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EC number: 235-468-7 | CAS number: 12237-62-6 This substance is identified in the Colour Index by Colour Index Constitution Number, C.I. 42535:3.
- 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
Adsorption / desorption
Administrative data
Link to relevant study record(s)
- Endpoint:
- adsorption / desorption: screening
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- Experimental test result performed using standard test guidelines
- 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))
- GLP compliance:
- no
- Type of method:
- HPLC estimation method
- Media:
- soil/sewage sludge
- Radiolabelling:
- no
- Test temperature:
- 25°C
- Details on study design: HPLC method:
- HPLC Procedure:
The solutions of the test chemical and reference substances were prepared in acetonitrile. Each of the reference substances and test chemical were analysed by HPLC. The column was saturated with solvent (mobile phase) in isocratic mode on above chromatographic conditions mentioned. After 20 min of column saturation with mobile phase, sequential analysis of urea (for dead time: t0), reference substances and test chemical was performed on HPLC. All the HPLC runs were performed in duplicates. Retention time tR was measured to calculate the capacity factors k (mentioned in below equation), it was then converted in log to obtain log k. A standard curve between log k versus log Koc was plotted to obtain the value of log Koc of test chemical.
K= tR -t0
t0
where
k= capacity factor,
tR= retention time of test substance and reference substance.
t0=retention time of Urea.
Operating Conditions:
HPLC Model No. : Agilent Technologies,1260 Infinity
Flow Rate : 1.0ml/min
Column : ZORBAX Eclipse Plus C18, 4.6×100mm, 3.5 μm
Mobile phase : ACN : water (55:45)
Temperature : 25°C
Detector : Diode Array Detector @210nm
Injector : Autosampler
Injector volume : 20μl
Data Acquisition software : ChemStationOpen lab Control Panel - Analytical monitoring:
- not specified
- Key result
- Sample No.:
- #1
- Type:
- log Koc
- Value:
- 2.787 dimensionless
- pH:
- 7.4
- Temp.:
- 25 °C
- Remarks on result:
- other: logKoc was reported to be 2.787±0.001
- Details on results (HPLC method):
- The Adsorption coefficient (KOC) on soil and on sewage sludge of the test chemical was determined to be 2.787±0.001 at 25°C
- Transformation products:
- not specified
- Validity criteria fulfilled:
- yes
- Conclusions:
- The Adsorption Coefficient of test chemiical was determined as per the HPLC method (OECD Guideline-121). The Log Koc value was determined to be 2.787±0.001 at 25°C. Thus based on the result it is concluded that the test chemical has a moderate sorption to soil and sediment and therefore have slow migration potential to ground water.
- Executive summary:
The adsorption coefficient Koc in soil and in sewage sludge of test chemical was determined by the Reverse Phase High Performance Liquid Chromatographic method according to OECD Guideline No. 121 for testing of Chemicals. The solutions of the test substance and reference substances were prepared in appropriate solvents. The sample of test chemical was prepared by adding 10 mg in acetonitrile to prepare 1000 mg/L test solution, sonicated for 1 mins and filtered through 0.22 μm nylon syringe filter. pH of the resulting solution was 7.4. The analysis was performed at constant recommended conditions such as temperature 25°C (solvent: water) ratio 55:45 at the flow rate of 1 mL/min at 210 nm. The reference substances were chosen according to estimated Koc range of the test substance and generalize calibration graph was prepared. Selected reference substances and test chemical were prepared in acetonitrile with concentration of 400 mg/L. Both were analyzed on HPLC considering the similar conditions. After analyzing on above conditions calibration curve of selected reference substances was prepared to obtain log Koc value. The reference substances were p-Toluamide, Aniline, N-methylaniline, 4-Chloroaniline, phenanthrene, Naphthalene, DDT, having Koc value
ranging from 1.8 to 2.9. The Log Koc value was test chemical was determined to be 2.787±0.001 at 25°C. Thus, based on the result it is concluded that the test chemical has a moderate sorption to soil and sediment and therefore have slow migration potential to ground water.
Reference
Result:
Table: List of reference substances
Reference Substance |
Tr1 |
Tr2 |
Mean tR± S.D. |
K |
Log K |
Log Koc |
Urea |
2.087 |
2.087 |
2.087±0.000 |
NA |
NA |
NA |
p-Toluamide |
3.132 |
3.133 |
3.133±0.001 |
0.501 |
-0.3 |
1.8 |
Aniline |
3.831 |
3.834 |
3.833±0.002 |
0.836 |
-0.078 |
2.1 |
N-methylaniline |
4.438 |
4.452 |
4.445±0.010 |
1.13 |
0.053 |
2.2 |
4-Chloroaniline |
4.044 |
4.047 |
4.046±0.002 |
0.938 |
-0.028 |
2.1 |
phenanthrene |
6.05 |
6.06 |
6.055±0.007 |
1.901 |
0.279 |
2.5 |
Naphthalene |
5.044 |
5.048 |
5.046±0.003 |
1.418 |
0.152 |
2.4 |
DDT |
9.846 |
9.863 |
9.855±0.012 |
3.722 |
0.571 |
2.9 |
Table: Adsorption coefficient (logKoc) value of test chemical.
Test substance |
K |
Log k |
Log Koc
|
Mean of Log Koc ± S.D.
|
|
Rt1 |
8.144 |
2.902 |
0.463 |
2.787 |
2.787±0.001
|
Rt2 |
8.159 |
2.909 |
0.464 |
2.788
|
Description of key information
The adsorption coefficient Koc in soil and in sewage sludge of test chemical was determined by the Reverse Phase High Performance Liquid Chromatographic method according to OECD Guideline No. 121 for testing of Chemicals (Experimental study report, 2019). The solutions of the test substance and reference substances were prepared in appropriate solvents. The sample of test chemical was prepared by adding 10 mg in acetonitrile to prepare 1000 mg/L test solution, sonicated for 1 mins and filtered through 0.22 μm nylon syringe filter. pH of the resulting solution was 7.4. The analysis was performed at constant recommended conditions such as temperature 25°C (solvent: water) ratio 55:45 at the flow rate of 1 mL/min at 210 nm. The reference substances were chosen according to estimated Koc range of the test substance and generalize calibration graph was prepared. Selected reference substances and test chemical were prepared in acetonitrile with concentration of 400 mg/L. Both were analyzed on HPLC considering the similar conditions. After analyzing on above conditions calibration curve of selected reference substances was prepared to obtain log Koc value. The reference substances were p-Toluamide, Aniline, N-methylaniline, 4-Chloroaniline, phenanthrene, Naphthalene, DDT, having Koc value ranging from 1.8 to 2.9. The Log Koc value was test chemical was determined to be 2.787±0.001 at 25°C. Thus, based on the result it is concluded that the test chemical has a moderate sorption to soil and sediment and therefore have slow migration potential to ground water.
Key value for chemical safety assessment
- Koc at 20 °C:
- 612.35
Additional information
The adsorption coefficient Koc in soil and in sewage sludge of test chemical was determined by the Reverse Phase High Performance Liquid Chromatographic method according to OECD Guideline No. 121 for testing of Chemicals (Experimental study report, 2019). The solutions of the test substance and reference substances were prepared in appropriate solvents. The sample of test chemical was prepared by adding 10 mg in acetonitrile to prepare 1000 mg/L test solution, sonicated for 1 mins and filtered through 0.22 μm nylon syringe filter. pH of the resulting solution was 7.4. The analysis was performed at constant recommended conditions such as temperature 25°C (solvent: water) ratio 55:45 at the flow rate of 1 mL/min at 210 nm. The reference substances were chosen according to estimated Koc range of the test substance and generalize calibration graph was prepared. Selected reference substances and test chemical were prepared in acetonitrile with concentration of 400 mg/L. Both were analyzed on HPLC considering the similar conditions. After analyzing on above conditions calibration curve of selected reference substances was prepared to obtain log Koc value. The reference substances were p-Toluamide, Aniline, N-methylaniline, 4-Chloroaniline, phenanthrene, Naphthalene, DDT, having Koc value ranging from 1.8 to 2.9. The Log Koc value was test chemical was determined to be 2.787±0.001 at 25°C. Thus, based on the result it is concluded that the test chemical has a moderate sorption to soil and sediment and therefore have slow migration potential to ground water.
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