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EC number: 222-340-0 | CAS number: 3437-84-1
- 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
Hydrolysis
Administrative data
Link to relevant study record(s)
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Juli 2011
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: Well conducted study under GLP, according to OECD principles, certificate of analysis included in the report.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 111 (Hydrolysis as a Function of pH)
- Deviations:
- yes
- Remarks:
- screening Tier 1 was performed at 15 degree C
- Principles of method if other than guideline:
- Based on the information of the sponsor the test substance was known to be thermically very unstable at ambient and higher temperatures. Therefore the screening hydrolysis study (Tier 1) was performed at a test temperature of 15°C instead of the required 50°C according to the guideline.
- GLP compliance:
- yes (incl. QA statement)
- Radiolabelling:
- no
- Analytical monitoring:
- yes
- Details on sampling:
- At the moment the test substance was added to the buffer solutions the first sample was taken from a test vessel and analyzed using the analytical method. Depending on the tested pH value the subsequent samples were taken on different time intervals and analyzed to determine the percentage of hydrolysis. Samples were analyzed directly after sampling in order to stop the hydrolysis.
- Buffers:
- Sterile test buffer solutions of pH 4.0, 7.0 and 9.0 were prepared according to the description in Annex 3 of OECD 111 and purged with nitrogen for at least 5 minutes. Sterilization of the buffer solutions was performed by autoclaving at 121°C for at least 20 minutes.
- Details on test conditions:
- Chemicals
All chemicals used were of reagent grade quality, unless stated otherwise.
Buffer solutions of the different pH values were prepared according to the information as described in Annex 3 of OECD 111.
Materials
All glassware and buffer solutions were sterilised. Buffer solutions were flushed with nitrogen to minimise oxidation. Test vessels were kept under dark conditions to avoid eventual photo degradation. A temperature controlled water bath was used; temperature was measured using a calibrated thermometer. pH was measured using a pH meter. - Duration:
- 180 min
- pH:
- 4
- Temp.:
- 15
- Initial conc. measured:
- 392.2 mg/L
- Duration:
- 180 min
- pH:
- 7
- Temp.:
- 15
- Initial conc. measured:
- 365.6 mg/L
- Duration:
- 120 min
- pH:
- 9
- Temp.:
- 15
- Initial conc. measured:
- 406.3 mg/L
- Preliminary study:
- The hydrolysis screening test was performed separately for each pH value tested. The test substance showed hydrolysis at all pH values, hydrolysis rate increased at higher pH values. The half-lives were calculated to be far less than 12 hours, the limit for conducting a water solubility test according to the REACH guidance
- Test performance:
- Only the screening part (Tier 1) of the hydrolysis study was conducted.
- Transformation products:
- not measured
- Details on hydrolysis and appearance of transformation product(s):
- pH value of 4
The temperature during the test varied between 14.9 and 15.0°C. It was observed that more than 85% of the test substance was hydrolyzed in 3 hours. Using the information gathered during the screening hydrolysis test also a calculation of the half-life (t ½) was determined by applying the Arrhenius relationship, the relation between the logarithmic value of the concentration of the test substance and the time. The half-life for the test substance was calculated to be 63 minutes.
pH value of 7
The temperature during the test varied between 14.8 and 15.1°C. It was observed that more than 88% of the test substance was hydrolyzed in 3 hours. Using the information gathered during the screening hydrolysis test also a calculation of the half-life (t ½) was determined by applying the Arrhenius relationship, the relation between the logarithmic value of the concentration of the test substance and the time. The half-life for the test substance was calculated to be 57 minutes.
pH value of 9
The temperature during the test varied between 14.8 and 15.1°C. It was observed that more than 93% of the test substance was hydrolyzed in 2 hours. Using the information gathered during the screening hydrolysis test also a calculation of the half-life (t ½) was determined by applying the Arrhenius relationship, the relation between the logarithmic value of the concentration of the test substance and the time. The half-life for the test substance was calculated to be 29 minutes. - pH:
- 4
- Temp.:
- 15 °C
- Hydrolysis rate constant:
- 0.011 min-1
- DT50:
- 63 min
- Type:
- (pseudo-)first order (= half-life)
- Remarks on result:
- other: regression equation: y=-0.0048x+2.6169; r2=0.9989
- pH:
- 7
- Temp.:
- 15 °C
- Hydrolysis rate constant:
- 0.012 min-1
- DT50:
- 57 min
- Type:
- (pseudo-)first order (= half-life)
- Remarks on result:
- other: regression equation: y=-0.0053x+2.6107; r2=0.9927
- pH:
- 9
- Temp.:
- 15 °C
- Hydrolysis rate constant:
- 0.024 min-1
- DT50:
- 29 min
- Type:
- (pseudo-)first order (= half-life)
- Remarks on result:
- other: regression equation: y=-0.0102+2.6021; r2=0.9881
- Validity criteria fulfilled:
- yes
- Conclusions:
- At a pH value of 4 the half-life (t½) for diisobutyryl peroxide at a temperature of 15°C was calculated to be 63 minutes.
At a pH value of 7 the half-life (t½) for diisobutyryl peroxide at a temperature of 15°C was calculated to be 57 minutes.
At a pH value of 9 the half-life (t½) for diisobutyryl peroxide at a temperature of 15°C was calculated to be 29 minutes.
Based on the determined half-lifes, being all far less than 12 hours, no water solubility testing is required accroding to the REACH Guidance - Executive summary:
A screening hydrolysis of diisobutyryl peroxide (Trigonox 187-C30) was determined at 15°C and at the pH values of 4, 7 and 9 with GLP, in agreement with OECD guideline 111.
Based on the information of the sponsor the test substance was known to be thermically very unstable at ambient and higher temperatures. Therefore the screening hydrolysis study (Tier 1) was performed at a test temperature of 15°C instead of the required 50°C according to the guideline.
The results of this hydrolysis study will be used for determination if it is useful to conduct also a water solubility test for the test substance. If the half life would occur to be less than 12 hours no water solubility testing would be required. Therefore only the screening part (Tier 1) of the hydrolysis study was conducted.
- Endpoint:
- hydrolysis
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study is a research based experiment, not conducted to GLP, Not conducted to a standard guideline. Considered reliable with restrictions.
- Principles of method if other than guideline:
- See section 6.6: 3437 -84 -1, Additional ecotoxicological information, ter Weele, 2012.
- GLP compliance:
- no
- Radiolabelling:
- no
- Analytical monitoring:
- yes
- Details on results:
- See section 6.6: 3437 -84 -1, Additional ecotoxicological information, ter Weele, 2012.
- Conclusions:
- For the degradation of Diisobutryl peroxide in water it can be concluded that:
- Bisisobutyryl peroxide decomposes completely in water after 60 minutes at 27°C (room temperature).
- The decomposition products observed are: Isobutyric acid (IBA), Isopropanol, propene and acetone.
- The main decomposition/hydrolysis product found is Isobutyric acid.
- Propene is also likely to be one of the main decomposition products but the exact amount can not be determined due to its high volatile nature. - Executive summary:
See section 6.6: 3437 -84 -1, Additional ecotoxicological information, ter Weele, 2012.
Referenceopen allclose all
Results screening hydrolysis, pH 4
Sample |
Time |
Conc. |
Hydrolysis |
Log Ct |
|
min. |
mg/l |
% |
|
pH 4, t=0 min. |
3 |
392.2 |
0.0 |
2.59 |
pH 4, t= 20 min. |
20 |
329.8 |
15.9 |
2.52 |
pH 4, t= 40 min. |
40 |
269.9 |
31.2 |
2.43 |
pH 4, t= 60 min. |
60 |
213.1 |
45.7 |
2.33 |
pH 4, t= 90 min. |
90 |
161.0 |
58.9 |
2.21 |
pH 4, t= 120 min. |
120 |
110.9 |
71.7 |
2.04 |
pH 4, t= 180 min. |
180 |
56.1 |
85.7 |
1.75 |
Results screening hydrolysis, pH 7
Sample |
Time |
Conc. |
Hydrolysis |
Log Ct |
|
min. |
mg/l |
% |
|
pH 7, t=0 min. |
3 |
365.6 |
0.0 |
2.56 |
pH 7, t= 20 min. |
20 |
309.9 |
15.2 |
2.49 |
pH 7, t= 40 min. |
40 |
254.7 |
30.3 |
2.41 |
pH 7, t= 60 min. |
60 |
205.4 |
43.8 |
2.31 |
pH 7, t= 90 min. |
90 |
142.5 |
61.0 |
2.15 |
pH 7, t= 120 min. |
120 |
100.7 |
72.5 |
2.00 |
pH 7, t= 180 min. |
180 |
41.0 |
88.8 |
1.61 |
Results screening hydrolysis, pH 9
Sample |
Time |
Conc. |
Hydrolysis |
Log Ct |
|
min. |
mg/l |
% |
|
pH 9, t=0 min. |
3 |
406.3 |
0.0 |
2.61 |
pH 9, t= 20 min. |
20 |
264.9 |
34.8 |
2.42 |
pH 9, t= 40 min. |
40 |
150.8 |
62.9 |
2.18 |
pH 9, t= 60 min. |
60 |
86.1 |
78.8 |
1.94 |
pH 9, t= 80 min. |
80 |
53.4 |
86.8 |
1.73 |
pH 9, t= 100 min. |
100 |
37.3 |
90.8 |
1.57 |
pH 9, t= 120 min. |
120 |
28.0 |
93.1 |
1.45 |
Calculation half-lives
Kobs |
t1/2 |
||
slope |
(min-1) |
(min) |
|
pH 4 |
-0.00476812 |
0.010979001 |
63 |
pH 7 |
-0.005326768 |
0.012265337 |
57 |
pH 9 |
-0.010217028 |
0.023525577 |
29 |
Kobs= -ln(10) * slope
t1/2= ln(2) / Kobs
Summary of method validations analytical method
Validation |
Parameter |
Result |
Requirement |
Linearity |
R squared |
R2= 0.998492738 |
R2≥ 0.98 |
Reproducibility |
Coefficient of variation |
12.5% |
< 20% |
Reproducibility |
Coefficient of variation |
1.5% |
< 20% |
Limit of detection |
|
3.75 mg/L |
|
Recovery aqueous |
Mean |
76.9% |
70 – 110% |
Standard deviation |
3.9% |
< 20% |
|
Recovery aqueous |
Mean |
86.1% |
70 – 110% |
Standard deviation |
4.7% |
< 20% |
|
Recovery aqueous |
Mean |
81.4% |
70 – 110% |
Standard deviation |
1.6% |
< 20% |
|
System stability |
Deviation control stand. from expected value |
1.9 to -3.1% |
< 10% |
See section 6.6: 3437 -84 -1, Additional ecotoxicological information, ter Weele, 2012.
Description of key information
At a pH value of 4 the half-life (t½) for diisobutyryl peroxide at a temperature of 15°C was calculated to be 63 minutes.
At a pH value of 7 the half-life (t½) for diisobutyryl peroxide at a temperature of 15°C was calculated to be 57 minutes.
At a pH value of 9 the half-life (t½) for diisobutyryl peroxide at a temperature of 15°C was calculated to be 29 minutes.
For the degradation of Diisobutryl peroxide in water it can be concluded that:
- The decomposition products observed are: Isobutyric acid (IBA), Isopropanol, propene and acetone.
- The main decomposition/hydrolysis product found is Isobutyric acid.
- Propene is also likely to be one of the main decomposition products but the exact amount can not be determined due to its high volatile nature.
Key value for chemical safety assessment
- Half-life for hydrolysis:
- 57 min
- at the temperature of:
- 15 °C
Additional information
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