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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
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2 August 2012 - 26 September 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 012
- Report date:
- 2012
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: Method for Testing the Biodegradability of Chemical Substances by Microorganisms” stipulated in the “Testing Methods for New Chemical Substances”
- Version / remarks:
- 31 March 2011, including the latest revisions
- Deviations:
- no
- GLP compliance:
- yes
Test material
- Reference substance name:
- 1-Propanol, 2-methyl-, reaction products with 1,5-diisocyanatopentane
- Cas Number:
- 1357171-37-9
- Molecular formula:
- not applicable (a generic formula cannot be provided for this UVCB substance)
- IUPAC Name:
- 1-Propanol, 2-methyl-, reaction products with 1,5-diisocyanatopentane
- Test material form:
- liquid
- Details on test material:
- - Physical appearance: colorless and transparent liquid
- Storage conditions: the test sample was sealed with nitrogen and stored by cold and dark place with silica gel.
Constituent 1
- Specific details on test material used for the study:
- Stability: Reacts with water; reacts when heated; stability in light is not investigated.
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: sludge consisted of surface water containing the surface soil of rivers, lakes and inland sea, and returned sludge from a sewage-treatment plant. The sludge was collected from 10 different locations in Japan. Date of collection: May, 2012
- Preparation of sludge: activated sludge was prepared and managed at our facilities and used in the test. In the test, synthetic sewage (glucose, peptone and potassium dihydrogen phosphate were dissolved in purified water, and pH was adjusted to 7.0 ±1.0) was added to the solution, and thus activated sludge was obtained. After 18.5 hours, the activated sludge was used. Date of use: 18 June 2012.
- Concentration of sludge: 3250 mg/L - Duration of test (contact time):
- 28 d
Initial test substance concentrationopen allclose all
- Initial conc.:
- 100 mg/L
- Based on:
- test mat.
- Initial conc.:
- 43.5 mg/L
- Based on:
- ThOD
Parameter followed for biodegradation estimation
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: In accordance with Japanese Industrial Standerds (JIS)K 0102-2008 Section 14.1
- Test temperature: 25 ±1°C
- pH (at the end of the test): 6.7 in abiotic control and 7.3 in test solution
- pH adjusted: no
- Aeration of dilution water: no
- Suspended solids concentration: 30 mg/L
- Continuous darkness: yes
TEST SYSTEM
- Culturing apparatus: glass erlenmeyer flask
- Number of culture flasks/concentration: 3
- Method used to create aerobic conditions: not indicated
- Measuring equipment: closed-system oxygen consumption measuring apparatus:
* Temperature controlled batch: AI-0001 (Asahi Techneion Co.)
* Data sampler: OM7000A (Ohkura Electric Co.)
* Vessel: glass bottles
- Details of trap for CO2: soda lime No. 1 (Wako Pure Chemical Industries) was used to absorb CO2
- Other: test solutions were stirred continuously by a stirrer
SAMPLING
- Sampling frequency: BOD of the test solutions was continuously measured
- Sampling method: by use of closed-system oxygen consumption measuring apparatus
- Other: The incubation temperature and the conditions of the test solutions were measured and recorded once a day.
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes, one replicate
- Abiotic sterile control: yes, one replicate (water + test item)
- Toxicity control: no
- Other: one positive control containing sludge and the reference substance
STATISTICAL METHODS: no statistical analysis was performed
Reference substance
- Reference substance:
- aniline
- Remarks:
- ThOD: 72.3 mg/L
Results and discussion
% Degradation
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 0
- Sampling time:
- 28 d
- Remarks on result:
- other: mean of 3 replicates was -1%
- Details on results:
- - Biodegradation was calculated by BOD. The BOD in individual test flasks was 6.9, 6.8 and 7.6 mg after 28 days. Biodegradation in individual flasks was -2, -2 and 0%
- Visual inspections showed that the test solutions were colorless. An insoluble compound (not sludge) was observed. Growth of the sludge was not observed.
- HPLC analysis of the test item showed that 100% of the test item was decreased after 28 days. A qualitative analysis was carried out to identify insoluble converted products.
- It was presumed that the test item in both the abiotic control and the test solution (sludge + test item) went through the hydrolysis of the isocyanate group (N=C=O) to form urea bonds [-NH-C(=O)-NH-] among molecules and turned into three-dimensional polymer having a molecular weight of not less than 1000 that was insoluble in general solvents. It is presumed that the formed three-dimensional polymer remained without undergoing biodegradation.
BOD5 / COD results
- Results with reference substance:
- The reference substance was biodegraded for 94% after 14 days.
Any other information on results incl. tables
Table 1 Biodegradation calculated by BOD
Vessel |
Day 7 |
Day 14 |
Day 21 |
Day 28 |
Mean |
||||
BOD (mg) |
Deg. (%) |
BOD (mg) |
Deg (%) |
BOD (mg) |
Deg (%) |
BOD (mg) |
Deg. (%) |
DEG. (%) |
|
Sludge + aniline |
54.7 |
70 |
73.9 |
94 |
76.4 |
95 |
77.9 |
97 |
|
Control blank |
4.4 |
|
6.1 |
|
7.6 |
|
7.8 |
|
|
Sludge + test item |
4.8 |
1 |
6.2 |
0 |
6.8 |
-2 |
6.9 |
-2 |
-1 |
Sludge + test item |
4.5 |
0 |
6.0 |
0 |
6.8 |
-2 |
6.8 |
-2 |
|
Sludge + test item |
4.4 |
0 |
6.5 |
1 |
7.4 |
0 |
7.6 |
0 |
|
Water + test item |
0.0 |
|
0.0 |
|
0.5 |
|
0.6 |
|
|
Deg. = [BOD-B]/[TOD]*100%
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Remarks:
- see 'Overall remarks' section
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- D-370N did not biodegrade over a period of 28 days in the MITI test (mean biodegradation of -1%).
- Executive summary:
In a readily biodegradation study, performed as a MITI test according to JIS K 0102 -2008, D-370N was evaluated for its ability to biodegrade over a period of 28 days. The test item was tested in triplicate alongside an abiotic control, a blank control and a reference control (aniline). Biodegradation was determined by continuous measurement of the biological oxygen demand (BOD) of the test item using a closed-system oxygen consumption measuring apparatus. Soda lime was used to absorb carbon dioxide. After the end of the incubation, the test item in the test solutions was analyzed, and the converted products that were difficult to determine quantitatively were determined qualitatively by HPLC and LC-MS. Furthermore, although it was presumed that the test item would not be dissolved in the testing solutions, analysis was performed as to the dissolved organic carbon (DOC) in the test solutions to confirm whether or not there was a formation of water-soluble converted products. Results showed that the test item was biodegraded for -1% (mean of three replicates). The TOD was calculated to be 43.5 mg while the mean BOD was determined to be 6.8 mg. Analyis showed a mean DOC of 0.87. Since the test item did not dissolve in water at a test concentration (100 mg/L) or higher, the DOC percentage biodegradation was not calculated. HPLC analysis of the test item showed that 100% of the test item was decreased after 28 days. The insoluble converted products were determined to be three-dimensional polymers generated by urea bonds. It was presumed that the three-dimensional polymer remained without undergoing biodegradation. The reference item was biodegraded for 94% after 14 days, showing that the test system functioned properly. The acceptability criteria were met and the test was considered to be valid.
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