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EC number: 412-600-3 | CAS number: 152827-98-0
- 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:
- 19 January 2004 to 24 February 2004
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study without detailed documentation
- Remarks:
- A GLP compliant study performed to standardised guidelines with limited amount of detail on the materials and methods.
- 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:
- (see below)
- Principles of method if other than guideline:
- The test substance eluted after the standard with the highest literature Koc. Therefore the sample was not bracketed by standards with higher and lower Koc values as per protocol. The test substance log Koc was reported as a value greater than the standard having the highest log Koc value. As per protocol, the dead time was not measured because it was not necessary to calculate the capacity factor since the test substance eluted after the highest log Koc reference standard. These protocol deviations had no effect on the outcome of the study.
- GLP compliance:
- yes
- Type of method:
- HPLC estimation method
- Radiolabelling:
- no
- Test temperature:
- 26 ± 1 ºC
- Details on study design: HPLC method:
- INSTRUMENT CONDITIONS
The samples were analysed using HPLC/UV with the following instrument conditions:
Instrument: Waters Module I Plus liquid chromatograph
Detector: Waters Module I Plus (486 internal) at 254 nm
Column: ThermoHypersil-Keystone, CPS-2 Hypersil, 150 x 3 mm i.d., 5 µm particle size
Solvent A: 0.01 M citrate buffer in distilled, deionized water, pH adjusted to 3.00 with concentrated citric acid
Solvent B: methanol
Injection size: 20 µL
Flow: 0.5 mL/min
Elution conditions: isocratic at 75 % B for 5 minutes
The standard used in this study was: DDT (1,1-bis(4-chlorophenyl)-2,2,2-trichlorethane).
The standard and the test substance were dissolved in methanol at working concentrations of approximately 1500 mg/L and 1200 mg/L, respectively. - Key result
- Type:
- log Koc
- Value:
- > 5.63
- Temp.:
- 26 °C
- Details on results (HPLC method):
- HPLC results of standard and test substance:
- Test substance: Mean retention time: 3.156 minutes; concentration: 1200 mg/L; Literature log Koc: not applicable
- DDT: Mean retention time: 2.859 minutes; concentration: 1460 mg/L; Literature log Koc: 5.63 - Transformation products:
- not specified
- Validity criteria fulfilled:
- not applicable
- Remarks:
- Due to the nature of the test material, the validity criteria of the testing guideline cannot be applied.
- Conclusions:
- Under the conditions of the test, the Koc of the test substance was estimated to be greater than 5.63.
- Executive summary:
In a GLP adsorption-desorption study conducted in line with OECD Guideline 121, the Koc of butanoic acid, 4-[[4-[7-chloro-6 -(1,1-dimethylethyl)-3H-pyrazolo[1,5-b][1,2,4]triazol-2-yl]phenyl]amino]-4-oxo, tetradecyl ester was determined using HPLC. The Koc of the substance was estimated to be greater than 5.63.
Reference
One standard with a known log Koc value was prepared and analysed with the test substance. The test substance was not bracketed by standards with higher and lower log Koc values. The test substance eluted after the DDT standard which is the standard having the highest literature log Koc value. Therefore, the log Koc of the test substance was estimated to be > 5.63. Since the log Koc value of the test substance was reported as a greater than value, an unretained organic compound was not analysed for the dead time determination.
The test substance was estimated to have three pKa values; 1.1, 7.5 and 13.1. Therefore the test substance is considered ionizable. Due to pH limits of the analytical column (pH 2 to 8) it was not possible to analyse the test substance in its nonionized form since this would require using a buffered water mobile phase at a pH one unit below 1. The test substance was analysed in its ionized form using a buffered water mobile phase at a pH of 3.00.
Description of key information
Key study:- Isaacs (2004b) 'Estimation of the adsorption coefficient (Koc) on soil and on sewage sludge using high performance liquid chromatography' was conducted in line with OECD Guideline 121. The Koc of the test substance was estimated to be greater than 5.63.
Key value for chemical safety assessment
Additional information
The key study (Isaacs, 2004b) was performed in compliance with GLP and to OECD Guideline 121 with a sufficient level of detail to assess the quality of the presented data. The study was performed to a good standard in line with an accepted, standardised guideline and was assigned a reliability score of 2 using the principles for assessing data quality as set out in Klimisch et al. (1997). The Koc of the test substance was estimated to be greater than 5.63.
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