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Diss Factsheets
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EC number: - | CAS number: -
- 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: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 D (Ready Biodegradability: Closed Bottle Test)
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, adapted
- Details on inoculum:
- The inoculum was prepared from a secondary effluent obtained from Peppers Ferry Wastewater Treatment Plant (Blacksburg, Virginia). Effluent was preconditioned
for 7 days prior to use, by aerating at 20 °C. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 5 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- Test Bottle Preparation
1. Mineral medium was aerated for 20 minutes and allowed to stand for 20
hours prior to use. Dissolved oxygen was measured after this period.
2. Mineral medium was added to a large flask to approximately one third full
(the inoculum blank, or IB). Then, appropriate amounts of test substance
and reference substance were added to separate large flasks to make 5g
test substance per liter of mineral medium in the final solution (the test
solution, or TS), and 2g reference substance per liter of mineral medium in
the final solution (the procedure control, or PC).
3. Appropriate amounts of test substance and reference substance were added
to a fourth large flask to make up a treatment with a final solution
concentration of 5g test substance and 2g reference substance per liter of
mineral medium (the toxicity control, or TC).
4. Finally, inoculum was added to all flasks.
5. There were 10 bottles prepared with the inoculum blank, 10 bottles with
the test solution, 10 with the procedure control, and 6 bottles with the
toxicity control.
6. The concentration of the dissolved oxygen did not fall below 0.5 mg/l
throughout the test.
Biodegradability Test Procedure
All testing and reporting was conducted as per OECD 301D.
1. The contents of the large bottles were well mixed and any excess bubbles
were removed by gently tapping when finished stirring. The prepared
solutions were immediately transferred to their respective group of BOD
bottles by hose from the lower quarter (not the bottom) of the large flasks
until all the BOD bottles were completely filled.
The zero-time bottles were analyzed right away for dissolved oxygen. The
remaining bottles were stoppered, taking care to avoid trapping any air
bubbles inside, and those bottles stored at 20 degrees Celsius in an
incubator in the dark.
3. Each series of testing bottles was accompanied by a parallel series of
bottles with inoculated blank medium. These were withdrawn for analysis
at the same time intervals as the other bottles being tested. They were
checked weekly over the 28-day time period of the test. - Reference substance:
- acetic acid, sodium salt
- Parameter:
- % degradation (DOC removal)
- Value:
- -3
- Sampling time:
- 7 d
- Parameter:
- % degradation (DOC removal)
- Value:
- -2.8
- Sampling time:
- 14 d
- Parameter:
- % degradation (DOC removal)
- Value:
- -2.5
- Sampling time:
- 21 d
- Parameter:
- % degradation (DOC removal)
- Value:
- -1.9
- Sampling time:
- 28 d
- Details on results:
- Validity of the Test
Oxygen depletion in the inoculum blank reached 1.07 mg dissolved oxygen/l at the end of 28 days. This did not exceed the method-specified limit of 1.5 mg dissolved oxygen/l.
The residual concentration of oxygen in the test bottles did not fall below 0.5 mg/l at any time. The difference of extremes of replicate values of the removal of the test chemical at the plateau was 2.01%. This difference did not exceed the method-specified limit of 20%. The removal of the reference compound on day 7 reached 64.09%, exceeding the method-specified minimum removal value of 60% of ThOD. - Results with reference substance:
- The removal of the reference compound on day 7 reached 64.09%, exceeding the method-specified minimum removal value of 60% of ThOD.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- Results of biodegradability closed bottle test following the OECD 301D guidelines determined taht benzylated polyamine is not readily biodegrade over the course of the 28-day test, nor it is inhibitory to biodegradation of a reference compound.
- Executive summary:
Results of biodegradability closed bottle test following the OECD 301D guidelines determined taht benzylated polyamine is not readily biodegrade over the course of the 28-day test, nor it is inhibitory to biodegradation of a reference compound.
Reference
Description of key information
Results of a biodegradability closed bottle test following the OECD 301D guidelines determined that benzylated polyamine is not readily biodegrade over the course of the 28-day test, nor it is inhibitory to biodegradation of a reference compound.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
- Type of water:
- freshwater
Additional information
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
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