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Reaction products of 1-(substitutedphenyl)urea coupled with diazotated potassium sodium substituted-5-{[2-(substituted)ethyl]sulfonyl}benzenesulfonate, further condensed with 2,4,6-trichloro-1,3,5-triazine, further converted with disubstituted benzene-1,4-disulfonic acid in aq. sodium hydroxide
EC number: - | CAS number: -
- 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:
- The study was conducted between 29 September 2015 and 24 February 2016
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: GLP guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 107 (Partition Coefficient (n-octanol / water), Shake Flask Method)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method A.8 (Partition Coefficient)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Type of method:
- shake-flask method to: flask method
- Partition coefficient type:
- octanol-water
- Analytical method:
- high-performance liquid chromatography
- Type:
- Pow
- Partition coefficient:
- 0
- Temp.:
- 22 °C
- pH:
- 7
- Type:
- log Pow
- Partition coefficient:
- -3.66
- Temp.:
- 22 °C
- pH:
- 7
- Details on results:
- pH of n-octanol saturated water: 7.0
pH of stock solution: 6.4
Temperature: 22.0 ± 0.5 °C
Overall Pow: 2.21E-04
Log10 Pow : -3.66
Pow standard deviation: 2.29E-05 - Conclusions:
- The partition coefficient of the test item has been determined to be 2.21E-04 at 22.0 ± 0.5 °C, log10 Pow -3.66.
- Executive summary:
Partition Coefficient (n-Octanol/Water). 2.21 x 10-4at 22.0 ± 0.5 °C, log10Pow-3.66, using the shake-flask method, designed to be compatible with Method A8 Partition Coefficient of Commission Regulation (EC) No 440/2008 of 30 May 2008 and Method 107 of the OECD Guidelines for Testing of Chemicals, 27 July 1995.
Reference
The mean peakareas obtained for the standard, stock and sample solutions are shown in the following two tables:
Organic Phase
Solution |
Mean total peakarea |
Standard 10.2 mg/L |
1.9745 x 106 |
Standard 10.0 mg/L |
1.8764 x 106 |
Organic phase matrix blank |
N.D. |
Sample 1 |
4.0776 x 105 |
Sample 2 |
4.6124 x 105 |
Sample 3 |
3.4795 x 105 |
Sample 4 |
4.2874 x 105 |
Sample 5 |
4.6344 x 105 |
Sample 6 |
4.5570 x 105 |
Aqueous Phase
Solution |
Mean total peakarea |
Standard 101 mg/L |
2.3090 x 107 |
Standard 106 mg/L |
2.4324 x 107 |
Aqueous phase matrix blank |
N.D. |
Sample 1 |
2.2918 x 107 |
Sample 2 |
2.2838 x 107 |
Sample 3 |
2.3484 x 107 |
Sample 4 |
2.3473 x 107 |
Sample 5 |
2.3879 x 107 |
Sample 6 |
2.3744 x 107 |
Stock solution A |
2.3468 x 107 |
Stock solution B |
2.3186 x 107 |
N.D. = None detected
The total weights (mg) and analyzed concentration (mg/L) of the respective phases are shown in the following table:
Sample number |
Total weight (mg)* |
Organic phase |
Aqueous phase |
% recovery |
|||
Analyzed concentration (mg/L)** |
Weight (mg)† |
Analyzed concentration (mg/L) |
Weight (mg)† |
pH |
|||
1 |
1.12 x 103 |
2.15 |
0.118 |
1.00 x 104 |
1.10 x 103 |
6.3 |
98.3 |
2 |
1.12 x 103 |
2.43 |
0.134 |
9.96 x 103 |
1.10 x 103 |
6.3 |
97.9 |
3 |
865 |
1.83 |
0.156 |
1.02 x 104 |
871 |
6.3 |
101 |
4 |
865 |
2.26 |
0.192 |
1.02 x 104 |
870 |
6.3 |
101 |
5 |
560 |
2.44 |
0.269 |
1.04 x 104 |
573 |
6.3 |
102 |
6 |
560 |
2.40 |
0.264 |
1.04 x 104 |
570 |
6.3 |
102 |
* From analysis of the stock solution
** See discussion
† From analysis of the respective phase
The partition coefficient determined for each sample is shown in the following table:
Sample number |
Organic/aqueous volume ratio |
Partition coefficient |
Log10Pow |
Mean partition coefficient |
1 |
1:2 |
2.15 x 10-4 |
-3.67 |
2.29 x 10-4 |
2 |
2.44 x 10-4 |
-3.61 |
||
3 |
1:1 |
1.79 x 10-4 |
-3.75 |
2.00 x 10-4 |
4 |
2.21 x 10-4 |
-3.66 |
||
5 |
2:1 |
2.34 x 10-4 |
-3.63 |
2.33 x 10-4 |
6 |
2.32 x 10-4 |
-3.64 |
Validation
Organic phase: The linearity of the detector response with respect to concentration was assessed over the concentration range of 2.54 to 20.3 mg/L (n = 6). The results were satisfactory with a correlation coefficient (r) of 0.9996 being obtained.
Aqueous phase: The linearity of the detector response with respect to concentration was assessed over the nominal concentration range of 25.0 to 200 mg/L (n = 6). The results were satisfactory with a correlation coefficient (r) of 1.0000 being obtained.
Description of key information
The partition coefficient (n-Octanol/Water)was found to be 2.21 x 10-4at 22.0 ± 0.5 °C, log10Pow-3.66, using the shake-flask
method.
Key value for chemical safety assessment
- Log Kow (Log Pow):
- -3.66
- at the temperature of:
- 22 °C
Additional information
The partition coefficient (n-Octanol/Water)was found to be 2.21 x 10-4at 22.0 ± 0.5 °C, log10Pow-3.66, using the shake-flask
method.
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