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EC number: 604-200-4 | CAS number: 14078-41-2
- 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
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Adsorption / desorption
Administrative data
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- between 08 January 2009 and 01 April 2009.
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Study conducted to GLP and in compliance with agreed protocols, with no or minor deviations from standard test guidelines and/or minor methodological deficiencies, which do no effect the quality of the relevant results
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 009
- Report date:
- 2009
Materials and methods
Test guidelineopen allclose all
- 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: 19/08/08 Date of Signature: 04/03/09
- Type of method:
- HPLC estimation method
- Media:
- soil/sewage sludge
Test material
- Reference substance name:
- EXAMPLE: Indicate the identity for one or more appropriate identifiers, e.g. CAS number, CAS name, IUPAC name. Copy this block of fields as appropriate.
- IUPAC Name:
- EXAMPLE: Indicate the identity for one or more appropriate identifiers, e.g. CAS number, CAS name, IUPAC name. Copy this block of fields as appropriate.
- Details on test material:
- Sponsor's identification : L17_Precursor
Description : pale yellow powder
Chemical name : 5,5-dimethoxy-3,3’-di-tert-butyl-2,2’-biphenol
CAS number : 14078-41-2
Purity : 93.4%
Batch number : DALA046312
Date received : 11 November 2008
Storage conditions : room temperature in the dark
Constituent 1
- Radiolabelling:
- no
Study design
HPLC method
- Details on study design: HPLC method:
- EEQUIPMENT
- Apparatus:
The sample, dead time and reference standard solutions were injected in duplicate using the following HPLC parameters:
HPLC System : Agilent Technologies 1100, incorporating autosampler and workstation
Column : Zorbax SB-CN 5μ (250 x 4.6 mm id)
Column temperature : 30ºC
Mobile phase : methanol:water (55:45 v/v)
pH of mobile phase : 6.0
Flow-rate : 1.0 ml/min
Injection volume : 10 µl
UV detector wavelength : dead time and reference standards: 210 nm
sample : 300 nm
DETERMINATION OF DEAD TIME
The dead time was determined by measuring the retention time of formamide (purity* ≥99.5%, 505 mg/l solution in mobile phase).
REFERENCE SUBSTANCES
- Identity:
Solutions of reference standards (see following table) were prepared in methanol.
Standard Purity (%)* Concentration (mg/l)
Acetanilide 99+ 104
Phenol 99+ 118
Atrazine 97.4 100
Isoproturon 99.8 100
Triadimenol 98.4 112
Linuron 99.5 103
Naphthalene ≥99.0 110
Endosulfan-diol 99.8 105
Fenthion 97.8 126
-Endosulfan 99.6 120
Phenanthrene ≥97.0 104
Diclofop-methyl 99.5 106
DDT 98 104
DETERMINATION OF RETENTION TIMES
The mobile phase was ramped to 100% methanol after the retention time of DDT to elute any highly retained components of the test material.
EVALUATION
- Calculation of capacity factors k':
k= tr- to/ to
where:
k = capacity factor
tr = retention time (min)
t0 = dead time (min)
Batch equilibrium or other method
- Analytical monitoring:
- no
- 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:
- 205 000
- Type:
- log Koc
- Value:
- 5.31
Results: HPLC method
- Details on results (HPLC method):
- The retention times of formamide and the retention times, capacity factors (k) and log10 Koc values for the reference standards are shown in Tables 1 and 2
Adsorption coefficient of sample
The retention times, capacity factors and log10 Koc values determined for the sample are shown below:
Injection Retention Time (mins) Capacity Factor (k) Log10 k Log10 Koc
1 50.928 17.0 1.23 5.31
2 50.871 17.0 1.23 5.31
Mean log10 Koc: 5.31
Adsorption coefficient: 2.05 x 105
Discussion:
Although the main peak in the chromatography (as shown in attachment 1) that represents the test material eluted before DDT, and so within the range of the calibration curve, a ramp to 100% methanol after the retention time of DDT was performed to show that there were no more significant components in the test material. A chromatogram of a sample blank was subtracted from the chromatograms of the sample to remove the baseline drift due the mobile phase gradient.
Results: Batch equilibrium or other method
- Statistics:
- None stated.
Any other information on results incl. tables
Calibration
The retention times of formamide and the retention times, capacity factors (k) and log10Kocvalues for the reference standards are shown in the two following tables below:
Table 1:
Dead Time |
Retention Time (mins) |
Mean Retention Time (mins) |
|
Injection 1 |
Injection 2 |
||
Formamide |
2.828 |
2.827 |
2.828 |
Table 2:
Standard |
Retention Time (mins) |
Mean Retention Time (mins) |
Capacity Factor (k) |
Log10k |
Log10Koc |
|
Injection 1 |
Injection 2 |
|||||
Acetanilide |
3.983 |
3.983 |
3.983 |
0.409 |
-0.389 |
1.25 |
Phenol |
3.790 |
3.797 |
3.794 |
0.342 |
-0.466 |
1.32 |
Atrazine |
5.829 |
5.826 |
5.828 |
1.06 |
2.57 x 10-2 |
1.81 |
Isoproturon |
6.217 |
6.217 |
6.217 |
1.20 |
7.87 x 10-2 |
1.86 |
Triadimenol |
8.524 |
8.525 |
8.525 |
2.02 |
0.304 |
2.40 |
Linuron |
9.037 |
9.037 |
9.037 |
2.20 |
0.342 |
2.59 |
Naphthalene |
7.620 |
7.618 |
7.619 |
1.70 |
0.229 |
2.75 |
Endosulfan-diol |
11.017 |
11.024 |
11.021 |
2.90 |
0.462 |
3.02 |
Fenthion |
14.494 |
14.494 |
14.494 |
4.13 |
0.616 |
3.31 |
a-Endosulfan |
20.926 |
20.930 |
20.928 |
6.40 |
0.806 |
4.09 |
Phenanthrene |
16.539 |
16.553 |
16.546 |
4.85 |
0.686 |
4.09 |
Diclofop-methyl |
23.479 |
23.469 |
23.474 |
7.30 |
0.863 |
4.20 |
DDT |
50.123 |
50.157 |
50.140 |
16.7 |
1.22 |
5.63 |
Adsorption coefficient of sample
The retention times, capacity factors and log10Kocvalues determined for the sample are shown in the following table:
Table 3:
Injection |
Retention Time (mins) |
Capacity Factor (k) |
Log10k |
Log10Koc |
1 |
50.928 |
17.0 |
1.23 |
5.31 |
2 |
50.871 |
17.0 |
1.23 |
5.31 |
Mean log10Koc: 5.31
Adsorption coefficient: 2.05 x 105
Discussion
Although the main peak in the chromatography that represents the test material eluted before DDT, and so within the range of the calibration curve, a ramp to 100% methanol after the retention time of DDT was performed to show that there were no more significant components in the test material. A chromatogram of a sample blank was subtracted from the chromatograms of the sample to remove the baseline drift due the mobile phase gradient.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The adsorption coefficient (Koc) of the test material has been determined to be 2.05 x 10E5, log10 Koc 5.31.
- 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
Although the main peak in the chromatography that represents the test material eluted before DDT, and so within the range of the calibration curve, a ramp to 100% methanol after the retention time of DDT was performed to show that there were no more significant components in the test material. A chromatogram of a sample blank was subtracted from the chromatograms of the sample to remove the baseline drift due the mobile phase gradient.Conclusion
The adsorption coefficient (Koc) of the test material has been determined to be 2.05 x 105, log10Koc 5.31.
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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