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EC number: 242-893-1 | CAS number: 19223-55-3
- 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
Partition coefficient
Administrative data
Link to relevant study record(s)
- Endpoint:
- partition coefficient
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- From 4 October 2012 to 25 January 2013
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 123 (Partition Coefficient (1-Octanol / Water), Slow-Stirring Method)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- 2012-12-15
- Type of method:
- slow-stirring method
- Partition coefficient type:
- octanol-water
- Analytical method:
- high-performance liquid chromatography
- Key result
- Type:
- log Pow
- Partition coefficient:
- 2.1
- Temp.:
- 25 °C
- pH:
- >= 7.6 - <= 7.85
- Remarks on result:
- other: log Pow of the C12 fraction (weighted average value)
- Conclusions:
- Using the low stirring method, it was shown that the weighed average value of the 1-octanol/water partition coefficient log10 Pow of the C12 fraction present in test item is equal to 2.10 ± 0.02 at 25 ± 1°C.
- Executive summary:
The n-octanol/water partition coefficient of the substance EC 939-455-3 (freeze-dried) was investigated in a GLP-compliant study performed in accordance with OECD Guideline 123 (Partition Coefficient (1-Octanol / Water), Slow-Stirring Method). The mean n-octanol/water partition coefficient log10 Pow of the C12 fraction present in test item was 2.10 ± 0.02 at 25°C.
- Endpoint:
- partition coefficient
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- 1. HYPOTHESIS FOR THE ANALOGUE APPROACH
C8-C18 AAPHS and C12 AAPHS have the same functional groups, and general composition. The main variable resides in the alkyl chain distribution.
2. SOURCE AND TARGET CHEMICAL(S) (INCLUDING INFORMATION ON PURITY AND IMPURITIES)
Source chemical = C8-18 cocamidopropyl hydroxysultaine (EC 939-455-3)
Target chemical = C12 cocamidopropyl hydroxysultaine (EC 242-893-1)
3. ANALOGUE APPROACH JUSTIFICATION
The alkyl C-chain distribution of the source chemical significantly overlaps with the one of the target chemical, the C12-alkyl derivative being the major constituent in both chemicals. The structural differences in side C-chains is not expected to lead to significant differences on phys-chem properties.
4. DATA MATRIX: see "Documentation and scientific justification of the read-across approach" in section 13.2. - Reason / purpose for cross-reference:
- read-across source
- Key result
- Type:
- log Pow
- Partition coefficient:
- 2.1
- Temp.:
- 25 °C
- pH:
- >= 7.6 - <= 7.85
- Remarks on result:
- other: log Pow of the C12 fraction (weighted average value)
- Remarks:
- read-across from EC 939-455-3
- Conclusions:
- By analogy with the source substance EC 939-455-3, a n-octanol/water partition coefficient log10 Pow of 2.10 ± 0.02 at 25°C was reported for the target substance (2-Hydroxy-3-sulphopropyl) dimethyl[3-[(1-oxododecyl) amino]propyl]ammonium hydroxide (EC 242-893-1).
Referenceopen allclose all
Results:
Calibration curve for 1 -octanol phases analysis
Reference of calibration solution | Peak area (area units) | Conc (mg/L) | Response factor | Final Volume (ml) | Dilution factor | Sample weight (mg) | Conc back-calc | Diff |
A | C= (w*P)/(V*Df) | RF = A/C | V | Df | w | C'= (A-b)/a | % | |
Lin 25% | 1830264 | 19.31 | 9.48048E+04 | 100 | 4.0 | 20.11 | 18.49 | -4.25% |
Lin 25% | 1845749 | 19.31 | 9.56069E+04 | 100 | 4.0 | 20.11 | 18.65 | -3.37% |
Lin 50% | 3905839 | 39.71 | 9.83700E+04 | 100 | 1.0 | 10.34 | 40.46 | 1.89% |
Lin 50% | 3915468 | 39.71 | 9.86125E+04 | 100 | 1.0 | 10.34 | 40.56 | 2.14% |
Lin 75% | 5574447 | 57.14 | 9.75591E+04 | 100 | 1.0 | 14.88 | 58.12 | 1.72% |
Lin 75% | 5493480 | 57.14 | 9.61421E+04 | 100 | 1.0 | 14.88 | 57.26 | 0.21% |
REF05 | 7463735 | 78.84 | 9.46752E+04 | 100 | 1.0 | 20.53 | 78.11 | -0.91% |
REF05 | 7502554 | 78.84 | 9.51676E+04 | 100 | 1.0 | 20.53 | 78.52 | -0.39% |
Lin 125% | 9176261 | 96.38 | 9.52052E+04 | 100 | 1.0 | 25.10 | 96.24 | -0.16% |
Lin 125% | 9169449 | 96.38 | 9.51346E+04 | 100 | 1.0 | 25.10 | 96.16 | -0.23% |
Lin 150% | 10797715 | 112.59 | 9.59040E+04 | 100 | 1.0 | 29.32 | 113.40 | 0.72% |
Lin 150% | 10661311 | 112.59 | 9.46925E+04 | 100 | 1.0 | 29.32 | 111.95 | -0.57% |
Response function Peak Area = 94488.13*Concentration + 83143.53
The graph of the calibration curve is shown in Attachment 1.
Calibration curve for water phase analysis:
Reference of calibration solution | Peak area (area units) | Conc (mg/L) | Response factor | Final Volume (ml) | Dilution factor | Sample weight (mg) | Conc back-calc | Diff |
A | C= (w*P)/(V*Df) | RF = A/C | V | Df | w | C'= (A-b)/a | % | |
REF 05 dil20 | 369203 | 3.94 | 9.36645E+04 | 100 | 20 | 20.53 | 3.90 | -1.01% |
REF 05 dil20 | 351222 | 3.94 | 8.91028E+04 | 100 | 20 | 20.53 | 3.69 | -6.34% |
REF 05 dil10 | 699817 | 7.88 | 8.87696E+04 | 100 | 10 | 20.53 | 7.74 | -1.78% |
REF 05 dil10 | 710573 | 7.88 | 9.01340E+04 | 100 | 10 | 20.53 | 7.86 | -0.25% |
REF 05 dil5 | 1413337 | 15.77 | 8.96387E+04 | 100 | 5 | 20.53 | 16.03 | 1.65% |
REF 05 dil5 | 1437975 | 15.77 | 9.12013E+04 | 100 | 5 | 20.53 | 16.32 | 3.49% |
REF 05 dil4 | 1720595 | 19.71 | 8.73009E+04 | 100 | 4 | 20.53 | 19.60 | -0.56% |
REF 05 dil4 | 1733152 | 19.71 | 8.79380E+04 | 100 | 4 | 20.53 | 19.75 | 0.20% |
REF 05 dil2,5 | 2735643 | 31.53 | 8.67520E+04 | 100 | 2.5 | 20.53 | 31.40 | -0.44% |
REF 05 dil2,5 | 2734947 | 31.53 | 8.67299E+04 | 100 | 2.5 | 20.53 | 31.39 | -0.48% |
Response function Peak Area = 86061.61*Concentration + 33709.60
The graph of the calibration curve is shown in Attachment 1.
Main test results:
The three filtered aliquots of 50 mL obtained from the 1-octanol saturated phase were analyzed and the concentrations of the C12 fraction were found to be equal to 1.86 g/L (4.84 g/L of test item). This value is lower than the theoretical one and shows a weak dissolution of test item during the two hours of preparation.
The results for the C12 fraction concentration in the two phases at each time are given in the following table:
Vessel number and sampling time | Concentration in the aqueous phase (mg/l) | Concentration in the 1-octanol phase (mg/l) | Pow ratio | log Pow |
12-091 Z1T=93H | 12.70 | 1499 | 118.00 | 2.07 |
12-091 Z2T=93H | 11.44 | 1524 | 133.20 | 2.12 |
12-091 Z3T=93H | 12.14 | 1558 | 128.30 | 2.11 |
12-091 Z1T=117H | 11.24 | 1497 | 133.20 | 2.12 |
12-091 Z2T=117H | 11.94 | 1539 | 128.90 | 2.11 |
12-091 Z3T=117H | 11.78 | 1582 | 134.30 | 2.13 |
12-091 Z1T=137H | 11.54 | 1503 | 130.20 | 2.11 |
12-091 Z2T=137H | 12.18 | 1601 | 131.40 | 2.12 |
12-091 Z3T=137H | 13.38 | 1629 | 121.70 | 2.09 |
12-091 Z1T=144H | 11.48 | 1511 | 131.60 | 2.12 |
12-091 Z2T=144H | 12.78 | 1513 | 118.40 | 2.07 |
12-091 Z3T=144H | 13.26 | 1569 | 118.30 | 2.07 |
12-091 Z1T=163H | 12.02 | 1489 | 123.90 | 2.09 |
12-091 Z2T=163H | 12.14 | 1552 | 127.80 | 2.11 |
12-091 Z3T=163H | 12.34 | 1599 | 129.60 | 2.11 |
The pH of the saturated water phase at the start of the test was 7.88 at 21 °C.The measured pH of the aqueous phases were between 7.60 and 7.85 at 21 °C.
The average value of log Pow of the different vessel units is calculated as the average of the results of the individual experimental units weighed with their respective variances.The results are shown in the following table.
Vessel Z1 | Mean value Z1 | Standard deviation Z1 | Vessel Z2 | Mean value Z2 | Standard deviation Z2 | Vessel Z3 | Mean value Z3 | Standard deviation Z3 |
2,07 | 2,102 | 0,02 | 2,12 | 2,106 | 0,02 | 2,11 | 2,102 | 0,02 |
2,12 | 2,11 | 2,13 | ||||||
2,11 | 2,12 | 2,09 | ||||||
2,12 | 2,07 | 2,07 | ||||||
2,09 | 2,11 | 2,11 |
Mean / Vessel | Average | Standard deviation | |
Vessel Z1 | 2,102 | 2,103 | 0,02 |
Vessel Z2 | 2,106 | ||
Vessel Z3 | 2,102 |
Using the low stirring method, it was shown that the weighed average value of the 1-octanol/water partition coefficient log10 Pow of the C12 fraction present in test item is equal to 2.10 ± 0.02 at 25 ± .1°C.
Demonstration of attainment of equilibrium:
Achievement of chemical equilibrium is demonstrated by plotting for each vessel unit log Pow against time as shown in the figures shown in Attachment 2 where the slopes are very near to 0.
Description of key information
As the n-octanol/water partition coefficient of the REACh substance (2-Hydroxy-3-sulphopropyl) dimethyl[3-[(1-oxododecyl) amino]propyl]ammonium hydroxide (EC 242-893-1) has not been determined experimentally, a read-across approach was followed to fill in the endpoint. The n-octanol/water partition coefficient of a structural analogue substance (= source substance EC 939-455-3, C8-18 AAPHS) was investigated in a GLP-compliant study (Meriaux, 2013) performed in accordance with OECD Guideline 123 (Partition Coefficient (1-Octanol / Water), Slow-Stirring Method). The mean n-octanol/water partition coefficient log10 Pow of the analogue substance was 2.10 ± 0.02 at 25°C. By analogy, a n-octanol/water partition coefficient log10 Pow of 2.10 ± 0.02 at 25°C is reported for the target REACh substance (EC 242-893-1, C12 AAPHS).
The alkyl C-chain distribution of the source substance EC 939-455-3 significantly overlaps with the one of the target substance EC 242-893-1, the C12-alkyl derivative being the major constituent in both chemicals. The structural differences in side C-chains is not expected to lead to significant differences on phys-chem properties.
Key value for chemical safety assessment
- Log Kow (Log Pow):
- 2.1
- at the temperature of:
- 25 °C
Additional information
The n-octanol/water partition coefficient of the structural analogue substance (= source substance EC 939-455-3) was investigated in a GLP-compliant study (Meriaux, 2013) performed in accordance with standard methods, without deviations. The study is considered as reliable (Klimisch 1) and was selected as key study for the endpoint of the target substance EC 242-893-1.
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