study, the test item adsorption coefficient (log Koc) for soil/sewage sludge was estimated to be log Koc 3.84 at 35°C and pH 7.0 by UPLC analysis.
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