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EC number: 204-262-9 | CAS number: 118-58-1
- 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
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Between 26 May 2011 and 16 June 2011.
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Study conducted in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do not affect the quality of the relevant results. The study report was conclusive, done to a valid guideline and the study was conducted under GLP conditions.
- 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
- 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
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Date of Inspection: 26 and 27 October 2010 Date of Signature: 8 February 2011
- Type of method:
- HPLC estimation method
- Media:
- soil/sewage sludge
- Radiolabelling:
- no
- Test temperature:
- 35 ºC
- Details on study design: HPLC method:
- Preparation of sample solution:
A solution of the test substance was prepared (12.5 mg in 50 ml methanol/water 55/45 v/v).
After equilibrium of the HPLC system, the calibration mixture was injected first, followed by the test chemical solution twice and the calibration mixture again.
Retention times tR were measured and averaged and the decimal logarithms of the capacity factors k were calculated. The linear regression parameters of the relationship:
log Koc = f (log k)
were also calculated from the data obtained with the calibration mixture and, therewith, log Koc of the test substance was determined from its measured capacity factor.
Finally solutions of the reference substances were injected individually to confirm the peak assignment.
Principle of the Method
Reverse phase High Performance Liquid Chromatography on cyanopropyl-modified silica stationary phase, containing lipophilic and polar moieties, is used.
While passing through the column among with the mobile phase the test substance interacts with the stationary phase. As a result of the partitioning between the mobile and stationary phase the test substance is retarded. The dual-composition of the stationary phase having polar and non-polar sites allows for interaction of polar and non-polar groups of a molecule in a similar way as it is the case for organic matter in soil or sewage sludge matrices. This enables the relationship between the retention time on the column and the adsorption coefficient on organic matter to be established.
Equipment and Conditions:
The sample, formamide and reference standard solutions were injected in duplicate using the following HPLC parameters:
HPLC System: Perkin Elmer (series 200) HPLC system comprising:
-a high pressure pump (module N2910102, serial number: 291N8051901A)
-an auto-sampler (module N2930100, serial number: 293N8052404A)
-a column compartment (module N2601581, serial number OVH0802151130)
-a reflective index detector (series 200a, serial number 125829)
-Column: 250 mm x 4.6 mm, Nucleodur 100-5 CN-RP (Macherey-Nagel)
Serial number: N10080027, batch 34518023
-Column temperature: 35 ºC
-Mobile phase: methanol/water 55/45 (v/v)
-Flow-rate: 1.0 ml/min
UV detector wavelength: dead time and reference standards: 210 nm, sample: 510 nm
-Injection volume: 100 µl - Analytical monitoring:
- no
- Key result
- Type:
- Koc
- Value:
- 5 623 L/kg
- Type:
- log Koc
- Value:
- 3.75
- Details on results (HPLC method):
- - Retention times of reference substances used for calibration: yes
- Details of fitted regression line (log k' vs. log Koc): yes
- Graph of regression line attached: yes
- Average retention data for test substance: - Transformation products:
- not measured
- Details on results (Batch equilibrium method):
- Not applicable.
- Statistics:
- None stated.
- Validity criteria fulfilled:
- yes
- Conclusions:
- The chromatograms of Benzyl Salicylate show one peak at an average retention time of 12.52 minutes, corresponding to an adsorption coefficient (log value) of 3.75.
Therefore: Adsorption coefficient (Koc) of Benzyl Salicylate: log Koc = 3.75 - Executive summary:
Method
The determination was carried out using the HPLC screening method, Method C19 of Commission Directive 2001/59/EC (which constitutes Annex V of Council Directive 67/548/EEC), Method 121 of the OECD Guidelines for Testing of Chemicals, 22 January 2001.
Discussion
Reverse phase High Performance Liquid Chromatography on cyanopropyl-modified silica stationary phase, containing lipophilic and polar moieties, is used. While passing through the column among with the mobile phase the test substance interacts with the stationary phase. As a result of the partitioning between the mobile and stationary phase the test substance is retained. The dual-composition of the stationary phase having polar and non-polar sites allows for interaction of polar and non-polar groups of a molecule in a similar way as it is the case for organic matter in soil or sewage sludge matrices. This enables the relationship between the retention time on the column and the adsorption coefficient on organic matter to be established.Conclusion
The chromatograms of Benzyl Salicylate show one peak at an average retention time of 12.52 minutes, corresponding to an adsorption coefficient (log value) of 3.75. Therefore: Adsorption coefficient (Koc) of Benzyl Salicylate: log Koc = 3.75
Reference
Appendix 1: Adsorption coefficient calculations
Koc Partition Coefficient Determination by Reverse-Phase HPLC
REFERENCE SUBSTANCES |
log Koc |
tR1 |
tR2 | tRm | k | log k |
Formamide |
4.29 |
4.52 | 4.40 | |||
2 -Nitrobenzenamide |
1.45 |
4.86 |
5.01 | 4.93 | 0.120 | -0.921 |
Methyl Benzoate |
1.80 |
6.44 |
6.64 | 6.54 | 0.485 | -0.314 |
Naphthalene |
2.75 |
9.32 |
9.60 | 9.46 | 1.148 | 0.060 |
1,2,3 -Trichlorobenzene |
3.16 |
10.39 |
10.69 | 10.54 | 1.393 | 0.144 |
Phenanthrene |
4.09 |
14.53 |
14.91 | 14.72 | 2.342 | 0.370 |
4,4'-DDT |
5.63 |
30.60 |
31.51 | 31.05 | 6.051 | 0.782 |
tR1, tR2, tRm: retention times (1rst measurement, 2nd measurement, average)
k = (tR/t0)-1: capacity factor, t0: "dead time", i.e. retention time of formamide
Linear regression parameters: log Koc = a * log k + b
Correction coefficient r = 0.9410 a = 2.4777 c = 3.0973
TEST SUBSTANCE:Benzyl Salicylate
tR1 |
tR2 |
tRm | k | log k | log koc | |
Benzyl Salicylate |
12.46 |
12.55 |
12.51 | 1.8396 | 0.2647 | 3.750 |
Description of key information
Based on GLP study following OECD 121, log Koc is 3.75 (Koc = 5623 L/kg).
Key value for chemical safety assessment
- Koc at 20 °C:
- 5 623
Additional information
The chromatograms of Benzyl Salicylate show one peak at an average retention time of 12.52 minutes, corresponding to an adsorption coefficient (log value) of 3.75. Therefore, adsorption coefficient (Koc) of Benzyl Salicylate: log Koc = 3.75, equivalent to a Koc of 5623.
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