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EC number: 206-581-9 | CAS number: 355-37-3
- 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
Phototransformation in air
Administrative data
- Endpoint:
- phototransformation in air
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Study period:
- N/A
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
Data source
Reference
- Reference Type:
- publication
- Title:
- Unnamed
- Year:
- 2 003
- Report date:
- 2003
Materials and methods
Test guideline
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline draft (Photochemical Oxidative Degradation in the Atmosphere)
- Principles of method if other than guideline:
- Methods were equivalent to those discussed in the OECD guideline draft, namely flash photolysis methods, covering absolute and relative rate.
- GLP compliance:
- no
Test material
- Reference substance name:
- Trideca-1,1,1,2,2,3,3,4,4,5,5,6,6-fluorohexane
- EC Number:
- 206-581-9
- EC Name:
- Trideca-1,1,1,2,2,3,3,4,4,5,5,6,6-fluorohexane
- Cas Number:
- 355-37-3
- Molecular formula:
- C6HF13
- IUPAC Name:
- 1,1,1,2,2,3,3,4,4,5,5,6,6-tridecafluorohexane
- Test material form:
- liquid
Constituent 1
Study design
- Estimation method (if used):
- Estimation was calculated using the formula:
Τ(CF3CF2CF2CF2CF2CHF2) = ((Κ CH3CCl3)/(K CF3CF2CF2CF2CF2CHF2)) x T(CH3CCl3)
where Τ(CF3CF2CF2CF2CF2CHF2) and T(CH3CCl3) represent the tropospheric lifetimes of CF3CF2CF2CF2CF2CHF2 and CH3CC13 through reaction with OH radicals,
and Κ CH3CCl3 and K CF3CF2CF2CF2CF2CHF2 represent the rate constants for the reactions of CH3CCh and CF3CF2CF2CF2CF2CHF2 with OH radicals at 272 K. - Light source:
- Xenon lamp
- Light spectrum: wavelength in nm:
- 308
- Details on light source:
- EG&G FX-1930, typically 800 V and 2 µF
- Details on test conditions:
- Absolute Rate Method
A Pyrex glass reactor with an inner diameter of 25 mm and a length of about 40 cm was used for the FP- LIF and LP-LIF experiments. For the FP-LIF method, OH radicals were produced by the pulsed photolysis of H2O by a Xe flash lamp (EG&G FX-1930, typically 800 V and 2 µF) in the presence of a large excess of argon bath gas. For the LP-LIF method, OH radicals were produced by the reaction O(^1 D) + H2O -+ 2OH in the presence of a large excess of helium or argon bath gas. O(^1 D) atoms were generated by photodissociation of N2O with an ArF excimer laser. For both LP and FP methods, initial concentration of OH radicals were always kept smaller than 10^11 molecule cm^-3 to prevent accumulation of photofragmentation products, reaction products, or both, all photolysis experiments were carried out under slow-flow conditions. The repetition rates of the FP lamp and excimer laser were set at 10 Hz.
The excitation light for the FP-LIF and LP-LIF methods was from a frequency-doubled tuneable dye laser (pumped by the second-harmonic of a Nd:YAG laser, 10 Hz), and the wavelength was tuned at about 308 nm. The fluorescence signal from the OH radicals was monitored at about 308 nm. A monochromator was used to limit the amount of scattered excitation light (and photolysis light) reaching the photomultiplier tube that was used to monitor the fluorescence signals. The signals were accumulated by a multichannel scaler/averager.
The flow rate of each gas was measured and controlled by calibrated mass flow controllers. The total gas pressure of the reactor was monitored by using a capacitance manometer and was kept constant by an electrically controlled exhaust throttle valve. The temperature of the reactor was maintained either by an electric heater or by circulating fluid through the outer jacket of the reactor from a thermostated bath. The temperature was measured with a CA (type K) thermo couple. During the experiments, the temperature across the reaction volume was maintained at better than ±2 K over the temperature range examined. To ensure that the experimental data were free from unexpected daily fluctuation of experimental conditions and experimental setup, the experiments were repeated at intervals from several days to several months under a variety of experimental conditions.
Relative Rate Method
Experiments were performed in a previously described 11.5-dm^3 quartz cylindrical chamber (10-cm i.d., 146 cm long) with an external jacket. The chamber temperature (253-328 K) was controlled by circulating heated water or a coolant (PF-5060; Sumitomo 3M Ltd.) through the external jacket. A/ constant-temperature bath (GT50L; Thermo Haake Co., Germany) was used to maintain the temperature of the circulating fluid. Ten low-pressure Hg lamps (GL- 40; National Co., Japan) surrounding the chamber were used as the light source.
The initial concentrations (in units of molecules cm^-3) were 5.0 x 10^14 (CF3CF2CF2CF2CF2CHF2), 5.0 x 10^14 (reference compound), and ~5.8 x 10^17 (H20) in 200 Torr of He. He was used because of its low 0(^1D) quenching efficiency. CHF2Cl (HCFC- 22) and CH2FCF3 (HFC-134a) were used as reference compounds. A greaseless vacuum line was used in preparing the reaction gas mixtures. An O3/O2 (3%) gas mixture, which was generated from pure O2 with a silent-discharge ozone generator (ECEA-1000; Ebarajitsugyo, Japan), was continuously introduced into the chamber at a flow rate of 10-50 cm^3 min^-1 during the UV irradiation. A steady-state high OH radical con centration of (0.53-1.2) x 10 15 molecule cm=' can be produced in the chamber by using this technique. The flow rate of the O3/O2 gas mixture was controlled by a mass flow controller. In all experiments, the initial pressure in the chamber was 200 Torr. The total pressure increased during irradiation and reached 300- 500 Torr by the end of the experiment.
- Reference substance:
- no
Results and discussion
Degradation rate constant
- Key result
- Reaction with:
- OH radicals
- Rate constant:
- 0 cm³ molecule-1 s-1
- Transformation products:
- no
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- Using both absolute and relative rate methods, we determined the rate constants for the reaction of CF3CF2CF2CF2CF2CHF2 with OH radicals over the temperature range 250-430 K: k, = (4.71 ± 0.94) x 10-13 exp[-(1630 ± 80)/T] cm^3 molecule-1 s-1. The FP-LIF and LP-LIF techniques were employed in the absolute method, and CHF2Cl and CH2FCF3 were used as reference compounds in the relative rate method. The rate constants determined by the two methods agreed with each other within the experimental uncertainties. This fact implies that the k data obtained in this study have a high reliability. The tropospheric lifetime of CF3CF2CF2CF2CF2CHF2 through reaction with OH radicals was estimated to be 31 years.
- Executive summary:
The rate constants k1for the reaction of CF3CF2CF2CF2CF2CHF2with OH radicals were determined by using both absolute and relative rate methods. The absolute rate constants were measured at 250 - 430 K using the flash photolysis-laser-induced fluorescence (FP-LIF) technique and the laser photolysis-laser-induced fluorescence (LP-LIF) technique to monitor the OH radical concentration. The relative rate constants were measured at 253 - 328 K in an 11.5-dm3reaction chamber with either CHF2CI or CH2FCF3as a reference compound. OH radicals were produced by UV photolysis of an O3-H2O-He mixture at an initial pressure of 200 Torr. Ozone was continuously introduced into the reaction chamber during the UV irradiation. The k1(298 K) values determined by the absolute method were (1.69± 0.07) x 10-15cm3molecule-1s-1(FP-LIF method) and (1.72 ± 0.07) x 10-15cm3molecule-1s-1(LP-LIF method). Whereas the k1(298 K) values determined by the relative method were (1.87 ± 0.11) x 10-15cm3molecule-1s-1(CHF2CI reference) and (2.12 ± 0.11) x 10-15cm3molecule-1s-1(CH2 FCF3 reference). These data are consistent with each other within the estimated experimental uncertainties. The Arrhenius rate constant determined from the kinetic data was k1= (4.71 ± 0.94) x 10-13 exp[-(1630± 80)/T] cm3molecule-1s-1. Using kinetic data for the reaction of tropospheric CH3CCl3with OH radicals [k1(272 K) = 6 0 x 10-15cm3molecule-1s-1, tropospheric lifetime of CH3CCl3= 6.0 years]. We estimated the tropospheric lifetime of CF3CF2CF2CF2CF2CHF2through reaction with OH radicals to be 31 years.
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