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EC number: 216-231-7 | CAS number: 1530-48-9
- 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
- Study period:
- Study plan dated : 15 May 2018 and experimental completion date 21 Jun 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-C (Determination of the "Ready" Biodegradability - Carbon Dioxide Evolution Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- Allyltributylphosphonium chloride
- EC Number:
- 216-231-7
- EC Name:
- Allyltributylphosphonium chloride
- Cas Number:
- 1530-48-9
- Molecular formula:
- C15H32P.Cl
- IUPAC Name:
- tributyl(prop-2-en-1-yl)phosphanium chloride
- Reference substance name:
- Tetrahydrothiophene 1,1-dioxide
- EC Number:
- 204-783-1
- EC Name:
- Tetrahydrothiophene 1,1-dioxide
- Cas Number:
- 126-33-0
- Molecular formula:
- C4H8O2S
- IUPAC Name:
- tetrahydrothiophene 1,1-dioxide
- Reference substance name:
- Tributyl-1-propen-1-yl-phosphonium chloride
- Molecular formula:
- C15H32P.Cl
- IUPAC Name:
- Tributyl-1-propen-1-yl-phosphonium chloride
- Test material form:
- other: solid : wax like
- Details on test material:
- Homogeneity : homogeneous if totally melted
Note: For every use the test item was completely melted and the melted test item
was used for the test.
Constituent 1
impurity 1
impurity 2
- Specific details on test material used for the study:
- Designation in Test Facility: 18032901G
Date of Receipt: 29. Mar. 2018
Condition at Receipt: Room temperature, in proper conditions
Batch no. INT 18 192
Appearance Beige crystallised mass
Homogeneity homogeneous if totally melted
Vapour pressure <0.1 hPa at 30 °C
Stability in solvents H2O: unknown; EtOH: unknown; acetone: unknown; CH3CN: unknown; DMSO: unknown
Solubility in solvents H2O: > 1 g/L; EtOH: unknown; acetone: unknown;
CH3CN: unknown; DMSO: unknown
Expiry date 17. Oct. 2019
Storage Room Temperature (20 ± 5°C)
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge (adaptation not specified)
- Details on inoculum:
- Activated sludge from a biologic sewage treatment plant was used as inoculum. The cho-sen plant treats mostly domestic sewage.
The sludge was taken from the activation basin of the sewage treatment plant, In den Seewiesen, 67480 Edenkoben
The sludge was filtrated through a cloth, washed with test medium (2x) and re-suspended in test medium. It was then aerated until use. The dry matter was determined to contain 4520 mg of suspended solids/L. - Duration of test (contact time):
- ca. 28 d
Initial test substance concentration
- Initial conc.:
- ca. 25 mg/L
- Based on:
- not specified
Parameter followed for biodegradation estimationopen allclose all
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Parameter followed for biodegradation estimation:
- DOC removal
- Details on study design:
- Apparatus
The test vessels were aerated with purified (by activated charcoal), CO2-scrubbed, mois-tened air. The scrubbing of carbon dioxide was achieved by bubbling the purified air through a flask containing 1.5 M NaOH. To control the absence of CO2, the air was then led through a flask containing a solution of Ba(OH)2 before reaching the test vessels.
Magnetic stirrers were used to prevent deposition of inoculum.
The emitted CO2 was trapped in 0.25 M NaOH. Two scrubbers containing 100 mL each were connected in series to the test vessels. The initial IC value of the 0.25 M NaOH was separately determined in each flask.
Sampling
From each front scrubber flask, 9 samples were taken in order to determine the emitted CO2 (on day 0, 2, 6, 8, 10, 14, 17, 23 and 29). The sample volume was 1 mL. The result-ing change in the volume of the front flask was considered in the calculation of emitted CO2 (see also chapter 8.3.1).
On day 28, 5 mL HCl 2 M was added to each test flask in order to drive off dissolved CO2. On day 29, samples from both scrubber flasks were taken.
CO2 Determination
Analyses of the emitted CO2 were made by IC measurement using the carbon analyser TOC multi N/C 2100S, Analytik Jena. Each sample was measured in duplicate or triplicate, respectively (depending on the variation between the measured values). The carbon ana-lyser was calibrated with freshly prepared reference solutions containing potassium hydro-gen phthalate (TC), sodium hydrogen carbonate and sodium carbonate (IC) every month. After every start, quality control samples were measured.
Reference substance
- Reference substance:
- aniline
- Remarks:
- Aniline was chosen as positive control.
Results and discussion
- Preliminary study:
- not performed
- Test performance:
- Preparations
The medium was prepared from the stock solutions. The stock solution of the positive con-trol was prepared and its DOC was measured. The stock solution of the test item was pre-pared and its DOC was measured. The inoculum was taken from its source, washed, aer-ated and the dry matter was determined.
The test vessels were filled with medium and inoculum. Then, all flasks were aerated for 96 hours with purified, CO2-free, moistened air to purge the system of CO2.
Sampling
From each front scrubber flask, 9 samples were taken in order to determine the emitted CO2 (on day 0, 2, 6, 8, 10, 14, 17, 23 and 29). The sample volume was 1 mL. The result-ing change in the volume of the front flask was considered in the calculation of emitted CO2 (see also chapter 8.3.1).
On day 28, 5 mL HCl 2 M was added to each test flask in order to drive off dissolved CO2. On day 29, samples from both scrubber flasks were taken
% Degradation
- Key result
- Parameter:
- % degradation (CO2 evolution)
- Value:
- ca. 1
- Sampling time:
- 28 d
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- The test item Allyltributylphosphonium chloride is considered as “not readily biode-gradable“.
The degree of biodegradation reached 1 % after 28 days.
The 10-day-window was not detected
Because the test item is a mixture, the 10-day window has not to be taken into ac-count. For the test item Allyltributylphosphonium chloride 1 % biodegradation was observed after 28 days. The 10-day window could not be determined. The criterion of reaching 60% of degradation after 28 days was not met. Allyltributylphosphonium chloride is therefore considered as “not readily biodegradable”.
The abiotic degradation reached 2.5 %. - Executive summary:
The test item Allyltributylphosphonium chloride was tested using a concentration of nomi-nally 20 mg organic carbon/L Allyltributylphosphonium chloride in test medium following OECD 301B and EU-Method C.4-C.
Aniline was chosen as positive control.
Activated sludge was used as inoculum (concentration in the test 25.0 mg dry matter/L). The test was left running for 28 days.
All validity criteria were met. Degradation of the positive control was 61 % after 10 days.
The following data were determined for the test item Allyltributylphosphonium chloride:
10-day-window: not detected degradation at the end of 10-day-window none degradation at the end of the test 1 % pass level following guideline: 60 % at the end of 10-day-window for pure substances
respective 60 % at the end of the test for mixtures
Therefore, when applying the 10-day-window, Allyltributylphosphonium chloride is not readily biodegradable following OECD 301B and EU C.4-C respectively.
Because the test item is a mixture the 10-day-window does not have to be taken into ac-count.
For the test item Allyltributylphosphonium chloride 1 % biodegradation was observed after 28 days. The 10-day window could not be determined. The criterion of reaching 60% of degradation after 28 days is not met. Allyltributylphosphonium chloride is therefore consid-ered as “not readily biodegradable”.
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