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Diss Factsheets
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EC number: 205-016-3 | CAS number: 131-17-9
- 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: inherent biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study without detailed documentation
- Qualifier:
- equivalent or similar to guideline
- Guideline:
- OECD Guideline 302 C (Inherent Biodegradability: Modified MITI Test (II))
- Deviations:
- not specified
- GLP compliance:
- not specified
- Oxygen conditions:
- not specified
- Inoculum or test system:
- activated sludge, adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: Sludge sampling were made at the following 10 places in Japan: Fukogawa city sewage plant (Sapporo-shi Hokkaido);
Fukashiba industry sewage plant (Kashima-gun Ibaragi);
Nakahama city sewage plant (Osaka-shi Osaka);
Ochiai city sewage plant (Shinjuku-ku Tokyo);
Kitakami river (Ishinomaki-shi Miyagi);
Shinano river (Nishikanbara-gun Niigata);
Yoshino river (Tokushima-shi Tokushima);
Lake Biwa (Otsu-shi Shiga);
Hiroshima bay (Hiroshima-shi Hiroshima);
Dookai bay (Kitakyushu-shi Fukuoka).
- Method of cultivation: About 30 min after ceasing the aeration to the sludge miture, supernatant corresponding to about 1/3 of the whole volume was removed. Then the equal volule of dechlorination water was added to the remaining portion and aerated again, followed by addition of synthetic sewage*, concentration of that portion was to be 0.1 (W/V)%. This procedure was repeated once every day. The culturing was carried out at 25+/-2°C.
*: Glucose, peptone and monopotassium phosphate were dissolved in dechlorination water respectively. Each concentation of them was to be 5(W/V)% and the solution was adjusted to pH 7.0 +/-1.0 with sodium hydroxide.
- Concentration of sludge: 30 mg/L - Duration of test (contact time):
- 4 wk
- Initial conc.:
- 100 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Remarks:
- BOD
- Parameter followed for biodegradation estimation:
- test mat. analysis
- Remarks:
- GC
- Details on study design:
- TEST CONDITIONS
- Concentration of test substance : 100mg/L
- Suspended solids concentration: 30 mg/L
- Volume of test solution 300mL
- Cultivation temperature : 25°C
- Cultivation duration : 28 days
PREPARATION OF BASAL CULTURE MEDIUM
- Each 3 mLof solution A, B, C and D, which are prescribed in JIS K 012-1986-21, were made up to 1000 mL with purified water, and then pH of this solution was adjusted to 7.0
SAMPLING
- Sampling frequency: March, June, September, and December in every year.
- Sampling method: Returned sluge of sewage plants were collected.
STATISTICAL METHODS
- Percentage biodegradation (%) = 100 x [BOD - B ] / TOD
- BOD: Biochemical Oxygen Demand in
- B: Biochemical Oxygen Demand in control blank
- TOD: Theorical Oxygen Demand required when the test substance was completely oxidized - Reference substance:
- aniline
- Remarks:
- (guaranteed reagent, Showa Chemicals Inc.)
- Test performance:
- ANALYSIS OF THE TEST SOLUTION
After the termination of cultivation, total organic carbon and the test substance in the test solutions were determined. The pH of the test solutions of [water + test substance] and [sludge + test substance] were measured. - Key result
- Parameter:
- % degradation (O2 consumption)
- Remarks:
- BOD
- Value:
- 82
- Sampling time:
- 4 wk
- Key result
- Parameter:
- % degradation (test mat. analysis)
- Remarks:
- GC
- Value:
- 96
- Sampling time:
- 4 wk
- Details on results:
- BOD : 92, 79 and 76% biodegradation.
GC : 100, 88 and 100% biodegradation - Validity criteria fulfilled:
- yes
- Interpretation of results:
- inherently biodegradable, not fulfilling specific criteria
- Conclusions:
- Biodegradation was found above 70% of theoretical (measured as BOD, GC) so it can be regarded as evidence of inherent, ultimate biodegradability.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- results derived from a valid (Q)SAR model and falling into its applicability domain, with adequate and reliable documentation / justification
- Principles of method if other than guideline:
- 28d BOD test (MITI-test).
- GLP compliance:
- not specified
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- other: Microorganisms
- Duration of test (contact time):
- 28 d
- Details on study design:
- No details.
- Preliminary study:
- .
- Parameter:
- % degradation (O2 consumption)
- Value:
- 84
- Remarks on result:
- other: No further details available.
- Validity criteria fulfilled:
- not specified
- Interpretation of results:
- readily biodegradable, but failing 10-day window
Referenceopen allclose all
Validity of test conditions
When percentage biodegradations of aniline calculated by BOD value were beyond 40% and 60% at the 7th and 14th day, respectively, it was concluded that the test condtion was valid.
Description of key information
Data based on 2 references (reliable with restrictions), which are both used for environmental risk assessment of chemicals by the Japanese government.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable but failing 10-day window
- Type of water:
- freshwater
Additional information
According to the OECD guideline for biodegradation above 70% of theoretical (measured as BOD, DOC removal or COD) should be regarded as evidence of inherent, ultimate biodegradability. Since the 10-day window criterion was not fulfilled, diallyl phthalate could not be considered as readily biodegradable. Within the REACH regulation, such substances are considered as readily biodegradable but failing the 10-day window.
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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