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EC number: 700-182-8 | CAS number: 134652-60-1
- 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
- Study period:
- 26 May to 27 May 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Recent study conducted by a GLP certified laboratory in accordance with a suitable study guideline.
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 010
- Report date:
- 2010
Materials and methods
Test guidelineopen allclose all
- 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 (incl. QA statement)
- Type of method:
- HPLC estimation method
- Media:
- soil/sewage sludge
Test material
- Reference substance name:
- Tripropan-2-ylsilyl 2-methylprop-2-enoate
- EC Number:
- 700-182-8
- Cas Number:
- 134652-60-1
- Molecular formula:
- C13 H26 O2 Si
- IUPAC Name:
- Tripropan-2-ylsilyl 2-methylprop-2-enoate
- Details on test material:
- - Name of test material: TIS-M
- Lot/batch No.: 9925
- Expiration date of the lot/batch: 2 December 2010
- Storage condition of test material: Under nitrogen at room temperature, continuously protected form all light.
Constituent 1
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
None - Radiolabelling:
- no
Study design
- Test temperature:
- 25 deg C (column temperature)
HPLC method
- Details on study design: HPLC method:
- APPARATUS
Stationary Phase LiChrospher 100 CN 250 x 4 mm, 5μm HPLC Column
No.: 841404
HPLC system: Merck-Hitachi LaChrom HPLC system:
D-7000 Interface, No.: 0811-181
L-7100 HPLC pump, No.: 0823-059
L-7200 Autosampler, No.: 0606-021
L-7400 UV Detector, No.: 0928-058
Hitachi 655A-52 Column Oven, No: 6211-016
L 7612 Degasser, No.: 012-05
Balance: BP221S Sartorius, No.: 11809117
Water purification system: MILLIPORE, DIRECT Q3, FOMNO 7334I
Ultrasonic bath: Elmasonic S300H, ELMA, No.: 010890105
HPLC Conditions:
Mobil Phase: ACN : Water ( 60 : 40 )
Flow: 0.5 ml/min.
Injection volume: 10 μl
Detector: UV at 218 nm
Column temperature: 25 °C
DETERMINATION OF DEAD TIME
- Method: Sodium nitrate used to calculate dead time.
REFERENCE SUBSTANCES
- Identity: Sodium nitrate, Acetanilide, Methyl benzoate, Linuron, Naphthalene, Fenthion, Phenantrene and DDT.
DETERMINATION OF RETENTION TIMES
- Quantity of test substance introduced in the column: TIS-M was dissolved in acetonitrile. The concentration of this solution was 1 mg/ml. This stock solution was diluted with ACN (1 to 100 dilution).
- Quantity of reference substances: Reference substances were dissolved in ACN. Concentration of these stock solutions was about 1 mg/ml.
These stock solutions were diluted with the mobile phase resulting in about 10 μg/ml solutions.
- Intervals of calibration: Various.
REPETITIONS
- Number of determinations: 6
EVALUATION
- Calculation of capacity factors k': k' = (tr-t0)/t0 where tR is the retention time of the selected reference substance and t0 is the dead time.
- Calculation of retention times: Three series of the above reference solutions and the test item solution were measured alternately, with two replicate injections. For the determination of t0 (t0 = retention time of the unretarded component) sodium nitrate solution was injected.
- Determination of the log Koc value: log k' = 0.1016 * log Koc + 0.0607. The calibration equation was determined by linear regression using the least squares method.
Batch equilibrium or other method
- Analytical monitoring:
- not specified
- Details on sampling:
- Not applicable
- Details on matrix:
- Not applicable
- Details on test conditions:
- Not applicable
- Computational methods:
- Not applicable
Results and discussion
Adsorption coefficientopen allclose all
- Type:
- Koc
- Value:
- 17 259
- Temp.:
- 25 °C
- Type:
- log Koc
- Value:
- 4.24
- Temp.:
- 25 °C
Results: HPLC method
- Details on results (HPLC method):
- - Mean Retention times of reference substances used for calibration: Sodium Nitrate: 2.40, Acetanilide: 5.82, Methyl Benzoate: 6.71, Linuron: 7.42, Naphthalene: 8.07, Fenthion: 8.88, Phenantrene: 9.13, DDT: 12.53.
- Details of fitted regression line (log k' vs. log Koc):
- Graph of regression line attached
- Average retention data for test substance: 9.85 minutes.
Results: Batch equilibrium or other method
- Transformation products:
- not specified
Any other information on results incl. tables
Table 2: Measured and calculated data of the reference substances and test item.
Chemical name |
Log Koc |
Retention Time (min) |
Log k’ |
Log Koc |
Accuracy |
Repeatability |
From OECD 121 |
calculated |
calculated |
Log unit |
ΔlogKoc, log unit |
||
Sodium Nitrate |
- |
2.41 |
For determination of dead time. |
|||
2.41 |
||||||
2.40 |
||||||
2.40 |
||||||
2.40 |
||||||
2.40 |
||||||
Mean |
2.40 |
|||||
CV% |
0.2 |
|||||
Acetanilide |
1.25 |
5.81 |
0.152 |
0.89 |
0.34 |
0.03 |
5.82 |
0.153 |
0.91 |
||||
5.83 |
0.154 |
0.92 |
||||
5.83 |
0.154 |
0.92 |
||||
5.82 |
0.153 |
0.91 |
||||
5.82 |
0.153 |
0.91 |
||||
Mean |
5.82 |
0.153 |
0.91 |
|||
CV% |
0.1 |
- |
- |
|||
Methyl- benzoate |
1.80 |
6.69 |
0.251 |
1.88 |
0.10 |
0.04 |
6.69 |
0.251 |
1.88 |
||||
6.73 |
0.255 |
1.92 |
||||
6.73 |
0.255 |
1.92 |
||||
6.72 |
0.254 |
1.91 |
||||
6.71 |
0.253 |
1.90 |
||||
Mean |
6.71 |
0.253 |
1.90 |
|||
CV% |
0.3 |
- |
- |
|||
Linuron |
2.59 |
7.39 |
0.317 |
2.52 |
0.04 |
0.04 |
7.40 |
0.318 |
2.53 |
||||
7.44 |
0.321 |
2.57 |
||||
7.42 |
0.320 |
2.55 |
||||
7.43 |
0.320 |
2.56 |
||||
7.42 |
0.320 |
2.55 |
||||
Mean |
7.42 |
0.319 |
2.55 |
|||
CV% |
0.3 |
- |
- |
|||
Naphthalene |
2.75 |
8.04 |
0.370 |
3.05 |
0.32 |
0.05 |
8.05 |
0.371 |
3.05 |
||||
8.10 |
0.375 |
3.09 |
||||
8.07 |
0.373 |
3.07 |
||||
8.08 |
0.373 |
3.08 |
||||
8.08 |
0.373 |
3.08 |
||||
Mean |
8.07 |
0.373 |
3.07 |
|||
CV% |
0.3 |
- |
- |
|||
Fenthion |
3.31 |
8.86 |
0.429 |
3.63 |
0.33 |
0.03 |
8.86 |
0.429 |
3.63 |
||||
8.90 |
0.432 |
3.65 |
||||
8.90 |
0.432 |
3.65 |
||||
8.88 |
0.431 |
3.64 |
||||
8.88 |
0.431 |
3.64 |
||||
Mean |
8.88 |
0.431 |
3.64 |
|||
CV% |
0.2 |
- |
- |
|||
Phenantrene
|
4.09
|
9.12 |
0.446 |
3.80 |
0.29 |
0.01 |
9.13 |
0.447 |
3.80 |
||||
9.14 |
0.448 |
3.81 |
||||
9.14 |
0.448 |
3.81 |
||||
9.13 |
0.447 |
3.80 |
||||
9.13 |
0.447 |
3.80 |
||||
Mean |
9.13 |
0.447 |
3.80 |
|||
CV% |
0.1 |
- |
- |
|||
DDT
|
5.63 |
12.55 |
0.626 |
5.56 |
0.08 |
0.03 |
12.56 |
0.626 |
5.56 |
||||
12.54 |
0.625 |
5.56 |
||||
12.53 |
0.625 |
5.55 |
||||
12.49 |
0.623 |
5.54 |
||||
12.49 |
0.623 |
5.54 |
||||
Mean |
12.53 |
0.625 |
5.55 |
|||
CV% |
0.2 |
- |
- |
|||
TIS-M |
- |
9.88 |
0.493 |
4.26 |
- |
- |
9.87 |
0.492 |
4.25 |
||||
9.85 |
0.491 |
4.24 |
||||
9.85 |
0.491 |
4.24 |
||||
9.83 |
0.490 |
4.23 |
||||
9.81 |
0.489 |
4.21 |
||||
Mean |
9.85 |
0.491 |
4.24 |
|||
CV% |
0.3 |
- |
- |
A calibration plot of log k' versus log Koc was prepared.The calibration equation was determined by linear regression using the least squares method.
-Repeatability is the difference of maximum and minimum values of log Koc derived from individual measurements.
-Accuracy is the difference between the estimated log Koc and the log Koc value determined by the batch equilibrium method.
Retention time of TIS-M (9.85 min) is within the calibrated range, so it was possible to estimate a log Koc value.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The log Koc of the registered substance was estimated to be 4.24 and the adsorption coefficient (Koc) was estimated to be 17 259.
- Executive summary:
The adsorption coefficient (Koc) of the registered substance was assessed according to EC C.19 using a HPLC method. It was calibrated using the following reference substances: Sodium Nitrate, Acetanilide, Methyl Benzoate, Linuron, Naphthalene, Fenthion, Phenantrene and DDT. The log Koc of the registered substance was estimated to be 4.24 and the adsorption coefficient (Koc) was estimated to be 17 259.
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