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EC number: 273-222-0 | CAS number: 68953-64-0
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
- Version / remarks:
- adopted July 17, 1992
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Identification: Quaternium-26
Appearance: Clear amber to dark amber liquid
Batch: 0001954899
Purity/Composition: UVCB
Test item storage: At room temperature
Stable under storage conditions until 22 December 2017 (retest date) - Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic (adaptation not specified)
- Details on inoculum:
- The source of test organisms was activated sludge freshly obtained from a municipal sewage treatment plant: 'Waterschap Aa en Maas', 's-Hertogenbosch, The Netherlands, receiving predominantly domestic sewage.
The freshly obtained sludge was used immediately. The concentration of suspended solids was determined to be 3.57 g/L in the concentrated sludge.
For experiment A, the sludge was allowed to settle (47 minutes) and the supernatant liquid was used as inoculum at the amount of 10 mL/L of mineral medium.
For experiment B, the sludge was allowed to settle (45 minutes) after which the supernatant was funnelled off and the sludge was made up to the initial volume using ISO-medium. The sludge was aerated (182 minutes) and diluted with ISO-medium to reach a SS concentration of 3.0 g/L. Magnetically stirred sludge was used as inoculum at the amount of 10 mL/L of mineral medium. The SS concentration in the test bottles of experiment B was 30 mg/L. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 25 mg/L
- Based on:
- test mat.
- Remarks:
- The test item was tested in duplicate at a target concentration of 25 mg/L, corresponding to 12 mg TOC/L.
- Parameter followed for biodegradation estimation:
- CO2 evolution
- Details on study design:
- Test duration:
- 28 days for the inoculum blank and test item (last CO2measurement on day 29).
- 14 days for the positive and toxicity control (last CO2 measurement on day 15).
Test vessels: 2 litre brown coloured glass bottles.
Pre-incubation medium: The day before the start of the test (day -1) mineral components, Milli-RO water (ca. 80% of final volume) and inoculum (1% of final volume) were added to each bottle. This mixture was aerated with synthetic CO2-free air overnight to purge the system of CO2.
On the day of testing the test item was added to the 2-litres test bottles containing medium with microbial organisms and mineral components, using weighed amounts on a small watch glass. For experiment A, these amounts were: test item bottle A: 49.8 mg; test item bottle B:50.0 mg. For experiment B, these amounts were: test item bottle A: 50.2 mg; test item bottle B: 49.9 mg.
Additional bottles: 2 bottles for blank with inoculum; 2 bottles for the propylene glycol control (solvent control), 1 bottle for the Positive control: containing reference item and inoculum or the toxicity control containing reference item with test item and inoculum
Preparation: At the start of the test (day 0), test and reference item were added to the bottles containing the microbial organisms and mineral components. The volumes of suspensions were made up to 2 litres with Milli-RO water, resulting in the mineral medium described before. Three CO2-absorbers (bottles filled with 100 mL 0.0125 M Ba(OH)2) were connected in series to the exit airline of each test bottle.
Determination of CO2:
The CO2 produced in each test bottle reacted with the barium hydroxide in the gas scrubbing bottle and precipitated out as barium carbonate. The amount of CO2 produced was determined by titrating the remaining Ba(OH)2 with 0.05 M standardized HCl (1:20 dilution from 1 M HCl (Titrisol® ampoule), Merck, Darmstadt, Germany). Test item titrations were made on day 1, 4, 6, 8, 11, 15, 18, 22, 25 and 29.
On the penultimate day, the pH of respective test suspensions was measured and 1 mL of concentrated HCl (37%, Merck) was added to the bottles of the inoculum blank and test suspension. The bottles were aerated overnight to drive off CO2 present in the test suspension.
The final titration was made on day 15 for positive and toxicity control, and on day 29 for the remaining vessels. - Reference substance:
- acetic acid, sodium salt
- Key result
- Parameter:
- % degradation (CO2 evolution)
- Remarks:
- Based on measurements of two separate bottles.
- Value:
- 122
- St. dev.:
- 5
- Sampling time:
- 28 d
- Details on results:
- The relative biodegradation values calculated from the measurements performed during the test period revealed 102% and 108% biodegradation of Quaternium-26, for A and B, respectively (based on ThCO2). Furthermore, biodegradation of Quaternium-26 of at least 60% was reached within a 10-day window.
The relative biodegradation values calculated for the solvent control revealed 77% and 79% biodegradation for A and B, respectively.
The relative biodegradation values calculated from the measurements performed during the test period revealed 117% and 127% biodegradation of Quaternium-26 (corrected for PG), for A and B, respectively (based on ThCO2). - Results with reference substance:
- > 80% within 15 days.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Remarks:
- k1st order = 0.0173x, R² = 0.9703
- Conclusions:
- In conclusion, Quaternium-26 was readily biodegradable under the conditions of the modified Sturm test presently performed in experiment B. According to the OECD 301 Guideline, showing ready biodegradability in a single test is sufficient to classify a test item as readily biodegradable. Therefore, it can be concluded that Quaternium-26 is readily biodegradable.
Reference
Description of key information
Quaternium-26 was readily biodegradable under the conditions of a modified Sturm test. According to the OECD 301 Guideline, showing ready biodegradability in a single test is sufficient to classify a test item as readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
- Type of water:
- freshwater
Additional information
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