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EC number: 276-911-4 | CAS number: 72829-25-5
- 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
Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: screening test, other
- Remarks:
- Inherent biodegradation Modified MITI test
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- April 24, 1996 to June 17 1996
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 302 C (Inherent Biodegradability: Modified MITI Test (II))
- Deviations:
- yes
- Remarks:
- The test substance was running in duplicate instead in triplicate. Inoculum control and reference control were running alone instead in duplicate. The title must be written: "1st Amendment to Study Plan" instead of "3rd Amendment to Study Plan"
- GLP compliance:
- yes
- Specific details on test material used for the study:
- Test medium:
3 ml of each following stock solutions were added per 1 litre distilled water to form the test medium:
Stock solution A:
8,50 g of potassium acid phosphate, 21,75 g of di-potassium hydrogen phosphate, 22,18 g of di-sodium hydrogenphosphate dihydrate and 1,70 g of ammonium chloride were dissolved in distilled water and adjusted to 1 litre. The pH value of this solution was 7,2.
Stock solution B: 22,50 g of magnesium sulfate heptahydrate were dissolved in distilled water and adjusted to 1 litre.
Stock solution C: 36,40 g of calcium chloride dihydrate were dissolved in distilled water and adjusted to 1 litre.
Stock solution D: 0,25 g of ferric chloride hexahydrate were dissolved in distilled water and adjusted to 1 litre. - Oxygen conditions:
- aerobic
- Inoculum or test system:
- other: Mixture of polyvalent bacteria collected on April 23, 1996 in the aeration tank of a domestic sewage treatment plant, PRO RHENO Basel communal.
- Details on inoculum:
- Mixture of polyvalent bacteria collected on April 23, 1996 in the aeration tank of a domestic sewage treatment plant, PRO RHENO Basel communal. Bacteria concentration: 100 mg/l suspended solids.
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 30 mg/L
- Based on:
- test mat.
- Details on study design:
- Performance of the test:
This test method was based on the following conditions:
- test chemicals as sole organic carbon sources
- no adaptation of micro-organisms to the test chemicals
Tested chemicals were inoculated in the testing vessels with micro-organisms. During the test period, the Biochemical Oxygen Demand was measured continuously by means of a BOD-meter. Biodegradability was calculated on the basis of the theoretical oxygen demand (ThOD) or less satisfactorily COD, if the ThOD could not be calculated. Optionally, primary biodegradation could be determined by analysis of dissolved organic carbon (DOC) at the beginning and the end of the test. - Reference substance:
- benzoic acid, sodium salt
- Remarks:
- Sodium benzoate
- Preliminary study:
- None
- Key result
- Parameter:
- other: Biodegradation measured as BOD versus ThOD
- Value:
- 12
- Sampling time:
- 28 d
- Remarks on result:
- other: Standard deviation is not available
- Details on results:
- Test substance:
The biodegradation of FAT 40034/D corrected by the inoculum control and measured as
BOD versus ThOD was: 12 % after 28 days
The BOD5 after 5 days was: 100 mg O2/g
Abiotic control:
The abiotic degradation at the end of the test and measured as BOD versus ThOD was: 0 % - Parameter:
- BOD5
- Value:
- 100 mg O2/g test mat.
- Results with reference substance:
- The biodegradation of the reference substance corrected by the inoculum control and measured as BOD versus ThOD was 84 % after 7 days; 94 % after 14 days and 100% after 28 days.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- not inherently biodegradable
- Conclusions:
- Biodegradation of FAT 40034/D after 28 days was 12 %.
- Executive summary:
An inherent biodegradability of FAT 40034/D was determined in a 28 days MITI (II) - Test according to the OECD Guideline for Testing of Chemicals, No. 302C. The test substance was tested in a concentration of 30 mg/l. The reference substance (Sodium benzoate) was tested in a concentration of 100 mg/l. Based on the results of the study, biodegradation of the test substance after 28 days was 12 % and the BOD5 after 5 days was : 100 mg 02/g.
Reference
The abiotic degradation at the end of the test and measured as BOD versus ThOD was 0 %.
Description of key information
An inherent biodegradability of FAT 40034/D was determined in a 28 days MITI (II) - Test according to the OECD Guideline for Testing of Chemicals, No. 302C. The test substance was tested in a concentration of 30 mg/l. The reference substance (Sodium benzoate) was tested in a concentration of 100 mg/l. Based on the results of the study, biodegradation of the test substance after 28 days was 12 % and the BOD5after 5 days was : 100 mg O2/g. Supporting studies were also performed to determine the chemical oxygen demand of FAT 40032/D which was found to be 798mg O2/g test material whereas the biological oxygen demand was found to be '0'mg O2/g test material.The relevant BOD5/COD quotient is <0.5 , therefore, the substance is not indicative of rapid degradation. Taking the data from key study and supporting studies into account, the test substance FAT 40034 is considered to be not biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- not biodegradable
- Type of water:
- freshwater
Additional information
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