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EC number: 470-090-8 | 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
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: OECD Guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 003
- Report date:
- 2003
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
Reference
- Name:
- Unnamed
- Type:
- Constituent
- Details on test material:
- Chemical Name:3-[(2,2-Dimethyl-1 ,2-azasilolidin-1-yl)(dimethyl)silyl]-l-propanamin
Aggregate State: liquid
Colour:colourless-yellowish
Storage: refrigerator
Stability: instable in water (::=; 1.0 min.)
Safety Precautions: Routine hygienic procedures were sufficient to assure personnel health and safety
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- supplied by the sewage plant Groß-Simmern, Germany
The activated sludge used for this study was washed by centrifugation and the supematant liquid phase was decanted. The solid material was resuspended in tap water and again centrifuged. This procedure was repeated twice. An aliquot of the final sludge suspension was weighed, dried and the ratio of wet sludge to its dry weight was determined. Based on this ratio, calculated aliquots of washed sludge suspension, corresponding to 1.5 g dry material per litre were mixed with test water and then aerated until use. - Duration of test (contact time):
- 28
Parameter followed for biodegradation estimation
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- The amounts of test item and reference item were directly weighed into the test flasks. No emulsifiers or solvents were used, but the solutions were dispersed by stirring to achieve a homogeneous solution of the test item.
The closed test flasks were incubated in a climatic chamber under continuous stirring. The consumption of oxygen was determined by measuring the change of pressure in the flasks.
Evolved carbon dioxide was absorbed in an aqueous solution (45 %) of potassium hydroxide.
Temperature was measured each working day in the climatic chamber.
pH-values were measured in all flasks at the start and end of the test using a pH-electrode WTW pH 340i
Surrounding Type: climatic chamber
Temperature: 21 - 22°C
Light Conditions: darkness
pH-Value of Test Solutions: 7.6 (measured at the start of the test)
Manometric Test System with test flasks containing a volume of 500 mL
Reference substance
- Reference substance:
- aniline
Results and discussion
% Degradation
- Parameter:
- % degradation (O2 consumption)
- Value:
- 0
- St. dev.:
- 1
- Sampling time:
- 28 d
- Details on results:
- Inoculum Control: The oxygen demand of the inoculum control (medium and inoculum) was 25 and 30 mg 02/L and was thus not greater than 60 mg O2/L within 28 days.
pH-Value: The pH-value of the test item flasks at the end of the test was 7.8 and thus within the range of pH 6.0 - 8.5.
Reference Item: The percentage degradation of the reference item Aniline reached the level for ready biode-gradability (> 60 %, based on ThODNH4) within 4 days.
Test Item: The difference of duplicate values for the degradation of the test item at any time during the test was less than 20 %.
BOD5 / COD results
- Results with reference substance:
0 % degradation after 1 d
63 % degradation after 4 d
81 % degradation after 7 d
99 % degradation after 14 d
100 % degradation after 21 d
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- The test item can be considered to be not readily biodegradable.
- Executive summary:
The test item was investigated for its ready biodegradability in a Manometric Respirometry Test (OECD 301 F) over a period of 28 days. The biodegradation was followed by the oxygen uptake of the micro organisms during exposure. As a reference item Aniline was tested simultaneously under the same conditions as the test item, and functioned as a procedure control. After correction for the mean biochemical oxygen demand of the inoculum controls at the end of the 28-day exposure period degradation rates of -1%and 1%,based on ThODNH4and ThODN03,were found. The test item can therefore be considered to be not readily biodegradable. The reference item Aniline was sufficiently degraded to 99%after 14 days, and to 109 % after 28 days of incubation, based on ThODNH4,thus confirming the suitability of the used activated sludge inoculum. In the toxicity control containing both, the test item and the reference item Aniline, 41 % biodegradation was noted within 14 days and 44%biodegradation was determined after 28 days of incubation, based on ThODNH4 •Thus, the test item can be assumed to be not inhibitory on the activated sludge micro organisms.
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