Registration Dossier
Registration Dossier
Diss Factsheets
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EC number: 807-113-1 | CAS number: 3709-71-5
- 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

Distribution modelling
Administrative data
- Endpoint:
- distribution modelling
- Type of information:
- calculation (if not (Q)SAR)
- Remarks:
- estimated by calculation
- Adequacy of study:
- key study
- Study period:
- 11 Feb - 14 Mar 2016
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Commonly-accepted level 3 fugacity model, use justified in scientific literature
Data source
Reference
- Reference Type:
- other company data
- Title:
- Unnamed
- Year:
- 2 016
- Report date:
- 2016
Materials and methods
- Model:
- calculation according to Mackay, Level III
- Calculation programme:
- NewEQC v.1.01, Centre for Environmental Modelling and Chemistry, Trent University, Peterborough, Ontario, Canada
- Release year:
- 2 012
- Media:
- air - biota - sediment(s) - soil - water
Test material
- Reference substance name:
- HFP kinetic dimer
- IUPAC Name:
- HFP kinetic dimer
- Details on test material:
- - Name of test material (as cited in study report): HFP kinetic dimer, FA-188
Constituent 1
Study design
- Test substance input data:
- - Molar mass: 264.086
- Data temperature: 22 °C
- Water solubility: 0.649 g/m³
- Vapour pressure: 3.47E+04 Pa
- log Pow: 4.1
- Mineral matter - water partition coefficient: N/A
- Melting point: -80 °C
- Reaction half-life estimates for
- Air: 4.92E+03 hours
- Water: 1.2E+07 hours
- Soil: 2.4E+07 hours
- Sediment: 2.4E+07 hours
The uses described in this dossier direct 100% of releases to the air during production, however during service life and disposal some proportion may be subject to burial. A total emission rate of 100 tonnes/year was modeled as entirely to the air compartment, with a second run directing emissions entirely to the soil compartment.
Results and discussion
Percent distribution in media
- Air (%):
- 99.996
- Water (%):
- 0
- Soil (%):
- 0.004
- Sediment (%):
- 0
- Susp. sediment (%):
- 0
- Biota (%):
- 0
- Aerosol (%):
- 0
- Other distribution results:
- Tabulated percentage distribution is for case 1, 100% release to air (Table 2a). Details of terrestrial distribution: 0.0038% in bulk soil, 0.0036% in gas-filled pore paces, 0.00020 on solids, and 9.5e-07% in pore water. Shortest intermedia transport half-time (Table 3): soil to air, 1.47 hours. Half-times from air to soil or to water are >26,000 times longer.
Case 2, 100% release to soil, results in 2.11% retention in soil, of which 2.00% is in air-filled pore spaces and 0.11% is sorbed to solids (Table 2b).
Any other information on results incl. tables
Table 2a, predicted distribution of HFP kinetic dimer, 100 tpy to air |
|||
Compartment |
Amount in compartment (kg) |
Concentration in compartment (g/L except as indicated) |
Percent of total in compartment |
Air: Bulk |
1126 |
1.13E-11 |
99.996 |
Gas Phase |
1126 |
1.13E-11 |
99.996 |
Aerosol |
3.89E-06 |
9.74E-07 µg/g |
3.46E-07 |
Water: Bulk |
2.89E-04 |
1.44E-15 |
2.57E-05 |
Liquid |
2.88E-04 |
1.44E-15 |
2.55E-05 |
Suspended Sediment |
1.12E-06 |
7.48E-10 µg/g |
9.96E-08 |
Fish (wet weight) |
2.00E-07 |
9.99E-10 µg/g |
1.77E-08 |
Soil: Bulk |
0.0428 |
2.38E-12 |
3.80E-03 |
Pore Air |
0.0405 |
1.13E-11 |
3.60E-03 |
Pore Water |
1.07E-05 |
1.97E-15 |
9.46E-07 |
Solids |
0.00222 |
1.03E-10 µg/g |
1.97E-04 |
Sediment: Bulk |
8.90E-05 |
1.78E-13 |
7.91E-06 |
Water |
1.40E-06 |
3.51E-15 |
1.25E-07 |
Solids |
8.76E-05 |
3.65E-15 µg/g |
7.78E-06 |
Table 2b, predicted distribution of HFP kinetic dimer, 100 tpy to soil |
|||
Compartment |
Amount in compartment (kg) |
Concentration in compartment (g/L except as indicated) |
Percent of total in compartment |
Air: Bulk |
1.13E+03 |
1.13E-11 |
97.9 |
Gas Phase |
1.13E+03 |
1.13E-11 |
97.9 |
Aerosol |
3.89E-06 |
9.74E-07 µg/g |
3.39E-07 |
Water: Bulk |
1.76E-03 |
8.81E-15 |
1.53E-04 |
Liquid |
1.75E-03 |
8.77E-15 |
1.53E-04 |
Suspended Sediment |
6.84E-06 |
4.56E-09 µg/g |
5.95E-07 |
Fish (wet weight) |
1.22E-06 |
6.10E-09 µg/g |
1.06E-07 |
Soil: Bulk |
24.2 |
1.35E-09 |
2.11 |
Pore Air |
23.0 |
6.38E-09 |
2.00 |
Pore Water |
6.04E-03 |
1.12E-12 |
5.25E-04 |
Solids |
1.26 |
5.82E-08 µg/g |
0.109 |
Sediment: Bulk |
5.43E-04 |
1.09E-12 |
4.72E-05 |
Water |
8.57E-06 |
2.14E-14 |
7.45E-07 |
Solids |
5.35E-04 |
2.23E-09 µg/g |
4.65E-05 |
Table 3, Intermedia transport half-times |
|
Transfer process |
Half-time (years, unless otherwise listed) |
Air to Water |
89,100 |
Air to Soil |
4.41 |
Water to Air |
11.6 days |
Water to Sediment |
3.24 |
Soil to Air |
1.47 hours |
Soil to Water |
372 |
Sediment to Water |
1.34 |
Transfer time ratio |
|
Air : Water |
2.80E+06 |
Air : Soil |
2.63E+04 |
Water : Sediment |
2.42 |
Applicant's summary and conclusion
- Conclusions:
- HFP kinetic dimer will distribute predominantly (97.9% - 99.996%) to the atmospheric compartment according to a Level III Mackay model
- Executive summary:
HFP kinetic dimer distribution in the environment was modeled using a Level III fugacity model within the New Equilibrium Criterion model (NewEQC) v.1.01 (Trent University, Peterborough, ON, Canada). Substance properties were entered as per data in this dossier. A total emission rate of 100 kg/year of HFP kinetic dimer was directed entirely (100%) to air based on uses described in this dossier. A second run directed releases entirely to the soil compartment to help characterize service life of buried articles containing HFP kinetic dimer, as well as disposal of such articles by landfill at end of life. The predominant fraction (97.9% - 99.996%) was modeled as remaining present in the gas phase of the air compartment. The calculated intermedia distribution half-time from the soil compartment to the air compartment was 1.47 hours.
Distribution modeling was done using a well-accepted model. It is considered reliable with restrictions.
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