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EC number: 210-913-8 | CAS number: 625-84-3
- 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:
- 2006
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: OECD Guideline Study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 006
- Report date:
- 2006
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- 2,5-dimethyl-1H-pyrrole
- EC Number:
- 210-913-8
- EC Name:
- 2,5-dimethyl-1H-pyrrole
- Cas Number:
- 625-84-3
- Molecular formula:
- C6H9N
- IUPAC Name:
- 2,5-dimethyl-1H-pyrrole
- Reference substance name:
- 2,5-Dimethylpyrrole
- IUPAC Name:
- 2,5-Dimethylpyrrole
- Test material form:
- other: yellowish liquid
- Details on test material:
- 2,5-Dimethylpyrrole was a yellowish liquid with a purity of 99.7%.
Constituent 1
Constituent 2
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- The source of test organisms was activated sludge
freshly obtained from a municipal sewage treatment
plant: 'Waterschap de Maaskant', 's-Hertogenbosch,
the Netherlands, receiving predominantly domestic
sewage. - Duration of test (contact time):
- ca. 28 d
- Details on study design:
- 28 days (last CO2-measurement on the 29th day).
During the test period the test media were aerated
and stirred continuously.
Reference substance
- Reference substance:
- acetic acid, sodium salt
Results and discussion
% Degradation
- Parameter:
- % degradation (CO2 evolution)
- Value:
- ca. 16 - ca. 17
- Sampling time:
- 28 d
- Details on results:
- 2,5-Dimethylpyrrole was found not to inhibit microbial activity.
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- not readily biodegradable
- Interpretation of results:
- other:
- Conclusions:
- The relative degradation values calculated from the measurements performed during the test
period revealed 16 and 17% degradation of 2,5-Dimethylpyrrole, for the duplicate bottles tested.
Thus, the criterion for ready biodegradability (at least 60% biodegradation within a 1a-day
window) was not met.
In conclusion, 2,5-Dimethylpyrrole was not readily biodegradable under the conditions of the
modified Sturm test presently performed. - Executive summary:
Determination of 'ready' biodegradability: carbon dioxide (C02) evolution test (modified Sturm
test) with 2,5-Dimethylpyrrole.
The study procedure was based on EEC directive 92/69, CA-C, December 1992, OECD
guideline No. 301 B July 17, 1992 and ISO Standard 9439 (1999).
2,5-Dimethylpyrrole was a yellowish liquid with a purity of 99.7%. 2,5-Dimethylpyrrole was
tested in duplicate at 32 mg per 2 litres, corresponding to 12 mg TOC/1. The organic carbon
content was based on the molecular formula. The Theoretical CO2 production (ThC02 ) of
2,5-Dimethylpyrrole was calculated to be 2.77 mg CO2/mg.
The study consisted of six bottles:
2 blank controls (no test material),
2 test bottles (2,5-Dimethylpyrrole, 16.1 mg/I),
1 positive control (sodium acetate, 40.0 mg/I) and
1 toxicity control (2,5-Dimethylpyrrole, 16.1 mg/I; plus sodium acetate, 40.0 mg/I).
Since 2,5-Dimethylpyrrole was easily soluble in water the test media were prepared using a
stock solution of 1 g/I in Milli-RO water. Preparation was as much as possible performed under
yellow light and/or dimmed light conditions. A weighed amount of 1007.5 mg of
2,5-Dimethylpyrrole was dissolved in Milli-RO water and made up tol 000 ml.17 Minutes of
magnetic stirring was used to accelerate dissolution and to ensure homogeneity. The resulting
stock was a clear and colourless solution. Aliquots of 32 ml of the stock solution were added to
the test medium, containing the microbial organisms, of test substance bottles A and B and the
toxicity control. The test solutions were continuously stirred during the test, to ensure optimal
contact between the test substance and the test organisms.
The relative degradation values calculated from the measurements performed during the test
period revealed 16 and 17% degradation of 2,5-Dimethylpyrrole, for the duplicate bottles tested.
Thus, the criterion for ready biodegradability (at least 60% biodegradation within a 10-day
window) was not met. In the toxicity control, 2,5-Dimethylpyrrole was found not to inhibit
microbial activity.
Since all criteria for acceptability of the test were met, this study was considered to be valid.
In conclusion, 2,5-Dimethylpyrrole was not readily biodegradable under the conditions of the
modified Sturm test presently performed.
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