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EC number: 417-440-8 | CAS number: 2516-92-9
- 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
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- comparable to guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 996
- Report date:
- 1996
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar 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:
- not specified
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- HPLC estimation method
- Media:
- soil
Test material
- Reference substance name:
- 1,10-bis(2,2,6,6-tetramethyl-1-piperidinyloxy)-1,10-dioxodecane
- EC Number:
- 417-440-8
- EC Name:
- 1,10-bis(2,2,6,6-tetramethyl-1-piperidinyloxy)-1,10-dioxodecane
- Cas Number:
- 2516-92-9
- Molecular formula:
- C28 H50 N2 O6
- IUPAC Name:
- bis(1-hydroxy-2,2,6,6-tetramethylpiperidin-4-yl) decanedioate
- Details on test material:
- Batch: CXA681901
Constituent 1
- Radiolabelling:
- no
Study design
HPLC method
- Details on study design: HPLC method:
- EQUIPMENT
- Apparatus:
HPLC pump: M 480, from Gynkotek, Munchen, BRD
Degasser: DG-1300, from Gynkotek, Munchen, BRD
Autosampler: Gina M 160, from Gynkotek, Munchen, BRD
Thermostat: MGW Lauda RM 20, from MGW, Lauda-Konigshofen, BRD
Chromatographic data system: PC AT486 with GYNKOSOFT Version 5.50, from Gynkotek, Munchen, BRD
Stationary phase: cyanopropyl (5 pm, Zorbax CN), from VDS Optilab, Berlin, BRD
Injection volume: variable between 10 pl and 200 pl
Flow rate: 1.0 ml/min
Spectrometer: Lambda 5 UV/VIS-Spektrometer (Perkin-Elmer, Uberlingen, BRD)
- Type, material and dimension of analytical (guard) column:
Column thermostat: Cosytherm, from Labor Technik Barkey, Bielefeld, BRD
Column temperature: 40°C
Column dimensions: 250x4.6 mm
- Detection system:
Diode array detector: UVD 320, from Gynkotek, Munchen, BRD
MOBILE PHASES
- Type: not specified
- Experiments with additives carried out on separate columns: no
- pH: 6
- Solutes for dissolving test and reference substances:
methanol: 0.01 mol/l citrate buffer pH 6.0 = 55 : 45 / v:v
DETERMINATION OF DEAD TIME
- Method: by inert substances which are not retained by the column
In this study Forrnamide was used as inert substance.
Preparation of solution: 10.5 mg Formamide were dissolved in 10 ml of methanol. An aliquot of this solution was chromatographed under standard chromatographic conditions and the retention time was determined.
REFERENCE SUBSTANCES
N-Phenylacetamide
Atrazine
Monuron
Triapenthenol
Linuron
Fenthion
Trifluralin
DETERMINATION OF RETENTION TIMES
- Quantity of test substance introduced in the column:
A stock solution of the test substance was prepared by dissolving 10.19 mg in 10 ml of methanol. 490 pl of the stock solution were diluted to 10 ml with methanol.
- Quantity of reference substances:
A stock solution of each reference substance was prepared by dissolving approximately 10 mg in 10 ml of methanol. The stock solutions were diluted 1:100 with methanol.
- Intervals of calibration:
The calibration was performed at regular inten/als in duplicate at least once daily, so that possible changes in column performance could have been allowed for.
REPETITIONS
- Number of determinations: once
EVALUATION
- Calculation of capacity factors k': k' = (tR-tO)/tO.
tR = retention time of test substance or reference substance; tO= column dead time (retention time of formamide)
- Calculation of retention times: measured
- Determination of the log Koc value: Log Koc of the test substance was calculated from the fitted regression line (log k' versus logKoc).
Results and discussion
Adsorption coefficient
- Sample No.:
- #1
- Type:
- log Koc
- Value:
- 3.58 dimensionless
- pH:
- 6
Results: HPLC method
- Details on results (HPLC method):
- - Retention times of reference substances used for calibration:
N-Phenylacetamide: 3.34 min
Atrazine: 3.82 min
Monuron: 3.94 min
Triapenthenol: 4.86 min
Linuron: 5.00 min
Fenthion: 6.65 min
Trifluralin: 10.01 min
- Details of fitted regression line (log k' vs. log Koc):
log Koc = 2.239 • log k' + 2.874.
coefficient of correlation = 0.979
- Graph of regression line attached: see figure
- Average retention data for test substance: 8.49 min
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The determination of the adsorption coefficient (log Koc) of CXA 5415 (TK A 40075) on soil by means of a HPLC-screening method gave the following result:
log Koc = 3.58 - Executive summary:
The determination of the adsorption coefficient (log Koc) of CXA 5415 (TK A 40075) on soil by means of a HPLC-screening method gave the following result:
log Koc = 3.58
A suitable set of reference substances with adsorption coefficients (log Koc), which had been determined using the OECD guideline 106, and the test substance were chromatographed under standard chromatographic conditions and their retention times (t„) were determined. Using the retention times and the column dead time (t„), which was determined by means of formamide, the corresponding capacity factors (k') were calculated. The log k' of the reference substances and their log Koc-values were used to construct a calibration plot of log k' versus log Koc. The adsorption-coefficient (log Koc) of the test substance was calculated using the log k' of the test substance and the fitted regression line.
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