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EC number: 639-791-8 | CAS number: 3345-29-7
- 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
Biodegradation in water: screening tests
Administrative data
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Report date:
- 2022
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- GLP compliance:
- yes
Test material
- Reference substance name:
- 2,2,3,3,8,8,9,9-octafluorotricyclo[8.2.2.2⁴,⁷]hexadeca-1(12),4,6,10,13,15-hexaene
- EC Number:
- 639-791-8
- Cas Number:
- 3345-29-7
- Molecular formula:
- C16H8F8
- IUPAC Name:
- 2,2,3,3,8,8,9,9-octafluorotricyclo[8.2.2.2⁴,⁷]hexadeca-1(12),4,6,10,13,15-hexaene
1
- Specific details on test material used for the study:
- Batch n. 340421
Production date November 19, 2021
Expiry date November 19, 2024
Purity ≥98.00%
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic (adaptation not specified)
- Remarks:
- The study was performed using aerobic activated sludge from BRIANZACQUE civil wastewater treatment plant.
- Details on inoculum:
- A homogenized aliquot of the wet sludge was centrifuged, the supernatant was removed while the solid phase was weighed, dried and the ratio of wet to dry weight was calculated to be equal to 7.4%.
Based on this ratio, calculated amounts of wet sludge was centrifuged, the supernatant was removed and the solid phase was suspended in the test medium to get a concentration equivalent to 3 g dry material per litre.
The prepared sludge inoculum was pre-conditioned to the experimental conditions by aerating it in the dark. The concentrated suspension was used as inoculum to give a final concentration of 15 mg dry material per litre into test flasks. - Duration of test (contact time):
- 28 d
Initial test substance concentrationopen allclose all
- Initial conc.:
- 100 mg/L
- Initial conc.:
- 81.8 mg/L
- Based on:
- ThOD
- Details on study design:
- The assay on test item was carried out in parallel with the following bottles:
- a known ready biodegradable reference item (one replicate), Sodium Benzoate, at 100 mg/L;
- two inoculum control replicates (blank);
- two test item replicates at 50.0 mg/L concentration.
- one abiotic control containing the test item at 50.0 mg/L and a sterilizing agent (HgCl2) at 100
mg/L (without inoculum);
- one toxicity control, containing the test item at 50.0 mg/L and reference item at 100 mg/L.
BOD flasks of 500 mL capacity, equipped with pressure sensors fitted on the bottle mouth, were used as test units.
The method is based on an electro-chemical analyses process. The iodegradation process consumes the dissolved oxygen in liquid and generates CO2. Evolved carbon dioxide is adsorbed by potassium hydroxide and the total pressure decreases in the test flasks.
The pressure decrease is detected and converted into an electrical signal by means of an electrode type manometer.
Test item concentration should be 100 mg/L or a concentration giving at least 50-100 ThOD /L.
The tested concentration was 50.0 mg/L (corresponding to 81.8 mg ThOD/L).
All reported results are related to the nominal concentration of test item, since the test concentrations were not measured during the test.
Reference substance
- Reference substance:
- benzoic acid, sodium salt
Results and discussion
% Degradationopen allclose all
- Parameter:
- % degradation (O2 consumption)
- Value:
- 18.9
- Sampling time:
- 10 d
- Remarks on result:
- other: mean percentage values between two test item replicates
- Parameter:
- % degradation (O2 consumption)
- Value:
- 16.5
- Sampling time:
- 28 d
- Remarks on result:
- other: mean percentage values between two test item replicates (22%), after nitrification correction.
BOD5 / COD results
- Results with reference substance:
- The reference item exceeded (85.6%) the biodegradation pass level (60%) within the range fixed by
OECD Guideline 301F (first 14 days).
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- At the end of the 10-day window the biodegradation was 18.9% (mean percentage values between two replicates).
Therefore, the test item, was found to be not ready and completely biodegradable under the
conditions applied in a manometric respirometry test.
At the end of the test (28 day) and after nitrification correction, a maximum biodegradation of 16.5% was found, (mean percentage values between two replicates). - Executive summary:
A study to evaluate the ready biodegradability of the test item PARYLENE HT®:, following the “Manometric Respirometry” method, was performed.
Test item concentration should be 100 mg/L or a concentration giving at least 50-100 ThOD /L.
The tested concentration was 50.0 mg/L (corresponding to 81.8 mg ThOD/L).
All reported results are related to the nominal concentration of test item, since the test concentrations
were not measured during the test.The biodegradation was followed by measuring the oxygen uptake (mg/L) of the test item under
defined conditions by the means of a manometric method and calculating from these values the BOD
(Biochemical Oxygen Demand).The ThODNH3 value (Theoretical Oxygen Demand without nitrification process) was calculated to be
equal to 1.67 mg O2/mg for reference item, Sodium Benzoate, while ThODNH3 value was assessed to
be 1.64 mg O2/mg for the test item.These values, 1.67 mg O2/mg for reference item and 1.64 mg O2/mg for the test item, were used to calculate per % biodegradation.
Nitrate and nitrite concentration were measured at the start and at the test end.
At the start and test end no nitrite and nitrate were present.At the test end nitrate concentration in the blank bottles (4.00 mg/L as mean value) was subtracted from the nitrate concentration found in test item bottles (8.35 mg/L as mean value), therefore the found value (4.35 mg/L), calculated as Total oxygen equivalent, was subtracted from the test biodegradation value at the end of the test.
At the end of the 10-day window the biodegradation was 18.9% (mean percentage values between two replicates).
Therefore, the test item, was found to be not ready and completely biodegradable under the conditions applied in a manometric respirometry test.
At the end of the test (28 day) and after nitrification correction, a maximum biodegradation of 16.5%
was found, (mean percentage values between two replicates).No significant degradation was observed in the abiotic control (equal to 7.3% at the test end).
The toxicity control clearly showed that the test item does not cause inhibitory effect on the microorganisms activity at the tested concentration. The toxicity control exceeded the 25 % pass level within the 14 days of exposure (42.1%).The reference item exceeded (85.6%) the biodegradation pass level (60%) within the range fixed by OECD Guideline 301F (first 14 days).
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