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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
- 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:
- yes
- Remarks:
- (on four measurements the temperatures recorded for the water bath were below the recommended minimum temperature. As the validity criteria were met, this deviation was not considered to have affected the integrity of the study.)
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-D (Determination of the "Ready" Biodegradability - Manometric Respirometry Test)
- Deviations:
- yes
- Remarks:
- (on four measurements the temperatures recorded for the water bath were below the recommended minimum temperature. As the validity criteria were met, this deviation was not considered to have affected the integrity of the study.)
- 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: Worlingworth sewage treatment works (Suffolk, UK)
- Method of cultivation / Preparation of inoculum for exposure: At the time of collection, the sludge was sieved (1 mm²) then transported to the laboratory and left stand for approximately 30 minutes to allow the sewage solids to settle. A portion of the supernatant was removed and the sludge aerated until required. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 50 mg/L
- Based on:
- ThOD/L
- Initial conc.:
- 18 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: mineral salts medium (MSM) according to guideline, prepared using tap-water that had been softened and treated by reverse osmosis and then purified; nominal resistivity ≥ 18 MegOhm.cm. The pH was adjusted to 7.56 with 5M HCl. This water complies with the relevant standards (British Standard (BS) 3978, 1987; American Society for Testing and Materials (ASTM) D 1193-06) for classification as Grade 1 or Type 1 water for laboratory use.
- Test temperature: 21.3 to 21.9°C. On Days 6, 15, 20, and 28 the minimum temperatures recorded for the water bath were below this range (18.2, 12.2, 18.2 and 18.0°C respectively). These low temperature values were considered anomalous as the ambient room temperature over the course of the study was considered acceptable. The reasons for these low recorded values are unknown. As the validity criteria for the study were met, this deviation from protocol is not considered to have affected the integrity of the study.
- pH: 7.5 at the start of the test and 7.5 to 8.1 at the end
- pH adjusted: not necessary
- Suspended solids concentration: 30 mg/L
- Continuous darkness: yes (amber glass bottles)
- Other: The inoculum was added to the culture bottles 1 day before test initiation to allow a period of ageing.
TEST SYSTEM
- Culturing apparatus: amber glass culture bottles in a thermostatically controlled water bath
- Number of culture flasks/concentration: 2
- Method used to create aerobic conditions: internal oxygen generating process
- Measuring equipment: Co-ordinated Environmental Services (CES) Ltd automated respirometer with associated software to monitor the cumulative amount of oxygen consumed
SAMPLING
- Sampling frequency: continuous monitoring of the cumulative amount of oxygen consumed; the cumulative oxygen demand made by each cell was printed at, typically, hourly intervals
CONTROL AND BLANK SYSTEM
- Inoculum blank (2 flasks): inoculated mineral salts medium (MSM)
- Reference (1 flask): inoculated MSM + sodium benzoate (50 mg O₂/L)
- Toxicity control (1 flask): inoculated MSM + test material (50 mg O₂/L) + sodium benzoate (50 mg O₂/L) - Reference substance:
- benzoic acid, sodium salt
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- 6
- Sampling time:
- 28 d
- Details on results:
- Due to the complex nature, and owing the low nitrogen content of the test material, there was considered to be no indication that any nitrification observed would be significant.
In the presence of test material the degradation of sodium benzoate achieved 62% after 3 days indicating that the test substance was not inhibitory to the microbial inoculum (Table 1). - Results with reference substance:
- The reference substance sodium benzoate had achieved 64% of the ThOD after 3 days of incubation and 101% by Day 28 (Table 1).
- Validity criteria fulfilled:
- yes
- Remarks:
- the removal of the test substance in replicate values differed less than 20%, the reference compound reached the pass level by day 3, and the cumulative amount of oxygen consumed by the control mixtures was 35-36 mg O₂/L
- Interpretation of results:
- under test conditions no biodegradation observed
Reference
Table 1: Biodegradation of the test and reference substances
% Biodegradation |
|||||
Day |
Test material (50 mgO2/L) |
Sodium Benzoate (50 mgO2/L) |
Sodium Benzoate (50 mgO2/L) in the inhibition mixture |
||
Test 1 |
Test 2 |
Mean |
|||
1 |
1 |
1 |
1 |
38 |
46 |
2 |
2 |
1 |
1 |
57 |
55 |
3 |
2 |
1 |
2 |
64 |
62 |
4 |
1 |
2 |
1 |
70 |
- |
5 |
1 |
2 |
2 |
74 |
- |
6 |
2 |
2 |
2 |
78 |
- |
7 |
2 |
2 |
2 |
80 |
- |
8 |
3 |
2 |
3 |
82 |
- |
9 |
3 |
2 |
3 |
84 |
- |
10 |
3 |
3 |
3 |
85 |
- |
11 |
3 |
3 |
3 |
87 |
- |
12 |
4 |
3 |
3 |
88 |
- |
13 |
4 |
3 |
3 |
89 |
- |
14 |
4 |
3 |
3 |
90 |
- |
15 |
4 |
3 |
3 |
91 |
- |
16 |
4 |
3 |
4 |
92 |
- |
17 |
4 |
3 |
4 |
93 |
- |
18 |
5 |
4 |
4 |
94 |
- |
19 |
5 |
4 |
4 |
95 |
- |
20 |
5 |
4 |
5 |
96 |
- |
21 |
5 |
4 |
5 |
96 |
- |
22 |
5 |
5 |
5 |
97 |
- |
23 |
5 |
5 |
5 |
98 |
- |
24 |
5 |
5 |
5 |
99 |
- |
25 |
5 |
5 |
5 |
99 |
- |
26 |
5 |
5 |
5 |
100 |
- |
27 |
6 |
5 |
6 |
101* |
- |
28 |
6 |
6 |
6 |
101* |
- |
*: Value slightly exceeds 100% of the available concentration. However this was not considered significant as this is within the level of experimental error for this type of study.
Description of key information
Biodegradation in water: screening tests: biodegradation <10% (ThOD) in 28 days (OECD 301F, EU C4-D)
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
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.
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