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EC number: 813-120-0 | CAS number: 1262967-45-2
- 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:
- 15 July 2011 - 09 February 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Remarks:
- Study conducted in accordance with International guidelines and in accordance with GLP. All guideline validity criteria were met.
- 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))
- Version / remarks:
- 22 Jan 2001
- 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))
- Version / remarks:
- Commission Regulation (EC) No 440/2008 laying down test methods pursuant to Regulation (EC) No 1907/2006 of the European Parliament and of the Council on the Registration, Evaluation, Authorisation and Restriction of Chemicals (REACH).
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- HPLC estimation method
- Specific details on test material used for the study:
- RADIOLABELLING INFORMATION (if applicable)
- Radiochemical purity: N/A
- Specific activity: N/A
- Locations of the label: N/A
- Expiration date of radiochemical substance: N/A
STABILITY AND STORAGE CONDITIONS OF TEST MATERIAL
- Storage condition of test material: Room temperature in the dark and under nitrogen.
- Stability under test conditions: Assumed stable.
- Solubility and stability of the test substance in the solvent/vehicle: N/A, applied as supplied.
- Reactivity of the test substance with the solvent/vehicle of the cell culture medium: N/A
TREATMENT OF TEST MATERIAL PRIOR TO TESTING
- Treatment of test material prior to testing: N/A
- Preliminary purification step (if any): N/A
- Final dilution of a dissolved solid, stock liquid or gel: N/A
- Final preparation of a solid: N/A
FORM AS APPLIED IN THE TEST (if different from that of starting material): Applied as supplied.
TYPE OF BIOCIDE/PESTICIDE FORMULATION (if applicable): N/A
OTHER SPECIFICS: No - Radiolabelling:
- no
- Details on study design: HPLC method:
- EQUIPMENT
- Apparatus: Agilent 1200 Series LC
- Column: HyperClone CPS (25 cm x 4.6 mm)
- Column temperature: 25 ºC
- Flow rate: 1 mL/min
- Detection system: UV set at 210 nm
MOBILE PHASES
- Type: Acetonitrile: water (55:45 v/v)
- Experiments with additives carried out on separate columns: no
- pH: Not adjusted
- Solutes for dissolving test and reference substances: Test item dissolved in mobile phase.
DETERMINATION OF DEAD TIME
- Method: measurement of an internal deadtime standard (IDS), formamide, which has no retention time on the HPLC column.
REFERENCE SUBSTANCES
- Identity: Acetanilide, nitrobenzene, naphthalene, 2-methylnaphthalene, anthracene and DDT.
DETERMINATION OF RETENTION TIMES
- Quantity of test substance introduced in the column: 20 µL of a solution prepared at 1440 mg/L.
- Quantity of reference substances: 20 µL of each of the following solutions; acetanilide (11 mg/L); nitrobenzene (11.1 mg/L); naphthalene (4.67 mg/L); 2-methylnaphthalene (5.24 mg/L); anthracene (9.60 mg/L); DDT (10.6 mg/L).
- Intervals of calibration: Before and after analysis of tet item.
REPETITIONS
- Number of determinations: 2
EVALUATION
- Calculation of capacity factors k': k = (Tr-T0) / T0 where; Tr = retention time of sample/ standard and T0 = retention time of IDS
- Calculation of retention times: Retention time of standard/ sample - retention time of IDS
- Determination of the log Koc value: A calibration plot of log10k versus log10Koc was constructed for the reference standards. The logarithms of the capacity factors for the test substance were then calculated and log10Koc values determined by interpolation. - Key result
- Sample No.:
- #1
- Type:
- log Koc
- Value:
- >= 4 dimensionless
- Remarks on result:
- other: N/A
- Details on results (HPLC method):
- See Table 1
- Validity criteria fulfilled:
- yes
- Conclusions:
- The components of Tetraesters of pentaerythritol with 2-methylpropanoic acid and 3,5,5-trimethyl-hexanoic acid were found to have log10 Koc values of greater than or equal to 4.0 (equivalent Koc ≥ 10000).
- Executive summary:
OECD 121 (2012) - The sorption behaviour of the test substance on soil was investigated using high performance liquid chromatography (HPLC).
The adsorption coefficient was deduced from the capacity factor (k) given by:
k = (tr– t0) / t0
where;
tr was the measured retention time of sample or reference standard
t0 was the retention time of the internal deadtime standard (formamide).
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 compounds. These reference compounds were selected to have log10 Koc values between 1.3 and 5.6. An internal standard (formamide) with no retention on the HPLC column was used to determine the deadtime of the HPLC system.
A solution of Tetraesters of pentaerythritol with 2-methylpropanoic acid and 3,5,5-trimethyl-hexanoic acid (1440 mg/l in HPLC mobile phase (acetonitrile:water 55:45 v/v), and also containing I.D.S. at the same concentration as in the reference mixture) was prepared and chromatographed in duplicate, bracketed by samples of the reference mixture, using HPLC.
A calibration plot of log10k versus log10 Koc was constructed for the reference standards. The logarithms of the capacity factors for the test substance were then calculated and log10 Koc values determined by interpolation, if appropriate.
Two of the components of Tetraesters of pentaerythritol with 2-methylpropanoic acid and 3,5,5-trimethyl-hexanoic acid had retention times within the range of the reference standards and were determined to have log10 Koc values of 4.0 and 5.2. The other components had a retention time greater than DDT, indicating log10 Koc values of greater than 5.6.
In summary, the components of Tetraesters of pentaerythritol with 2-methylpropanoic acid and 3,5,5-trimethyl-hexanoic acid were found to have log10 Koc values of greater than or equal to 4.0 (equivalent Koc ≥ 10000).
Reference
Table 1 HPLC determination of log10Koc for Tetraesters of pentaerythritol with 2- methylpropanoic acid and 3,5,5-trimethyl-hexanoic acid
Sample |
Component |
Retention time (tr) (mins) |
k |
log10k |
log10Koc |
Standard mix run A (t0= 2.909 mins) |
Acetanilide |
3.369 |
0.158 |
-0.801 |
1.3 |
Nitrobenzene |
3.881 |
0.334 |
-0.476 |
2.4 |
|
Naphthalene |
4.368 |
0.502 |
-0.300 |
2.8 |
|
2-methylnaphthalene |
4.575 |
0.573 |
-0.242 |
3.9 |
|
Anthracene |
4.984 |
0.713 |
-0.147 |
4.4 |
|
DDT |
6.697 |
1.302 |
0.115 |
5.6 |
|
|
|||||
Sample A (t0= 2.910 mins) |
Test Item |
4.808 6.191 |
0.652 1.127 |
-0.186 0.052 |
4.0 5.2 |
Sample B (t0= 2.907 mins) |
Test Item |
4.806 6.190 |
0.653 1.129 |
-0.185 0.053 |
4.0 5.2 |
|
|||||
Standard mix run B (t0= 2.912 mins) |
Acetanilide |
3.374 |
0.159 |
-0.800 |
1.3 |
Nitrobenzene |
3.886 |
0.334 |
-0.476 |
2.4 |
|
Naphthalene |
4.374 |
0.502 |
-0.299 |
2.8 |
|
2-methylnaphthalene |
4.581 |
0.573 |
-0.242 |
3.9 |
|
Anthracene |
4.990 |
0.714 |
-0.147 |
4.4 |
|
DDT |
6.706 |
1.303 |
0.115 |
5.6 |
Linear regression (based on std. mix run A & B): log10Koc= 4.93 log10k + 4.90
Description of key information
Adsorption/ desorption = logKoc: ≥4.0 (equivalent Koc ≥10000); OECD 121; Sydney, P. (2012)
Key value for chemical safety assessment
Additional information
OECD 121 (2012) - The sorption behaviour of the test substance on soil was investigated using high performance liquid chromatography (HPLC).
The adsorption coefficient was deduced from the capacity factor (k) given by:
k = (tr– t0) / t0
where;
tr was the measured retention time of sample or reference standard
t0 was the retention time of the internal deadtime standard (formamide).
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 compounds. These reference compounds were selected to have log10Kocvalues between 1.3 and 5.6. An internal standard (formamide) with no retention on the HPLC column was used to determine the deadtime of the HPLC system.
A solution of Tetraesters of pentaerythritol with 2- methylpropanoic acid and 3,5,5-trimethyl-hexanoic acid (1440 mg/l in HPLC mobile phase (acetonitrile:water 55:45 v/v), and also containing I.D.S. at the same concentration as in the reference mixture) was prepared and chromatographed in duplicate, bracketed by samples of the reference mixture, using HPLC.
A calibration plot of log10k versus log10Kocwas constructed for the reference standards. The logarithms of the capacity factors for the test substance were then calculated and log10Kocvalues determined by interpolation, if appropriate.
Two of the components of Tetraesters of pentaerythritol with 2- methylpropanoic acid and 3,5,5-trimethyl-hexanoic acid had retention times within the range of the reference standards and were determined to have log10Kocvalues of 4.0 and 5.2. The other components had a retention time greater than DDT, indicating log10Kocvalues of greater than 5.6.
In summary, the components of Tetraesters of pentaerythritol with 2- methylpropanoic acid and 3,5,5-trimethyl-hexanoic acid were found to have log10Kocvalues of greater than or equal to 4.0 (equivalent Koc ≥ 10000).
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