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EC number: 204-124-8 | CAS number: 116-09-6
- 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
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:
- 2018/01/10-2018/02/07
- 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)
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Landesamt für Umwelt, 55116 Mainz (15.05.2018)
- Specific details on test material used for the study:
- The test item was stored in a tightly closed vessel at room temperature (20 ± 5°C).
- 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): The sludge was taken from the activation basin of the ESN (Stadtentsorgung Neustadt) sewage treatment plant, Im Altenschemel, NW-Lachen-Speyerdorf. Date of collection: 10. Jan. 2018, batch no: 20180110.
- Method of cultivation: The sludge was filtrated, washed with test medium 2x, and resuspended in test medium. It was then aerated. The dry matter was determined as 5000 mg suspended solids/L. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 66 mg/L
- Based on:
- test mat.
- Remarks:
- corresponding to a ThOD of 100.4 mg/L
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium:
The medium was freshly prepared (volumes were adapted to final volume needed in the test).
Composition:
Solution a 10 mL
Solution b 1 mL
Solution c 1 mL
Solution d 1 mL
H2O demin. ad 1000 mL
Solution a
Potassium dihydrogen phosphate (KH2PO4): 8.5 g
Dipotassium hydrogen phosphate (K2HPO4): 21.75 g
Disodium hydrogenphosphate dihydrate (Na2HPO4*2H2O): 33.4 g
Ammonium chloride (NH4Cl): 0.5 g
H2O demin. ad 1000 mL
The pH was 7.4.
Solution b
Calcium chloride (CaCl2) 27.5 g
H2O demin. ad 1000 mL
Solution c
Magnesium sulphate heptahydrate (MgSO4*7H2O) 22.5 g
H2O demin. ad 1000 mL
Solution d
Iron(III) chloride hexahydrate (FeCl3*6H2O) 0.25 g
Disodium ethylene-diaminetetraacetate dihydrate (Na2EDTA*2H2O) 0.4 g
H2O demin. ad 1000 mL
- Test temperature: 20.7-20.9 °C
- pH: 7.3-7.6
- pH adjusted: yes (7.4 - 7.6)
- Suspended solids concentration: dry matter was determined as 5000 mg suspended solids/L.
TEST SYSTEM
- Culturing apparatus: 500 mL-flasks were used as test vessels.
- Number of culture flasks/concentration: 3
- Measuring equipment: OxiTop®-C measuring heads
- Details of trap for CO2 and volatile organics if used: Evolved carbon dioxide is absorbed in soda lime (mixture of sodium hydroxide and calcium hydroxide). The soda lime is filled in the OxiTop®-C measuring heads
SAMPLING
- Sampling method:The oxygen which was consumed by the content of the vessels was measured automatically by the test apparatus.
CONTROL AND BLANK SYSTEM
- Inoculum blank: 3 test vessels (medium and inoculum)
- Abiotic sterile control: 1 test vessels (test item and 10 mL 1% HgCl2 solution/L)
- Toxicity control: 1 test vessels (199.11 mg/L ThOD, ThOD test item and ThOD positive control) - Reference substance:
- benzoic acid, sodium salt
- Remarks:
- 60 mg/L sodium benzoate (corresponding to a ThOD of 99.93 mg/L)
- Test performance:
- The oxygen which was consumed by the content of the vessels was measured automatically by the test apparatus.
After 28 days, the test was ended.
Because the test item and positive control do not contain nitrogen, presence of nitrate and nitrite was not checked. - Parameter:
- % degradation (O2 consumption)
- Value:
- 82
- Sampling time:
- 28 d
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 73
- Sampling time:
- 10 d
- Remarks on result:
- other: from day 2 to day 12
- Details on results:
- The degree of biodegradation reached 82 % after 28 days for the test item. The degradation phase was from day 2 to day 12.
The 10-day-window began on day 2. At its end (day 12), 73 % biodegradation was reached (this is stated as lag phase), staying above the pass level of 60 % given in the OECD guideline. - Results with reference substance:
- The positive control reached the pass level of 60% on day 4 (criterion: <= 14 days)
- Validity criteria fulfilled:
- yes
- Remarks:
- please refer to table 3
- Interpretation of results:
- readily biodegradable
- Conclusions:
- The degree of biodegradation reached 82 % after 28 days for the test item. The degradation phase was from day 2 to day 12. The 10-day-window began on day 2, at its end (day 12), 73 % biodegradation was reached (this is stated as lag phase), staying above the pass level of 60 % given in the OECD guideline.
Therefore, when applying the 10-day-window, the test item Hydroxyacetone is readily biodegradable following OECD 301F/EU C.4-D. - Executive summary:
The study for determination of the Ready Biodegradability of hydroxyacetone was conducted following OECD guideline 301F and EU mothod C.4 -D in compliance with GLP.
The test item hydroxyacetone was tested using a concentration of 66 mg test item/L (equivalent to a theoretical oxygen demand of 100.4 mg O2/L). Activated sludge was used as inoculum. The test was left running for 28 days. All validity criteria were met. The positive control reached the pass level of 60% on day 4 (criterion: <= 14 days).
The following data could be determined for the test item hydroxyacetone:
10-day-window: day 2 – 12
degradation at the end of 10-day-window 73 %
degradation at the end of the test 82 %
Therefore, when applying the 10-day-window, hydroxyacetone is classified as readily biodegradable following OECD 301F and EU C.4 -D, respectively.
Reference
table 2a: pH value on day 0 and day 28 and Oxygen demand and degradation values on day 28
Flask | Blank control 1 | Blank control 2 | Blank control 3 | Positive control 1 | Positive control 2 | Positive control 3 |
pH at day 0 | 7.6 | 7.6 | 7.6 | 7.6 | 7.6 | 7.6 |
pH at day 28 | 7.4 | 7.4 | 7.4 | 7.6 | 7.6 | 7.6 |
Oxygen demand in mg/L at day 28 | 19.8* | 21.5* | 21.5* | 108 | 110 | 104 |
Oxygen demand in mg/L after deductions | -- | -- | -- | 87.1 | 89.1 | 83.1 |
% biological degradation | -- | -- | -- | 87.1 | 89.1 | 83.1 |
*mean = 20.9 mg/L
table 2b: pH values on day 0 and day 28 and Oxygen demand and degradation values on day 28 (continued)
Flask | Test item1 | Test item2 | Test item3 | Mean Test item | Abiotic Control | Toxicity Control |
pH at day 0 | 7.6 | 7.6 | 7.6 | -- | 7.4 | 7.4 |
pH at day 28 | 7.4 | 7.4 | 7.4 | -- | 7.3 | 7.5 |
Oxygen demand in mg/L at day 28 | 102 | 106 | 101 | -- | 1.8 | 184 |
Oxygen demand in mg/L after deductions | 81.1 | 85.1 | 80.1 | -- | 1.8 | 163.1 |
% biological degradation | 80.7 | 84.7 | 79.8 | 81.7 | 1.8 | 81.9 |
table 3: Validity
Parameter | Criterion | Found | Assessment |
Degradation of positive control > 60% | < 14 days | 4 days | valid |
Mean O2 demand of the controls | < 60 mg/L | 20.9 mg/L | valid |
Degradation in the toxicity flask on day 14 | > 25% | *71 % | non - toxic |
pH at the end of the test | 6.0 - 8.5 | 7.3 - 7.6 | valid |
* Biological degradation of 71 % in the toxicity control on day 14 is calculated as follows:
DT = (OA - OB) / (ThODT * CT + ThODP * CP)* 100%
with:
OA O2-uptake in the toxicity flask in mg O2/L on day 14 = 160 mg/L
OB Mean O2-uptake of the control in mg O2/L on day 14 = 18 mg/L
ThODT Theoretical oxygen demand without nitrification test item = 1.512 mg O2 / mg test item
ThODP Theoretical oxygen demand without nitrification positive control = 1.665 mg O2 / mg positive control
CT Concentration of the test item in the toxicity flask = 66 mg/L
CP Concentration of the positive control in the toxicity flask = 60 mg/L
Description of key information
activated sludge, OECD 301 F, GLP: readily biodegradable
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
- Type of water:
- freshwater
Additional information
The study for determination of the Ready Biodegradability of hydroxyacetone was conducted following OECD guideline 301F and EU mothod C.4 -D in compliance with GLP.
The test item hydroxyacetone was tested using a concentration of 66 mg test item/L (equivalent to a theoretical oxygen demand of 100.4 mg O2/L). Activated sludge was used as inoculum. The test was left running for 28 days. All validity criteria were met. The positive control reached the pass level of 60% on day 4 (criterion: <= 14 days).
The following data could be determined for the test item hydroxyacetone:
10-day-window: day 2 – 12
degradation at the end of 10-day-window 73 %
degradation at the end of the test 82 %
Therefore, when applying the 10-day-window, hydroxyacetone is classified as readily biodegradable following OECD 301F and EU C.4 -D, respectively.
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