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EC number: 209-963-3 | CAS number: 599-04-2
- 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
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 2009-10-05 to 2009-12-15
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: OECD guideline compliant GLP compliant
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 009
- Report date:
- 2009
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 A (Ready Biodegradability: DOC Die Away Test)
- Version / remarks:
- as at 1992
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-A (Determination of the "Ready" Biodegradability - Dissolved Organic Carbon (DOC) Die-Away Test)
- Version / remarks:
- as at 2008
- Deviations:
- no
- GLP compliance:
- yes
Test material
- Reference substance name:
- α-hydroxy-β,β-dimethyl-γ-butyrolactone
- EC Number:
- 209-963-3
- EC Name:
- α-hydroxy-β,β-dimethyl-γ-butyrolactone
- Cas Number:
- 599-04-2
- Molecular formula:
- C6H10O3
- IUPAC Name:
- (3R)-3-hydroxy-4,4-dimethyloxolan-2-one
- Details on test material:
- - Name of test material (as cited in study report): R-Pantolactone
- Physical state: white to yellowish crystalline mass
- Analytical purity: 99.6 %
- Lot/batch No.: Bx TL 00906092
- Expiration date of the lot/batch: June 2011
- Storage condition of test material: at room temperature, protected from sunlight
Constituent 1
Study design
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- - Source of inoculum/activated sludge: aerobic activated sludge from municipal STP (ARA Ergolz II, Füllinsdorf, Switzerland)
- Method of cultivation: not cultivated
- Storage length: not stored, freshly obtained sludge was used
- Pretreatment: sludge was washed twice with tap water by centrifugation, decantation of supernatant and resuspension
- Concentration of sludge: 4 g (± 10%) dry matter per litre - Duration of test (contact time):
- 21 d
Initial test substance concentration
- Initial conc.:
- 51.1 - 51.7 mg/L
- Based on:
- test mat.
Parameter followed for biodegradation estimation
- Parameter followed for biodegradation estimation:
- DOC removal
- Details on study design:
- TEST CONDITIONS
- Composition of medium: mineral medium was prepared in accordance with the technical guideline
- Additional substrate: not applicable
- Solubilising agent (type and concentration if used): not applicable
- Test temperature: 22 to 24 °C
- pH: 7.3 to 7.4
- pH adjusted: no
- Suspended solids concentration: 30 mg/L
- Continuous darkness: yes
TEST SYSTEM
- Culturing apparatus: 2000 mL Erlenmeyer flasks, final volume of test medium was 1000 mL
- Number of culture flasks/concentration: 2
- Method used to create aerobic conditions: flasks were loosely covered with aluminium foil to allow air exchange between flasks and surrounding environment, contents were continuously stirred
- Measuring equipment: TOC analyser equipped with automatic sampler (Shimadzu TOC-5000A)
- Test performed in open system: yes
SAMPLING
- Sampling frequency: test item and inoculum control were sampled on days 0, 3, 7, 10, 14, 21; positive reference substance control was sampled on days 0, 3, 7, 14 and 21; toxicity control was sampled on days 0, 7, 14 and 21
- Sampling method: one sample of about 10 mL was taken from each test flask per sampling date; prior to sampling, losses by water evaporation were determined and were compensated by adding purified water
- Sample storage before analysis: samples were analysed immediately or stored at -2 to -4 °C for 24 hours
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes
- Abiotic sterile control: no
- Toxicity control: yes
Reference substance
- Reference substance:
- acetic acid, sodium salt
- Remarks:
- for details see above under "reference substance"
Results and discussion
- Preliminary study:
- not applicable
- Test performance:
- - Biodegradation started between experimental days 3 and 7
- 70% DOC removal was seen during a 10-day window in the flasks with test substance and activated sludge
- Complete DOC removal was seen within a test period of 21 days
- Postive reference substance was degraded (> 90%) within seven days
- The substance was not inhibiting to the activity of the active sludge
% Degradationopen allclose all
- Parameter:
- % degradation (DOC removal)
- Value:
- 56 - 67
- Sampling time:
- 7 d
- Parameter:
- % degradation (DOC removal)
- Value:
- 100
- Sampling time:
- 14 d
- Details on results:
- See tables under "Any other information on results"
BOD5 / COD results
- Results with reference substance:
- The positive control substance was degraded by at least 90% with 7 days.
Any other information on results incl. tables
Table 1: Dissolved organic carbon concentrations (DOC) in the test flasks
Time (days) |
Dissolved organic carbon (DOC) in mg/L1, 2 |
|||||||||
Test substance |
Positive control |
Inoculum control |
Toxicity control |
|||||||
Replicate No |
Replicate No |
Replicate No |
Replicate No |
|||||||
1 |
2 |
Mean3 |
1 |
2 |
Mean3 |
1 |
2 |
Mean |
13 |
|
0 |
31.5 |
30.5 |
27.7 |
32.4 |
31.6 |
28.7 |
4.3 |
2.3 |
3.3 |
56.5 |
3 |
30.8 |
31.3 |
28.5 |
3.7 |
2.4 |
0.5 |
1.9 |
3.3 |
2.6 |
-- |
7 |
11.9 |
14.4 |
10.7 |
4.4 |
3.4 |
1.3 |
2.7 |
2.5 |
2.6 |
28.2 |
10 |
2.9 |
3.1 |
0.2 |
-- |
-- |
-- |
2.5 |
3.2 |
2.9 |
-- |
14 |
2.6 |
2.1 |
0.1 |
3.2 |
2.3 |
0.5 |
2.4 |
2.2 |
2.3 |
1.5 |
21 |
2.3 |
2.2 |
0.0 |
2.3 |
2.5 |
0.2 |
2.3 |
2.2 |
2.3 |
1.6 |
1) Mean values of at least triplicate measurements per sample; 2) Sampling was ended before 28 days because the biodegradation curve reached a plateau for three determinations; 3) Values corrected for the inoculum controls; -- not determined |
Table 2: Percentage biodegradation in the test flasks
Time (days) |
Percentage biodegradation1, 2 |
||||||
Test |
Positive control |
Toxicity control |
|||||
Replicated No. |
Replicated No. |
Replicated No. |
|||||
1 |
2 |
Mean |
1 |
2 |
Mean |
1 |
|
0 |
0 |
0 |
0 |
0 |
0 |
0 |
0 |
3 |
0 |
-6 |
-3 |
96 |
101 |
98 |
-- |
7 |
67 |
56 |
61 |
94 |
97 |
95 |
50 |
10 |
100 |
99 |
99 |
-- |
-- |
-- |
-- |
14 |
99 |
101 |
100 |
97 |
100 |
98 |
97 |
21 |
100 |
100 |
100 |
100 |
99 |
99 |
97 |
1) Corrected for inoculum controls; 2) Sampling was ended before 28 days because the biodegradation curve reached a plateau for three determinations; -- not determined |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- readily biodegradable
- Conclusions:
- The substance was found to be readily biodegradable in a valid study according to the DOC Die Away test.
- Executive summary:
The ready biodegradability of the test substance R-Pantolactone was studied under GLP in accordance with OECD TG 301-A (DOC Die Away test). Non-adopted activated sludge freshly collected from a municipal STP treating mainly domestic sewage was used in the test, which was suspended in standard mineral medium prepared according to the guideline at a concentration of 30 mg/L suspended matter. The concentration of test medium in the flasks was about 50 mg/L. The study was conducted in 2-L Erlenmeyer flasks that were loosely covered during the test. The test volume of continuously stirred test medium was 1000 mL per flask, the test temperature was 22 to 24 °C and the test was performed in the dark. In parallel, flasks with the inoculum alone, with the positive control sodium benzoate and with a mixture of positive reference substance and test substance (toxicity control) were tested under similar conditions. The reference substance was degraded by more than 90% within 14 days and the test substance did not inhibit the activity of the activated sludge. The test was considered as valid. Biodegradation of the test substance commenced between day 3 and 7 and reached more than 70% within a 10-day window. Complete biodegradation of the test substance was observed within 21 days and the test was ceased as biodegradation reached a plateau for three consecutive measurements.
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