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Diss Factsheets
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EC number: 944-329-6 | 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
- Study period:
- 22 May - 20 Jun 2017
- 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)
- Version / remarks:
- 1992
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-D (Determination of the "Ready" Biodegradability - Manometric Respirometry Test)
- Version / remarks:
- 2008
- Qualifier:
- according to guideline
- Guideline:
- EPA OPPTS 835.3110 (Ready Biodegradability)
- Version / remarks:
- 1998
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Swiss Federal Office of Public Health, Bern, Switzerland
- 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 activated sludge was obtained from the aeration stage of wastewater treatment plant "ARA Birs", Birsfelden, Switzerland.
- Preparation of inoculum for exposure: The sludge was washed three times by centrifugation, decantation of the supernatant liquid phase and resuspension of the solid phase in tap water and finally in mineral medium.
- Storage length: 1 d
- Storage conditions: Sludge was aerated at room temperature.
- Concentration of sludge: 30 mg dry material/L - Duration of test (contact time):
- 28 d
- Initial conc.:
- 100 mg/L
- Based on:
- test mat.
- Initial conc.:
- 235 mg/L
- Based on:
- COD
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- TEST CONDITIONS
- Composition of medium: according to guideline, prepared in purified water
- Test temperature: 22 - 23 °C in a thermostatic cabinet
- pH: 7.4 (test start), 7.4 - 7.8 (test end)
- pH adjusted: The pH of the test medium was adjusted from 7.8 to 7.4 with a diluted hydrochloric acid solution.
- Suspended solids concentration: 30 mg/L
- Continuous darkness: no, diffuse lighting
TEST SYSTEM
- Culturing apparatus: GL45 laboratory glass bottles (volume: 500 mL; fill volume: 164 mL; headspace: 336 mL), air-tight closed with OxiTop measuring heads.
- Number of culture flasks/concentration: 2
- Measuring equipment: OxiTop measuring heads
- Test performed in closed vessels: yes
- Details of trap for CO2 and volatile organics if used: CO2 was absorbed by an alkali trap.
SAMPLING
- Sampling frequency: BOD values were recoreded automatically every three hours.
- Sampling method: No sampling was necessary since the gas pressure reduction was measured continuously.
- Sterility check if applicable: no
CONTROL AND BLANK SYSTEM
- Inoculum blank: yes, two replicates
- Abiotic sterile control: no
- Toxicity control: yes, 1 replicate
- Other: procedure control: yes, 2 bottles - Reference substance:
- benzoic acid, sodium salt
- Remarks:
- Tested at a concentration of 100 mg/L.
- Parameter:
- % degradation (O2 consumption)
- Value:
- 0
- Sampling time:
- 28 d
- Results with reference substance:
- The reference item was degraded by an average of 67 and 87% after 3 d and 14 d, respectively(≥ 60 % degradation after 14 d). After 28 d the reference item was degraded to 91%.
- Validity criteria fulfilled:
- yes
- Remarks:
- For further details please refer to “Any other information on results incl. tables”.
- Interpretation of results:
- under test conditions no biodegradation observed
- Conclusions:
- The available study was performed according to OECD 301F (GLP). After 28 days, no biodegradation was recorded. Consequently, the substance is considered to be not biodegradable under the test conditions within 28 days. The study is valid since all validity criteria were met. Moreover, the test item is not inhibitory to the inoculum since significant degradation was recorded in the toxicity control (≥ 25% degradation by Day 14).
Reference
Table 1: % degradation of the test item
|
Percent degradation |
||||
Test item |
Reference substance |
Toxicity control |
|||
Replicate |
Replicate |
Replicate |
|||
1 |
2 |
1 |
2 |
1 |
|
0 |
0 |
0 |
0 |
0 |
0 |
1 |
-1 |
0 |
26 |
25 |
11 |
2 |
-1 |
1 |
48 |
46 |
19 |
3 |
-2 |
0 |
67 |
68 |
28 |
4 |
-2 |
-1 |
73 |
73 |
29 |
5 |
-2 |
-1 |
76 |
76 |
30 |
6 |
-2 |
-1 |
77 |
79 |
31 |
7 |
-2 |
-1 |
79 |
79 |
32 |
8 |
-3 |
-2 |
79 |
80 |
32 |
9 |
-2 |
-1 |
81 |
84 |
33 |
10 |
-3 |
-1 |
82 |
84 |
33 |
11 |
-3 |
-1 |
84 |
85 |
34 |
12 |
-2 |
-1 |
85 |
85 |
34 |
13 |
-3 |
-1 |
85 |
87 |
35 |
14 |
-2 |
-1 |
87 |
87 |
35 |
15 |
-3 |
-1 |
88 |
87 |
35 |
16 |
-3 |
-1 |
88 |
88 |
35 |
17 |
-3 |
-1 |
89 |
88 |
35 |
18 |
-3 |
-1 |
89 |
88 |
35 |
19 |
-2 |
-1 |
90 |
89 |
36 |
20 |
-2 |
-1 |
91 |
89 |
35 |
21 |
-3 |
-1 |
91 |
89 |
36 |
22 |
-2 |
-1 |
92 |
90 |
36 |
23 |
-2 |
0 |
91 |
91 |
36 |
24 |
-3 |
-1 |
92 |
91 |
36 |
25 |
-3 |
0 |
92 |
92 |
36 |
26 |
-2 |
0 |
92 |
92 |
36 |
27 |
-2 |
0 |
92 |
92 |
37 |
28 |
-3 |
-1 |
91 |
91 |
36 |
Table 2: Validity criteria
Criterion from the guideline |
Outcome |
Validity criterion fulfilled |
Difference of extremes of replicate values of the removal of the test chemical at the plateau, at the end of the test or at the end of the 10-d window, as appropriate, is less than 20%. |
Not applicable since no biodegradation was recorded. |
Not applicable |
Percentage degradation of the reference compound has reached the pass levels by day 14. |
67% after 14 d |
yes |
The oxygen uptake of the inoculum blank is normally 20-30 mg O2/L and should not be greater than 60 mg/L in 28 days. |
17 mg/L |
yes |
Description of key information
Not biodegradable: 0% after 28 d (O2 consumption, OECD 301F)
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
One experimental study is available investigating the
biodegradation of the substance. The study was performed according to
OECD 301F (GLP) using activated sludge from a domestic sewage treatment
plant (non-adapted). 100 mg/L (235 mg/L based on COD) of the substance
was tested and the O2 consumption was measured automatically every 3 h
for 28 d. In addition a toxicity control was prepared containing test
item and reference substance (benzoic acid, sodium salt) in order to
assess possible toxic effects of the test item to the inoculum.
After 28 days no biodegradation was recorded (0%). Thus, the substance
is not readily biodegradable according to the OECD criteria. In the
toxicity control a biodegradation of 36% was recorded indicating that
the substance is not inhibitory to the inoculum.
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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