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EC number: 205-399-7 | CAS number: 140-11-4
- 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:
- January 7, 2010 - April 09, 2010
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Reason / purpose for cross-reference:
- reference to same study
- Reason / purpose for cross-reference:
- reference to other 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))
- Principles of method if other than guideline:
- Not relevant
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- HPLC estimation method
- Media:
- soil
- Radiolabelling:
- no
- Test temperature:
- 25 °C
- Details on study design: HPLC method:
- EQUIPMENT
Commercially available analytical columns packed with a solid phase containing a moderately polar stationary phase with lipophilic and polar moieties (e.g. cyano-propyl bonded phase). The sorption behaviour of the test substnace on soil was investigated using HPLC.
Instrument: Agilent 1200 series Liquid Chromatograph
Column: Hypersil CPS (25 cm x 4.6 mm internal diameter)
Flow rate: 1.0 ml/min
Injection volume: 20 ul
Detector: UV set at 210 nm
MOBILE PHASES
Acetonitrile;water (55:45 v/v)
DETERMINATION OF DEAD TIME
An internal standard (formamide) with no retention on the HPLC column was used to determine the deadtime of the HPLC system.
REFERENCE SUBSTANCES
Please see table 1 for details
DETERMINATION OF RETENTION TIMES
Please see table 1 for details.
REPETITIONS
A solution of benzyl acetate (14.2 mg/l) in HPLC mobile phase, and also containing IDS at the same concentration as in the reference mixture) was prepared and chromatographed in duplicate, bracketed by samples of the reference mixture, using the conditions outlined above.
EVALUATION
The adsorption coefficient is deduced from the capacity factor (k) given by:
tr-to
k = ________
to
where tr is the measured retention time of sample or reference
and to is the retention time of the internal deadline standard.
In order to correlate the measured capacity factor (k) of the test material with its Koc, six reference materials were selected from a list of recommended compunds. These reference compounds were selected to have log10Koc values between 1.3 and 5.6. - Analytical monitoring:
- not required
- Details on sampling:
- Not relevant
- Details on matrix:
- Not relevant
- Details on test conditions:
- Not relevant
- Computational methods:
- A calibration of log10k versus log10Koc was constructed for ther reference standards. The logarithm of the capacity factors for the test substance was then calculated and the log10Koc value was determined by interpolation.
- Type:
- Koc
- Value:
- 250
- Temp.:
- 25 °C
- Type:
- log Koc
- Value:
- 2.4
- Temp.:
- 25 °C
- Details on results (HPLC method):
- Benzyl acetate was determined to have a log10Koc value of 2.4 (equivalent Koc = 250). Please see table 2 for more details.
- Adsorption and desorption constants:
- Not relevant
- Recovery of test material:
- Not relevant
- Concentration of test substance at end of adsorption equilibration period:
- Not relevant
- Concentration of test substance at end of desorption equilibration period:
- Not relevant
- Details on results (Batch equilibrium method):
- Not relevant
- Statistics:
- Not relevant
- Validity criteria fulfilled:
- yes
- Conclusions:
- Benzyl acetate was determined to have a log10Koc value of 2.4 (equivalent Koc = 250).
- Executive summary:
A study was performed according to OECD Guideline 121 (Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC)). The purpose of the study was to estimate the adsorption coefficient (Koc) of Benzyl acetate by HPLC. Benzyl acetate was determined to have a log10Koc value of 2.4 (equivalent Koc = 250).
Therefore, Benzyl acetate has a medium potential for soil mobility.
Reference
Table 2: HPLC determination of log10Kocfor benzyl acetate
Sample |
Component |
tr(mins) |
k |
Log10k |
Log10Koc |
Standard Run A (t0= 2.971 mins) |
Acetanilide |
3.498 |
0.177 |
-0.751 |
1.3 |
Nitrobenzene |
4.253 |
0.432 |
-0.365 |
2.4 |
|
Naphthalene |
4.890 |
0.646 |
-0.190 |
2.8 |
|
2-Methylnaphthalene |
5.165 |
0.738 |
-0.132 |
3.9 |
|
Anthracene |
5.716 |
0.924 |
-0.034 |
4.4 |
|
DDT |
8.442 |
1.841 |
0.265 |
5.6 |
|
Sample A (t0= 2.971 mins) |
Benzyl acetate |
4.097 |
0.379 |
-0.421 |
2.4 |
Sample B (t0= 2.970 mins) |
Benzyl acetate |
4.096 |
0.379 |
-0.421 |
2.4 |
Standard Run B (t0= 2.972 mins) |
Acetanilide |
3.499 |
0.177 |
-0.751 |
1.3 |
Nitrobenzene |
4.254 |
0.431 |
-0.365 |
2.4 |
|
Naphthalene |
4.889 |
0.645 |
-0.190 |
2.8 |
|
2-Methylnaphthalene |
5.164 |
0.738 |
-0.132 |
3.9 |
|
Anthracene |
5.716 |
0.923 |
-0.035 |
4.4 |
|
DDT |
8.439 |
1.840 |
0.265 |
5.6 |
Linear regression (based on mean of standard runs A and B): log10Koc= 4.46 log10k + 4.28
Description of key information
A study was performed according to OECD Guideline 121 (Estimation of the Adsorption Coefficient (Koc) on Soil and on Sewage Sludge using High Performance Liquid Chromatography (HPLC)). The purpose of the study was to estimate the adsorption coefficient (Koc) of Benzyl acetate by HPLC. Benzyl acetate was determined to have a log10Koc value of 2.4 (equivalent Koc = 250).
Therefore, Benzyl acetate has a medium potential for soil mobility.
Key value for chemical safety assessment
- Koc at 20 °C:
- 250
Additional information
[LogKoc: 2.4]
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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