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Diss Factsheets
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EC number: 433-470-4 | 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
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:
- March 2004
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: According to OECD test methd and to GLP standards
- 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:
- yes
- Remarks:
- For calculation of pKa values from the structural formula, different hardware and a previous version of the software were used. Results and therefore study integrity were not affected by this deviation.
- Principles of method if other than guideline:
- For calculation of pKa values from the structural formula, different hardware and a previous version of the software were used. Results and therefore study integrity were not affected by this deviation.
- GLP compliance:
- yes
- Type of method:
- HPLC estimation method
- Media:
- soil/sewage sludge
- Radiolabelling:
- no
- Test temperature:
- A temperature controlled column compartment at 35°C was used.
- Details on study design: HPLC method:
- A High Performance Liquid Chromatograph with a spectrophotometric detector was used. The stationary phase was a cyanopropyl chemically bound resin on silica basis (Hypersil BDS-CN). The mobile phase was 55/45 (v/v) methanol/water. A temperature controlled column compartment at 35°C was used.
Reagents
Methanol HPLC-grade, Labscan, Dublin, Ireland
Acetonitrile HPLC-grade, Labscan, Dublin, Ireland
Milli-Q water Tap water purified by reversed osmosis and subsequently passed over activated carbon and ionexchange cartridges; Millipore, Bedford, MA, USA
Formamide >/=99.5%, Acros Organics, Geel, Belgium
Refrence substances (with log Koc Values)
Phenol (99%, Acros organics, Geel, Belgium) 1.32
N,N-dimethylbenzamide (98%, Acros organics, Geel, Belgium) 1.52
Methylbenzoate (99%, Acros organics, Geel, Belgium) 1.80
3,5-Dinitrobenzamide (97%, .Acros organics, Geel, Belgium) 2.31
Naphtalene (99%, Acros organics, Geel, Belgium) 2.75
Mercaptodimethur (98.5%, Dr. Ehrenstorfer, Augsburg, 3.10
Germany)
Fenthion (96%, Riedel-de Ha1en, Seelze, Germany) 3.31
Phenantrene (>98%, Acros organics, Geel, Belgium) 4.09
2,4-DDT (97%, Dr. Ehrensto1fer, Augsburg, Germany) 5.63
Analytical conditions
Column Hypersil BDS-CN; 150 x 4.6 (l.D.) mm; dμ= 5 μm (Alltech, Deerfield, IL, USA)
Column temperature 35 °C
Mobile phase 55/45 (v/v) methanol/Milli-Q water
Flow 1 ml/min
Detection UV at J..= 210 nm
Injection volume 10 μI
Preparation of the solutions
Solutions of the reference substances in methanol, at concentrations between 0.99 and 6.4 g/I, were used. From these solutions, two mixtures of reference substances were prepared. One mixture contained 5 reference substances and was prepared by adding 50 μI of each reference substance solution to a volumetric 5 ml flask. The other mixture contained 4 reference substances and was prepared by adding 50 μI of each reference substance solution and 50 μI methanol to a volumetric 5 ml ·flask. Subsequently, the flasks were filled up to the mark with mobile phase. As reference blank solutions, 95/5 (v/v) mobile phase/methanol was used.
A 5.4 g/I solution of formamide~ in methanol was diluted by a factor 10 with mobile phase. This solution was used for the determination of to (retention time of the unretarded component). As blank formamide solution, 90/10 (v/v) mobile phase/methanol was used.
A 1.1 g/I stock solution of Seta1fix X 11342 was prepared in acetonitrile. In order to dissolve the test substance completely, this solution was ultrasonicated for 5 minutes. The test solution was prepared by diluting the stock solution by a factor 100 with mobile phase. As blank solution 99/1 (v/v) mobile phase/acetronitrile was used.
Injections
The solutions were injected in the following sequence: mobile phase, the mixtures 1 and 2 of reference substances, the reforence blank solution, the formamide solution, the formamide blank solution, the test solution (in duplicate), the corresponding blank solution, the mixtures 1 and 2 of reference substances and the formamide solution. The chromatograms were recorded for 10 minutes, except for the 'formamide solution and the formamide blank solution which were recorded for 5 minutes. - Type:
- Koc
- Value:
- 50 000 dimensionless
- Temp.:
- 35 °C
- Details on results (HPLC method):
- Calculation of pKa values
According to pKa calculations using a computer calculation program, the test substance does not contain ionizable groups. Therefore, the mobile phase was not buffered during the performance of the test.
Determination of Koc
In the HPLC chromatograms of Setafix X 11342, using detection at 210 nm, one large and seven small test substance peaks were observed. It was assumed that the large peak derives from the major component of test substance whereas the small peaks derive from impurities.
The ‘t0’ was determined to be 1.925 minutes as a mean value of both measurements (i.e. 1.923 and 1.926 minutes).
The mean values of the retention times, k’ values, log k’ values, log Koc and Koc values are summarized below.
tr k' log k' log Koc
Reference substance
Phenol 2.281 0.185 -0.732 1.32
N,N-dimethylbenzamide 2.135 0.109 -0.961 1.52
Methylbenzoate 2.442 0.269 -0.570 1.80
3,5-Dinitrobenzamide 2.615 0.359 -0.445 2.31
Naphtalene 3.111 0.617 -0.210 2.75
Mercaptodimethur 2.928 0.521 -0.283 3.10
Fenthion 4.449 1.312 0.118 3.31
Phenantrene 4.358 1.264 0.102 4.09
2,4-DDT 7.134 2.707 0.432 5.63
tr k' log k' log Koc Koc Area%
Test substance
Peak 1 1.317 -0.316 - <1.32 <21 0.5
Peak 2 2.778 0.443 -0.353 2.64 440 1.2
Peak 3 3.230 0.678 -0.169 3.24 1800 0.5
Peak4 3.387 0.760 -0.119 3.40 2500 0.8
Peak 5 3.757 0.952 -0.021 3.72 5300 0.2
Peak 6 4.664 1.423 0.153 4.29 20000 0.3
Peak 7 (major) 5.586 1.903 0.279 4.70 50000 95.1
Peak 8 6.816 2.542 0.405 5.11 130000 1.4 - Conclusions:
- The adsorption coefficient (Koc:) of Setafix X 11342 was determined to be 50000 (log Koc= 4. 70) at 35°C.
- Executive summary:
The adsorption coefficient (Koc:) of Setafix X 11342 was determined to be 50000 (log Koc= 4. 70) at 35°C.
Reference
For seven impurities, the adsorption coefficient (Koc) was determined to be:
<21 (log Koc <1.32), 440 (log Koc= 2.64), 1800 (log Koc= 3.24 ), 2500 (log Koc= 3.40),
5300 (log Koc= 3.72), 20000 (log Koc= 4.29) and 130000 (log Koc= 5.11) at 35°C.
Description of key information
The adsorption coefficient (Koc:) of Setafix X 11342 was determined to be 50000 (log Koc= 4. 70) at 35°C.
Key value for chemical safety assessment
Additional information
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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