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EC number: 203-326-3 | CAS number: 105-74-8
- 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:
- 27-May-2010 to 31-Aug-2010
- 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 Certificate: November 12, 2008
- Type of method:
- HPLC estimation method
- Media:
- other: not applicable
- Radiolabelling:
- no
- Test temperature:
- 25 °C
- Details on study design: HPLC method:
- HPLC-Conditions
Methanol was found to be not suitable to elute Dilauroyl peroxide (CAS# 105-74-8). Referring to this, tetrahydrofuran was used as organic solvent.
Apparatus: Varian autosampler 9095
Varian pump 9012
Varian UV/VIS detector ProStar 310
Croco-Cil column oven LCSOF 55
Column: LiChrospher 100 CN, particle size 5 µm, 250 mm x 4 mm
HPLC Eluent: Water / tetrahydrofuran (45:55; v/v); pH 5.90
Detection: Test item: 210 nm
Reference item: 210 nm
Sodium nitrate: 210 nm
Temperature: 25 °C
Injection Volume: 20 µL
Flow: 1.0 mL/min
Run Time: 20 minutes
Retention Times: See Table 1 - Analytical monitoring:
- not required
- Type:
- Koc
- Value:
- > 426 580
- Temp.:
- 25 °C
- Remarks on result:
- other: determined by HPLC method
- Type:
- log Koc
- Value:
- > 5.63
- Temp.:
- 25 °C
- Remarks on result:
- other: determined by HPLC method
- Type:
- log Koc
- Value:
- > 7.81
- Temp.:
- 25 °C
- Remarks on result:
- other: calculated by QSAR
- Type:
- log Koc
- Value:
- ca. 8.3
- Temp.:
- 25 °C
- Remarks on result:
- other: calculated by extrapolation for experimental results
- Transformation products:
- not measured
- Validity criteria fulfilled:
- yes
- Conclusions:
- The log of the adsorption coefficient (KOC) of Dilauroyl peroxide (CAS# 105-74-8) was estimated to be log KOC > 5.63 which is equal to a KOC value of > 426580 using the HPLC method. The Log KOC can be extrapolated from the regression curve to be 8.3. The experimentally determined result was confirmed by a model calculation, which results in a value of log KOC > 7.81. The data indicates that Dilauroyl peroxide (CAS# 105-74-8) will be adsorbed by organic carbon in soil. Dilauroyl peroxide (CAS# 105-74-8) is immobile.
- Executive summary:
PURPOSE
The adsorption coefficient is defined as the ratio between the concentration of the substance in the soil/sludge and the concentration of the substance in the aqueous phase at adsorption equilibrium. The adsorption coefficient normalized to the organic carbon content of the soil KOC is a useful indicator of the binding capacity of a chemical on organic matter of soil and sewage sludge and allows comparisons to be made between different chemicals.
The experimental method uses HPLC for the estimation of the adsorption coefficient KOC in soil and sewage sludge.
The log of the adsorption coefficient (KOC) of Dilauroyl peroxide (# 105-74-8) was estimated to be
log KOC> 5.63 which is equal to a KOCvalue of >426580
using the HPLC method. The retention times after immediately injection and injection after 4 hours did not show significant differences. Thus, the test item solution was found to be stable during testing. The Log KOCcan be extrapolated from the regression curve to be 8.3.
The experimentally determined result was confirmed by a model calculation, which results in a value of log KOC > 7.81.
The data indicates that Dilauroyl peroxide (# 105-74-8) will be adsorbed by organic carbon in soil. Dilauroyl peroxide (# 105-74-8) can be classified to be immobile according these study results.
Reference
In a preliminary test, the stability of the test item was observed. The retention times of the injected test item solution did not differ after 4 hours of alteration compared to the test item solution injected immediately after preparation. Thus, the test item solution was found to be stable during testing.
The test item solution of the main test was injected three times and the reference mix solution was injected six times.In the present study the reference items covered the range from log KOC 1.25 to log KOC 5.63.The retention time of the test item is higher than the retention time of the reference item (2,4‑DDT) with the highest log KOC(5.63, which is equal to a KOCvalue of 426580).Therefore, the log KOCof the test item is> 5.63, which is equal to a KOCvalue of> 426580 using the HPLC method. This value indicates that Dilauroyl peroxide (# 105-74-8) is immobile and will be adsorbed by organic carbon in soil.
The Log KOCcan be extrapolated from the regression curve to be 8.3.
A typical HPLC chromatogram of the reference standard mixture is shown in the attached Figure 1. An HPLC chromatogram of the test item is shown in the attached Figure 2. A typical chromatogram of the determination of the dead-time is given in the attached Figure 3. The chromatography of the test item resulted in one peak with a well-defined and reproducible retention time. The HPLC method was therefore considered to be suitable for the purpose of the study.
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 log k’ was plotted versus KOCfor each component to obtain a regression curve (Table 2 and attached 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) |
1.344 |
1.338 |
1.344 |
|
|
|
Reference Items: |
||||||
Acetanilide |
2.921 |
2.931 |
2.932 |
2.923 |
2.921 |
2.920 |
Isoproturon |
3.303 |
3.314 |
3.315 |
3.307 |
3.305 |
3.303 |
Linuron |
3.572 |
3.582 |
3.583 |
3.576 |
3.572 |
3.571 |
Pyrazophos |
4.335 |
4.344 |
4.347 |
4.338 |
4.335 |
4.338 |
Diclofop-methyl |
4.911 |
4.916 |
4.921 |
4.914 |
4.905 |
4.913 |
2,4-DDT |
5.523 |
5.523 |
5.532 |
5.524 |
5.512 |
5.524 |
Dilauroyl peroxide (CAS# 105-74-8): |
|
|
|
|||
TestItemPeak |
9.636 |
9.691 |
9.667 |
|
|
|
The retention time of the test item peak in all runs is longer than the retention time of 2,4-DDT, the last reference item on the list of the guideline with a log KOCvalue of 5.63.
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) |
3 |
1.34 |
- |
- |
|
Reference Items: |
|||||
Acetanilide |
6 |
2.92 |
1.18 |
0.07 |
1.25 |
Isoproturon |
6 |
3.31 |
1.46 |
0.17 |
1.86 |
Linuron |
6 |
3.58 |
1.66 |
0.22 |
2.59 |
Pyrazophos |
6 |
4.34 |
2.23 |
0.35 |
3.65 |
Diclofop-methyl |
6 |
4.91 |
2.66 |
0.43 |
4.20 |
2,4-DDT |
6 |
5.52 |
3.12 |
0.49 |
5.63 |
|
slope = |
|
|
|
0.099 |
Linear Regression: |
y-axis intercept = |
-0.028 |
|||
|
coefficient of regression (r) = |
0.986 |
Description of key information
The log Koc based on extrapolation of retention times derived experimentally was 8.3. However, this is significantly above the highest reference substance and should be used in the absence of a more accurate value, with caution.
Key value for chemical safety assessment
- Koc at 20 °C:
- 199 526 231
Additional information
An adsorption study was performed using the HPLC method. Using the standard reference values the log Kow was found to be higher than that of the highest reference substance. However various methods were used in complement in order to provide a value. The only method that successfully calculated a value was the use of extrapolated retention times. The log Koc based on this was 8.3 and should be used with caution.
[LogKoc: 8.3]
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