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Diss Factsheets
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EC number: 932-164-2 | 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:
- From 3 November 1999 to 16 August 1999
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- other: EPA-Test Guideline CG-2050
- Deviations:
- yes
- Remarks:
- solutions 4 and 5
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- anaerobic
- Inoculum or test system:
- other: sewage, domestic
- Details on inoculum:
- - Laboratory culture: treatment plant at Taunusstein-Bleidenstadt
- Method of cultivation: the sludge was obtained directly from the digestor - Duration of test (contact time):
- 56 d
- Initial conc.:
- ca. 17.54 g/L
- Based on:
- test mat.
- Details on study design:
- TEST CONDITIONS
- Test temperature: 35±1ºC
- pH: 8.15
Solution 1*
0.5 g Resazurin
Solution 2*
20g (NH4)2HPO4
100 g NH4Cl
Solution 3*
23.84g CaCl2x2H2O
180g MgCl2x6H2O
130g KCl
2g MnCl2x4H2O
3g CoCl2x6H2O
0.6gH3BO3
0.23g CuCl2x2H2O
1.0g Na2MoO4x2H2O
0.2g ZnCl2
*were dissolved in 1L Ultrapure water
Solution 4+
The "solution 4" as described in the protocol (368g FeCl2x4H2O in 1L ultrapure water) was replaced by the addition of 2944 mg FeCl2x4H2O to 8000mL of final volume of the test solution.
Solution 5+
The "solution 5" as described in the protocol (50g Na2Sx9H2O in 1L ultrapure water) was replaced by the addition of 4mg Na2Sx9H2O to 8000mL of final volume of the test solution.
+This is a desviation of the protocol. The reason for this deviation is the aim of minimizing the introduction of any oxygen into the test solution.
- Parameter:
- other: tranformed into biogas
- Value:
- 81
- Sampling time:
- 56 d
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- other: biodegradable under anaerobic conditions
- Conclusions:
- The test substance was transformed 81% into biogas in 56 days and therefore can be considered as biodegradable under anaerobic conditions.
- Executive summary:
The substance was investigated for biodegradability under anaerobic conditions according to EPA Guideline CG-2050. In the same test, inhibitory/retardant properties towards methanogenic microflora could be determined. Under the conditions of this test the test substance was transformed 81% into biogas. The control substance ethanol was degraded 95% in the same time. There was a ratardant property of the test substance which was >20% only at the beginning of the test. The mathematical value of 7.6% "inhibition" is negligible.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 11/2/2003-12/3/2003
- 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)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-C (Determination of the "Ready" Biodegradability - Carbon Dioxide Evolution Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- other: activated sewage sludge micro-organisms
- Details on inoculum:
- - Source of inoculum/activated sludge: activated sewage sludge micro-organism
- Laboratory culture: aerobic stage of the Severn Trent Water Plc sewage treatment plant at Loughborough, Leicestershire, UK, which treats predominantly domestic sewage. - Duration of test (contact time):
- 28 d
- Initial conc.:
- 30 mg/L
- Based on:
- other: suspended solid
- Initial conc.:
- 10 mg/L
- Based on:
- other: carbon
- Details on study design:
- The following test preparation were prepared and inoculated in 5 litre glass culture vessels each containing 3 litres of solution:
a) A control, in duplicate, consisting of inoculated culture medium.
b) The standard material (sodium benzoate), in duplicate, in inoculated culture medium to give a final concentration of 10 mg carbon/L.
c) The test material, in duplicate, in inoculated culture medium to give a final concentration of 10 mg carbon/L.
d) The test material plus the standard material in inoculated culture medium to give a final concentration of 20 mg carbon/L to act as a toxicity control (one vessel only). - Reference substance:
- benzoic acid, sodium salt
- Parameter:
- % degradation (CO2 evolution)
- Value:
- 96
- Sampling time:
- 28 d
- Validity criteria fulfilled:
- yes
- Remarks:
- The result og the degradtion test are considered valid if in the same test the standard material yields >= 60% degradation by Day 14.
- Interpretation of results:
- readily biodegradable
- Conclusions:
- The test material attained 96% degradation after 28 days and satisfied the 10-Day window validation criterion, whereby 60% degradation must be attained within 10 days of the degradation rate exceeding 10%. The test material can therefore be considered to be readily biodegradable under the strict terms and conditions of OECD Guideline No 301B.
- Executive summary:
A study was performed to assess the ready biodegradability of the test material in an aerobic aqueous medium. The method followed that described in the OECD Guideline for Testing Chemicals (1992) No 301B, "Ready Biodegradability; CO2 Evolution Test" referenced as Method C.4 -C of Commission Directive and US EPA Fate, Tranport, and Transformation Test Guidelines OPPTS 835.3110 Paragraph (m). The test material, at a concentration of 10 mg C/L, was exposed to activated sewage sludge micro-organisms with culture medium in sealed culture vessels in the dark at 21ºC for 28 days. The degradation of the test material was assessed by the determination of carbon dioxide produced. Control solutions with inoculum and the standard material, sodium benzoate, together with a toxicity control were used for validation purposes. The test material attained 96% degradation after 28 days and satisfied the 10 -Day window validation criterion, whereby 60% degradation must be attained within 10 days of the degradation rate exceeding 10%. The test material can therefore be considered to be readily biodegradable under strict terms and conditions of OECD Guideline No 301B.
Referenceopen allclose all
Time (d) | %Degradation |
1 | 1,9 |
4 | 1,9 |
7 | 34,3 |
10 | 44 |
14 | 52 |
18 | 56 |
21 | 61 |
39 | 75 |
44 | 80 |
50 | 80 |
56 | 81 |
Description of key information
Aerobic biodegradation: The test material attained 96% degradation after 28 days and satisfied the 10-Day window validation criterion, whereby 60% degradation must be attained within 10 days of the degradation rate exceeding 10%.
Anaerobic biodegradation: In a test according to EPA Guideline CG-2050 the test substance was transformed 81% into biogas.
Key value for chemical safety assessment
- Biodegradation in water:
- readily biodegradable
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.