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EC number: 247-665-5 | CAS number: 26401-86-5
- 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:
- 11 November 1999 to 20 December 2000
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Reason / purpose for cross-reference:
- other: read-across target
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 301 F (Ready Biodegradability: Manometric Respirometry Test)
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.4-D (Determination of the "Ready" Biodegradability - Manometric Respirometry Test)
- Qualifier:
- according to guideline
- Guideline:
- ISO DIS 9408 (Ultimate Aerobic Biodegradability - Method by Determining the Oxygen Demand in a Closed Respirometer)
- Principles of method if other than guideline:
- The Manometric Respirometry Test is a static method for testing the ultimate aerobic biodegradability of a test substance in water. Mixtures of the test substance, a defined inorganic medium and an inoculum, which is not pre-adapted (e.g. activated sludge or effluent of a municipal or laboratory waste water treatment plant), are incubated and aerated in a respirometer (Sapromat) at room temperature up to 28 days regularly. The test period may be expanded if biodegradation processes are still ongoing after 28 days. The oxygen used for the biodegradation of the test substance (biochemical oxygen demand, BOD) is continuously produced and measured by the test apparatus.
In addition to the assays with test substance (in triplicate) the following investigations are required: blank values (BC), biodegradation of a reference substance (RS), inhibition of the inoculum (IH) and abiotic elimination (PC). - GLP compliance:
- yes
- Oxygen conditions:
- aerobic
- Inoculum or test system:
- activated sludge, domestic, non-adapted
- Details on inoculum:
- Municipal activated sludge from the waste water treatment plant of Mannheim, stored for 12 days in laboratory waste water treatment plant (WWTP) No. 1 which was fed with municipal waste water. One day before the start of the test the sludge from laboratory WWTP No.1 was washed and aerated for 24 hours and then added to the test vessels to obtain a sludge concentration of 30 mg/l dry solids.
- Duration of test (contact time):
- 39 d
- Initial conc.:
- 50 mg/L
- Based on:
- test mat.
- Parameter followed for biodegradation estimation:
- O2 consumption
- Details on study design:
- Evaluation of Test Results
The biochemical oxygen demand gives unequivocal evidence for biodegradation. The measured BOD is compared with the calculated theoretical oxygen demand (ThOD) or the measured chemical oxygen demand (COD) of the test substance and indicated as biodegradation degree in per cent. Since the micro-organisms oxidize only part of the test substance and incorporate the rest as biomass, substances with a degree of >60 % biodegradation are considered to be sufficiently biodegradable. The relation BOD to ThOD or COD is considered by the author as follows:
>60 % in 10 days - "readily biodegradable (OECD criteria)"
>60% - "biodegradable"
20-60% - "in this test primarily biodegradable"
<20% - "in this test poorly biodegradable"
One of the OECD criteria for ready biodegradable substances is the threshold value of 60% biodegradation within a period of 10 days during a total test period of 28 days. If a test substance is biodegradable in this test, it can be assumed that it will be biodegraded in the environment, especially in wastewater treatment plants and surface waters. - Reference substance:
- aniline
- Test performance:
- No unusual observations
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- >= 30 - <= 40
- Sampling time:
- 28 d
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- >= 50 - <= 60
- Sampling time:
- 39 d
- Details on results:
- Calculated specific BOD values (cumulative, by day sampled), in mg/g:
[data are reported as reference (aniline), followed by each test substance replicate]
1d: -40, 20, -60, -20
4d: 580, 60, 20, 79
7d: 1620, 79, 119, 139
10d: 1880, 179, 238, 258
13d: 2140, 278, 317, 317
16d: 2600, 397, 437, 397
19d: 2820, 516, 595, 516
22d: 2900, 556, 734, 595
25d: 2940, 635, 853, 655
28d: 3020, 694, 972, 774
*39d: 3120, 1052, 1409, 1151
* - incubation time was increased to 39 days as biodegradation of the test substance was shown to be a comparatively slow process
BOD of blank (after 39 days) = 16 mg/L
Biodegradation in relation to ThOD (cumulative, by day sampled), in %:
[data are reported as reference (aniline), followed by each test substance replicate]
1d: -2, 1, -3, -1
4d: 24, 3, 1, 4
7d: 68, 4, 5, 6
10d: 79, 8, 11, 12
13d: 89, 13, 14, 14
16d: 109, 18, 20, 18
19d: 118, 23, 27, 23
22d: 121, 25, 33, 27
25d: 123, 29, 39, 30
28d: 126, 32, 44, 35
*39d: 130, 48, 64, 52
* - incubation time was increased to 39 days as biodegradation of the test substance was shown to be a comparatively slow process
The reference substance (aniline) was degraded more than 60% in 10 days and the BOD of the blank after 39 days was 16 mg/L (within the test method criteria of 60 mg/L).
Octyltin tris(EHMA) was degraded 32-44% after 28 days and was determined to be not readily biodegradable.
Kinetic of test substance (in %):
= 8 ... 12 after 10 day(s)
= 32 ... 44 after 28 day(s)
= 48 ... 64 after 39 day(s)
Kinetic of control substance (in %):
= ... 79 after 10 day(s)
> ... 100 after 39 day(s)
Degradation products: not measured - Results with reference substance:
- Degradation degree of the reference substance was >60% after 14 days and therefore met the validity criteria. Degradation degree of the inoculum control was also <60% after 14 days.
- Validity criteria fulfilled:
- yes
- Interpretation of results:
- not readily biodegradable
- Conclusions:
- Under the conditions of this study the test material is not readily biodegradable.
- Executive summary:
The biodegradability of the test material was determined in accordance with the standardised guidelines OECD 301 F, EU Method C.4-D and ISO DIS 9408 under GLP conditions.
The test material was not biodegradable (e.g. BOD >60 % of ThOD) within a 10 day window within the 28 day period, as required by OECD 301 to be considered "readily biodegradable." However, biodegradation continued after 28 day and thus measurements continued to day 39. At day 39, biodegradation ranged from 50 to 60 %. Thus the test material may be considered somewhat biodegradable, but not "ready biodegradable".
Under the conditions of this study the test material is not readily biodegradable.
- Endpoint:
- biodegradation in water: ready biodegradability
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Study conducted on read-across material
- Justification for type of information:
- Read across to Octyltin tris(2-ethylhexylmercaptoacetate) (MOTE) (EC Number 248-227-6 and CAS No 27107-89-7) based on structural similarity and hydrolytical behaviour, see attached justification.
- Reason / purpose for cross-reference:
- read-across source
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- >= 30 - <= 40
- Sampling time:
- 28 d
- Key result
- Parameter:
- % degradation (O2 consumption)
- Value:
- >= 50 - <= 60
- Sampling time:
- 39 d
Referenceopen allclose all
No pre-adapted inoculum used
Test duration (days): 39
Duration of adaptation phase (days): 10
Duration of degradation phase (days): >29
Degradation of the test substance at the end of the ten-day window (% BOD/ThOD): --
Degradation degree of the test substance after 28 days (% BOD/ThOD): 30 -40
Degradation degree of the test substance at the end of the test (% BOD/ThOD): 50 -60
Degree of degradation of the test substance in the abiotic control after 20 days of the test (main study) (% BOD/ThOD): 3*
Reference substance: aniline
Degradation degree of the reference substance after 14 days (% BOD/ThOD): 90 -100
Degradation degree in the inhibition control after 14 days (% BOD/ThOD): 40-50
Remarks: *Increasing BOD values of the abiotic test assay (PC) after 20 days might be due to microbial biodegradative activities. Therefore this assay was validated for a test period of 20 days only. Further abiotic test assays did not show any significant degradation during the usual test period of 28 days.
Description of key information
Read-across to structurally similar substance Octyltin tris(2-ethylhexylmercaptoacetate) (MOTE) (CAS No 27107-89-7)
Under the conditions of this study the test material is not readily biodegradable.
Key value for chemical safety assessment
- Biodegradation in water:
- under test conditions no biodegradation observed
Additional information
Read-across to structurally similar substance Octyltin tris(2-ethylhexylmercaptoacetate) (MOTE).
The biodegradability of the test material was determined in accordance with the standardised guidelines OECD 301 F, EU Method C.4-D and ISO DIS 9408 under GLP conditions. The study was awarded a reliability score of 1 in accordance with the criteria set forth by Klimisch et al. (1997).
The test material was not biodegradable (e.g. BOD >60 % of ThOD) within a 10 day window within the 28 day period, as required by OECD 301 to be considered "readily biodegradable." However, biodegradation continued after 28 day and thus measurements continued to day 39. At day 39, biodegradation ranged from 50 to 60 %. Thus the test material may be considered somewhat biodegradable, but not "ready biodegradable".
Under the conditions of this study the test material is not readily biodegradable.
The Baumann, 1992, study is presented as supporting information only. The percentage biodegradation results of the study were as follows: 11.7 mg/L test material = 40 % in 28 days and 22.7 mg/L test material = 28 % in 28 days. Based upon these results it is considered that the test material does not meet the EU criteria for classification as a readily biodegradable substance.
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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