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EC number: 271-846-8 | CAS number: 68609-97-2
- 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
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 18-Feb-2010 to 30-Apr-2010
- 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:
- 2 010
- Report date:
- 2010
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 Signature on GLP certificate: November 12, 2008
- Type of method:
- other: HPLC estimation method.
- Media:
- other: Not applicable.
Test material
- Details on test material:
- Alkyl (C12-C14) glycidyl ether
Label: Epoxide 8
51% C12 Glycidyl ether
21% C14 Glycidyl ether
5% C16 Glycidyl ether
13% N +1's
4% alpha addition Products
94% total active (label claim)
- Physical state: Clear colorless liquid
- Storage condition of test material: ambient
Constituent 1
- Radiolabelling:
- no
Study design
- Test temperature:
- 20ºC
HPLC method
- Details on study design: HPLC method:
- The isocratic elution did not lead to the elution of the test item.
Apparatus: Merck-Hitachi autosampler L-7200
Merck-Hitachi pump L-6200
Sedex85 ELSD detector LCELSD 2, Oven Temperature: 50 °C (Channel B)
Merck-Hitachi UV detector L-4000 (Channel A)
Column: LiChrospher CN, particle size 5 µm, 250 mm x 4.6 mm
HPLC Eluent: Water / methanol (45:55; v/v); pH 6.13
Detection: Test item: ELSD
Reference items: 210 nm
Sodium nitrate: 210 nm
Temperature: Room temperature (20 °C)
Injection Volume: 10 µL
Flow: 1.0 mL/min
Run Time: 15 minutes
Retention Times: See Table 1
Batch equilibrium or other method
- Analytical monitoring:
- not required
Results and discussion
Adsorption coefficientopen allclose all
- Type:
- Koc
- Value:
- > 426 580 other: without unit
- Temp.:
- 20 °C
- Type:
- log Koc
- Value:
- > 5.63 other: without unit
- Temp.:
- 20 °C
Results: Batch equilibrium or other method
- Transformation products:
- not measured
- Details on results (Batch equilibrium method):
- In this case Not applicable.
Any other information on results incl. tables
The test item solution was injected three times and the combined reference solution was injected six times.In the present study the reference items covered the range of log KOC 1.25 to log KOC 5.63. The elution of the test item was not possible with the criteria given in the guideline (isocratic HPLC method and an elution system only with methanol and water).Therefore, thelog KOC of the test item is > 5.63, which is equal to a KOCvalue of >426580 using the HPLC method. This value indicates that Oxirane, mono[(C12-14-alkyloxy)methyl] derivs. / ERC Nr 17 is immobile, as it will be adsorbed by organic carbon in soil.This result was confirmed with a model calculation based on the water solubility and the partition coefficient of the test item, which states that the log KOC is higher than 4.90.
A typical HPLC chromatogram of the reference standard mixture is shown in Figure 1. An HPLC chromatogram of the test item is shown in Figure 2. A typical chromatogram of the determination of the dead-time is given in Figure 3.
The retention times of the individual measurements of the reference items, test item and the dead time are given in Table 1.The capacity factor (k’) was calculated for each reference item using the retention times. Log KOCwas plotted versus log k’ for each component to obtain a regression curve (Table 2 and Figure 4).The values given represent rounded values using the exact raw data.
Table 1 Retention Times in Minutes of the Reference Items and the Test Item
|
1strun |
2ndrun |
3rdrun |
4thrun |
5thrun |
6thrun |
Sodium nitrate (= dead time) |
1.508 |
1.492 |
1.500 |
1.500 |
|
|
Reference Items: |
||||||
Acetanilide |
3.183 |
3.158 |
3.185 |
3.167 |
3.158 |
3.158 |
Isoproturon |
3.708 |
3.667 |
3.667 |
3.675 |
3.658 |
3.667 |
Linuron |
4.292 |
4.233 |
4.233 |
4.242 |
4.225 |
4.225 |
Pyrazophos |
5.350 |
5.242 |
5.250 |
5.258 |
5.225 |
5.242 |
Diclofop-methyl |
5.942 |
5.792 |
5.792 |
5.817 |
5.775 |
5.783 |
2,4-DDT |
8.417 |
8.125 |
8.108 |
8.175 |
8.108 |
8.100 |
Oxirane, mono[(C12-14-alkyloxy)methyl] derivs. / ERC Nr 17: |
|
|
|
|||
Peak |
- |
- |
- |
|
|
|
Table 2 Results of Linear Regression of Log k’ vs. Log KOC
|
Number |
Mean retention time |
k' |
log k' |
log KOC |
Sodium nitrate (= dead time) |
4 |
1.50 |
- |
- |
|
Reference Items: |
|||||
Acetanilide |
6 |
3.17 |
1.11 |
0.05 |
1.25 |
Isoproturon |
6 |
3.67 |
1.45 |
0.16 |
1.86 |
Linuron |
6 |
4.24 |
1.83 |
0.26 |
2.59 |
Pyrazophos |
6 |
5.26 |
2.51 |
0.40 |
3.65 |
Diclofop-methyl |
6 |
5.82 |
2.88 |
0.46 |
4.20 |
2,4-DDT |
6 |
8.17 |
4.45 |
0.65 |
5.63 |
|
slope = |
|
|
|
0.134 |
Linear Regression: |
y-axis intercept = |
-0.100 |
|||
|
coefficient of regression (r) = |
0.998 |
The tabulated values represent rounded results, which were obtained by calculation using the exact raw data.
The test item could not be eluted, therefore the KOCof the test item can be estimated to be higher than the last reference item on the list of the guideline, which has a log KOCvalue of 5.63.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- EX
- Conclusions:
- The log of the adsorption coefficient (KOC) of Oxirane, mono[(C12-14-alkyloxy)methyl] derivs. / ERC Nr 17 was estimated to be log KOC > 5.63 which is equal to a KOC value of > 426580 using the HPLC method.
The experimentally determined result was confirmed by a model calculation, which results in a value of log KOC > 4.90 which is equal to a KOC value of > 286090. This value indicates that Oxirane, mono[(C12-14-alkyloxy)methyl] derivs. / ERC Nr 17 will be adsorbed by organic carbon in soil and is immobile. - Executive summary:
The log of the adsorption coefficient (KOC) of Oxirane, mono[(C12-14-alkyloxy)methyl] derivs. / ERC Nr 17 was estimated to be
log KOC> 5.63which is equal to a KOCvalue of>426580
using the HPLC method.
The experimentally determined result was confirmed by a model calculation, which results in a value of
log KOC> 4.90which is equal to a KOCvalue of> 286090
This value indicates that Oxirane, mono[(C12-14-alkyloxy)methyl] derivs. / ERC Nr 17 will be adsorbed by organic carbon in soil and can be classified to be immobile according these study results.
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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