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Diss Factsheets
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EC number: 217-588-1 | CAS number: 1897-45-6
- 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
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Biodegradation in water: screening tests
Administrative data
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: screening test, other
- 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 301 C (Ready Biodegradability: Modified MITI Test (I))
- Deviations:
- not specified
- GLP compliance:
- not specified
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge (adaptation not specified)
- Details on inoculum:
- - Sludge sampling sites: 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)
- Sludge sampling time: March, June, September, and December in every year
- Sludge sampling method: For city sewage, returned sludge of sewage plants were collected. For Rivers, lake and sea, surface water and surface soil which is in contact with atmosphere were collected.
- Mixing of fresh and old activated sludge: 5 L of the filtrate of the supernatant of an activated sludge in the present use was mixed with 500 mL of the filtrate of the supernatant of a newly collected sludge respectively and the mixture was cultured at pH 7.0 ± 1.0 under the sufficient aeration (Prefiltered open air was used for aeration).
- Method of cultivation: About 30 minutes after ceasing the aeration to the sludge mixture , supernatant corresponding to about 1/3 of the whole volume was removed. Then the equal volume 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)%. The synthetic sewage was prepared by dissolving glucose, peptone and monopotassium phosphate in dechlorination water respectively. Each concentration of them was to be 5(W/V)% and the solution was adjusted to pH 7.0 ± 1.0 with sodium hydroxide. This cultivation method was repeated once every day. The culturing was carried out at 25 ± 2 °C.
- Control: During the cultivation, appearance of the supernatant, precipitability, formation of flock, pH, dissolved oxygen concentration in the solution and temperature were checked and necessary adjustments were made. Microflora in the activated sludge was microscopically observed and sludge with no abnormal symptom was used for the test.
- Inspection of activity: Activity of the sludge was inspected to use reference substance. And the relation between new and old activated sludge was taken account. - Duration of test (contact time):
- 2 wk
- Initial conc.:
- 100 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Remarks:
- Biochemical oxygen demand (BOD)
- Details on study design:
- TEST CONDITIONS
- Test temperature: 25 ± 1 °C
TEST SYSTEM
- Culturing apparatus: 300 mL closed system
- Number of culture flasks/concentration: 2
- Absorbent for CO2: Soda lime No.1
- Stirring method: Test solution was stirred by a magnetic stirrer.
ANALYSIS OF 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.
- Reference substance:
- aniline
- Key result
- Parameter:
- % degradation (O2 consumption)
- Remarks:
- BOD
- Value:
- 1.8
- Sampling time:
- 14 d
- Details on results:
- The percent biodegradation of the test item was calculated to be 1.8% based on the biochemical oxygen demand (BOD) at the end of the experment.
- Results with reference substance:
- The percent biodegradations of aniline calculated by BOD value were > 40% and > 60% at the 7th and 14th day, respectively.
- Validity criteria fulfilled:
- yes
- Remarks:
- 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 condition was valid.
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- The test substance was not readily biodegradable under the conditions of the test.
- Executive summary:
The ready biodegradability of the test item was investigated at a concentration of 100 mg/L using aerobic activated sludge incubated at 25 °C for 14 days under continuous stirring. The test was conducted equivalent or similar to OECD TG 301 C. It was not specified whether the study was compliant with GLP or not. The tested sludge was sampled from 10 different locations in Japan. The cultivated sludge that used in the test was exposed to 100 mg/L test substance or reference substance, aniline. In addition, a blank control was also involved in this test. After 2 weeks exposure, thepercent biodegradations of the reference substance were > 40% and > 60% at the 7th and 14th day, respectively. The percent biodegradation of the test item was calculate as 1.8% based on the biochemical oxygen demand (BOD) at the end of the experiment.Therefore, it was concluded that the test substance was not readily biodegradable under the conditions of the test.
Reference
Description of key information
The test substance was not readily biodegradable under the conditions of the test.
Key value for chemical safety assessment
- Biodegradation in water:
- not biodegradable
- Type of water:
- freshwater
Additional information
The ready biodegradability of the test item was investigated at a concentration of 100 mg/L using aerobic activated sludge incubated at 25 °C for 14 days under continuous stirring. The test was conducted equivalent or similar to OECD TG 301 C. It was not specified whether the study was compliant with GLP or not. The tested sludge was sampled from 10 different locations in Japan. The cultivated sludge that used in the test was exposed to 100 mg/L test substance or reference substance, aniline. In addition, a blank control was also involved in this test. After 2 weeks exposure, the percent biodegradations of the reference substance were > 40% and > 60% at the 7th and 14th day, respectively. The percent biodegradation of the test item was calculate as 1.8% based on the biochemical oxygen demand (BOD) at the end of the experiment. Therefore, it was concluded that the test substance was not readily biodegradable under the conditions of the test.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
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