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Diss Factsheets
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EC number: 248-256-4 | CAS number: 27138-01-8
- 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)
Description of key information
The Reaction Mass of a,a,a’,a’-Tetramethyl-m-xylene-a,a’-diol and a, a, a’, a’ -Tetramethyl-p-xylene-a, a’-diol (m/p DIOL), was not readily biodegradable under the conditions of the test OECD 301B. A mean total of 2.0% degradation was achieved by Day 28.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
The ready biodegradability of the Reaction Mass of a,a,a’,a’-Tetramethyl-m-xylene-a,a’-diol and a,a,a’,a’ -Tetramethyl-p-xylene-a,a’-diol: (m/p DIOL) was assessed over a 28 day period by the CO2Evolution (Modified Sturm) Test. The study was conducted in accordance with procedures outlined in OECD Guideline 301B (1992).
The results of the test were as follows (28 day percent biodegradation values):
% Biodegradation |
m/p DIOL |
Sodium Benzoate |
Toxicity Control* |
|
A |
B |
|||
2.0 |
93.5 |
95.8 |
48.2 |
*The cumulative biodegradation determined in the Toxicity Control bioreactor is expressed in terms of the total organic carbon content resulting from the reference item only (A) and for the total organic carbon resulting from the reference and test item (B).
The test item (The Reaction Mass of a,a,a’,a’-Tetramethyl-m-xylene-a,a’-diol anda,a,a’,a’ -Tetramethyl-p-xylene-a,a’-diol: (m/p DIOL) was not readily biodegradable under the conditions of the test as it failed to achieve a transition from 10% to 60% degradation in a 10 day window during the 28 day test. The test item was not considered to be inhibitory to the microbial inoculum since the biodegradation observed in the toxicity control bioreactor was similar to that expected from the individual test and reference bioreactors.
The test failed to meet the validity criterion with respect to the differences in extremes of percent biodegradation in the test bioreactors. However, this was judged to be due to very low biodegradation values observed (1.8 and 2.2% for Test Bioreactors 1 and 2 respectively) and the possible influx of atmospheric CO2 into the final trap on Day 29. The test is therefore considered valid.
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