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Diss Factsheets
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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
Link to relevant study record(s)
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2019
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-D (Determination of the "Ready" Biodegradability - Manometric Respirometry Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 835.3110 (Ready Biodegradability)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): local wastewater treatment plant, ARA Birs (Birsfelden / Switzerland)
- Preparation of inoculum for exposure: The aerobic activated sewage sludge was washed three times by centrifugation, decantation of the supernatant (liquid phase) and resuspension of the solid material in tap water and finally in mineral medium. Aliquots of the homogenised final sludge suspension were weighed and dried (using a halogen moisture analyzer HS153 from Mettler Toledo).
- Concentration of sludge: Final concentration of 30 mg dry material per liter - Duration of test (contact time):
- 28 d
- Initial conc.:
- ca. 100 mg/L
- Based on:
- COD
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: Mineral medium was prepared according to the testing guidelines
- Test temperature: 22.8 to 23.3 °C
- pH: Prior to the start of the test (Day 0), the pH was measured in each test vessel before the addition of the inoculum, and was found to be 7.4 for all vessels.
- pH adjusted: no
- Continuous darkness: no
TEST SYSTEM
- Number of culture flasks/concentration: 2
- Measuring equipment: For the measurement of the BOD, the OxiTop® Control system from WTW GmbH, Weilheim, Germany consisting of pressure measuring heads, test bottles, inductive stirring system and the OxiTop® OC 110 Controller was used.
SAMPLING
Not applicable: BOD values were automatically recorded every four hours
CONTROL AND BLANK SYSTEM
- Inoculum blank: Included
- Abiotic sterile control: Not included
- Toxicity control: Included - Reference substance:
- benzoic acid, sodium salt
- Preliminary study:
- Due to the complex structure of the test item, its Chemical Oxygen Demand (COD) was determined according to the EU Commission Directive 92/69/EEC, Part C.6 following DIN 38414-S9.
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 5
- Sampling time:
- 28 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- 4.5
- Sampling time:
- 21 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- 4.5
- Sampling time:
- 14 d
- Parameter:
- % degradation (O2 consumption)
- Value:
- 2
- Sampling time:
- 7 d
- Parameter:
- COD
- Value:
- 2.05 g O2/g test mat.
- Results with reference substance:
- The percent of biodegradation of sodium benzoate was calculated based on the ThOD of 1.67 mg O2/mg. In the procedure controls, the average biodegradation of the reference item sodium benzoate reached 61 % and 77 % by Day 4 and Day 14, respectively. At the end of the test (Day 28), the average biodegradation was 79 %.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- 4,4’-isopropylidenediphenol, reaction products with 1-chloro-2,3-epoxypropane, mono, di and triesters with acrylic acid is not ready biodegradable.
- Executive summary:
The ready biodegradability of 4,4’-isopropylidenediphenol, reaction products with 1-chloro-2,3-epoxypropane, mono, di and triesters with acrylic acid was evaluated during a GLP-compliant study perform in accordance with the OECD Testing Guideline 301F (Manometric Respirometry).
The test was performed in closed vessels containing a known concentration of test item in inoculated medium incubated at constant temperature for 28 days. The percent of biodegradation of the test item was calculated based on the Chemical Oxygen Demand (COD) of 2.05 mg O2/mg test item.
Sodium benzoate was used as reference substance.
The Biochemical Oxygen Demand (BOD) of 4,4’-isopropylidenediphenol, reaction products with 1-chloro-2,3-epoxypropane, mono, di and triesters with acrylic acid in the test media was minimal above the oxygen consumption in the inoculum controls during the whole incubation period. Therefore, the calculated mean biodegradation value of the test item at the end of the test period, on Day 28, was at only 5 % of the COD.
Oxygen consumption was evaluated through the study.
Validation criteria were met. A toxicity control indicated that the test substance had no inhibitory effect on the activity of activated sludge microorganisms at the tested concentration of 100 mg/L.
4,4’-isopropylidenediphenol, reaction products with 1-chloro-2,3-epoxypropane, mono, di and triesters with acrylic acid was found to be not readily biodegradable under the test conditions within 28 days.
Reference
Description of key information
The ready biodegradability of 4,4’-isopropylidenediphenol, reaction products with 1-chloro-2,3-epoxypropane, mono, di and triesters with acrylic acid was evaluated during a GLP-compliant study perform in accordance with the OECD Testing Guideline 301F (Manometric Respirometry).
The test was performed in closed vessels containing a known concentration of test item in inoculated medium incubated at constant temperature for 28 days. The percent of biodegradation of the test item was calculated based on the Chemical Oxygen Demand (COD) of 2.05 mg O2/mg test item.
Sodium benzoate was used as reference substance.
The Biochemical Oxygen Demand (BOD) of 4,4’-isopropylidenediphenol, reaction products with 1-chloro-2,3-epoxypropane, mono, di and triesters with acrylic acid in the test media was minimal above the oxygen consumption in the inoculum controls during the whole incubation period. Therefore, the calculated mean biodegradation value of the test item at the end of the test period, on Day 28, was at only 5 % of the COD.
Oxygen consumption was evaluated through the study.
Validation criteria were met. A toxicity control indicated that the test substance had no inhibitory effect on the activity of activated sludge microorganisms at the tested concentration of 100 mg/L.
4,4’-isopropylidenediphenol, reaction products with 1-chloro-2,3-epoxypropane, mono, di and triesters with acrylic acid was found to be not readily biodegradable under the test conditions within 28 days.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
- Type of water:
- freshwater
Additional information
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.