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Diss Factsheets
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EC number: 271-928-3 | CAS number: 68630-95-5
- 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:
- 28 days
- 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)
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Test substance name: Crodateric CYAP
Scymaris reference number: 1014TS047
Supplier: Croda Europe Ltd.
Lot/batch number: PS-196-555
Purity/strength: 98.15% w/w solids - Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic (adaptation not specified)
- Details on inoculum:
- Activated sludge was obtained from Totnes Sewage Treatment Works, Totnes, Devon, UK on 07 September 2017. This works treats sewage of predominantly domestic origin. At the laboratory, the activated sludge was kept aerated at room temperature and the pH maintained at 7.0 1.0.
- Duration of test (contact time):
- 28 d
- Initial conc.:
- 100 mg/L
- Based on:
- test mat.
- Remarks:
- Test material is 98.15% active ingredient
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- All test bottles contained the prepared activated sludge inoculum in mineral medium, as described in Section 3.4. Following the pre-conditioning the test bottles were set up for the test according to the experimental design shown in Table 1. Inoculum blanks contained no test or reference substance, in order to demonstrate there was no other carbon source in the medium. Positive controls contained the reference substance, sodium benzoate at 100 mg/L, to demonstrate the viability of the inoculum. The test substance bottles contained Crodateric CYAP at 100 mg/L, to determine the biodegradation of the test substance. Toxicity controls contained the test and reference substances, both at 100 mg/L, and were used to show if there had been any inhibition of the inoculum by the test substance. Each set of bottles was prepared in triplicate. Additional single replicate Crodateric CYAP and toxicity control bottles were prepared for determination of pH at day 0, so undissolved test substance was not removed by the pH probe.
Due to the aqueous solubility being unknown, the bottles containing Crodateric CYAP were prepared by directly weighing the required quantity to the relevant test bottles. Sodium benzoate was dosed as a 1000 mg/L stock solution, prepared by dissolving sodium benzoate in RO water to give a clear and colourless solution, this was prepared on the day of exposure start.
Oxygen uptake was recorded automatically every 240 minutes during the 28-day experimental period. Oxygen uptake values were corrected for the inoculum blank and the biodegradation was calculated as a percentage of the chemical oxygen demand for the substance under test and as a percentage of the theoretical oxygen demand for the reference substance - Reference substance:
- benzoic acid, sodium salt
- Test performance:
- The validity requirements of the OECD guideline state:
• the difference between extremes of replicate biodegradation values should be less than 20% at the end of 10-day window, at the plateau or at the end of the test;
• the positive control should achieve > 60% biodegradation by Day 14.
• the oxygen consumption of the inoculum blank should not exceed 60 mg/L in 28 days.
Mean oxygen uptake of the inoculum blank was below 60 mg/L, as required in the OECD guideline.
The difference between replicate Crodateric CYAP extremes was < 20% after the 10-day window, at plateau, and on day 28. Sodium benzoate reached a mean 68% biodegradation by Day 14. The mean oxygen consumed in the inoculum blanks was 12.4 mg/L after 28 days. Therefore, this test has satisfied all the validity criteria - Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- ca. 67
- St. dev.:
- 4
- Sampling time:
- 28 d
- Details on results:
- The COD of the test substance was measured as 1.66 g O2/g and the mean BOD value after 28 days was 1.1 g O2/g.
The percentage degradation was calculated as (BOD/COD) x 100 - Key result
- Parameter:
- COD
- Value:
- 1.66 g O2/g test mat.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- Crodateric CYAP attained a mean level of biodegradation (based on the BOD:COD ratio) of 67% after 28 days and the results showed good replication.
As Crodateric CYAP is UVCB, according to OECD and ECHA guidance documents, the 10-day window can be waived. Therefore, as > 60% biodegradation was achieved within 28 days Crodateric CYAP is readily biodegradable.
Reference
Description of key information
Crodateric CYAP attained a mean level of biodegradation (based on the BOD:COD ratio) of 67% after 28 days and the results showed good replication.
As Crodateric CYAP is UVCB, according to OECD and ECHA guidance documents, the 10-day window can be waived. Therefore, as > 60% biodegradation was achieved within 28 days Crodateric CYAP is readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
Additional information
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