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EC number: 222-613-4 | CAS number: 3555-47-3
- 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
Toxicity to microorganisms
Administrative data
Link to relevant study record(s)
- Endpoint:
- activated sludge respiration inhibition testing
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 09 February 2012 - 09 February 2012
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 209 (Activated Sludge, Respiration Inhibition Test
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.11 (Biodegradation: Activated Sludge Respiration Inhibition Test)
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- ISO 8192 (Water quality - Test for inhibition of oxygen consumption by activated sludge for carbonaceous and ammonium oxidation)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- Silsequioxanes, phenyl (tested as received) was a clear colourless liquid that was not completely soluble in test medium at the loading rates initially prepared. Therefore, 1-Litre test bottles were filled with 200 ml of test substance mixtures in Milli-RO water (tap water purified by reverse osmosis; Millipore Corp., Bedford, Mass., USA) with initial loading rates of 2.5 times the final loading rate. These mixtures were stirred in closed dark brown bottles for 23½ hours, except in the abiotic control (25½ hours). Subsequently, 16 ml synthetic sewage feed, 250 ml sludge and Milli-RO water up to 500 ml were added resulting in the required loading rates. Optimal contact between the test substance and test organisms was ensured applying continuous aeration and stirring.
- Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- The sludge was coarsely sieved, washed and diluted with ISO-medium. A small amount of the sludge was weighed and dried overnight at ca. 105°C to determine the amount of suspended solids (3.0 g/l of sludge, as used for the test). The pH was 7.4 on the day of testing. The batch of sludge was used one day after collection; therefore 50 ml of synthetic sewage feed was added per litre of activated sludge at the end of the collection day. The sludge was kept aerated at test temperature until use.
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 3 h
- Post exposure observation period:
- After the 3-hour contact time, the oxygen consumption was recorded for a period of approximately 10 minutes. During measurement, the sample was not aerated but continuously stirred on a magnetic stirrer. The pH and temperature were determined in the remaining part of the reaction mixture.
- Test temperature:
- Between 18.1 and 20.5°C.
- pH:
- Before addition of sludge : 7.6 - 7.7.
After the 3 hour exposure period : 7.5 - 8.3. - Dissolved oxygen:
- The oxygen concentration at the start of measurements was at least 7.0 mg O2/l
Oxygen consumption:
Controls : 48 mg O2/l/h (mean value)
silsequioxanes, phenyl 10 mg/l : 42 mg O2/l/h
silsequioxanes, phenyl 100 mg/l : 49 mg O2/l/h
silsequioxanes, phenyl 1000 mg/l : 51 mg O2/l/h (mean value) - Nominal and measured concentrations:
- Nominal loading rates: 10, 100 and 1000 mg/l.
- Details on test conditions:
- TEST SYSTEM
- Type: open
- Material, size, headspace, fill volume: All glass
- Aeration: During exposure with clean, oil-free air
- No. of vessels per concentration (replicates): 1 for 10 and 100 mg/l and 3 for 1000 mg/l
- No. of vessels per control (replicates): 2
- Biomass loading rate: 1.5 g/l suspended solids in final test mixture
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: Tap-water purified by reverse osmosis (Milli-RO
EFFECT PARAMETERS MEASURED (with observation intervals if applicable): The respiration rate from each vessel, in mg O2/l/hr, was calculated from the linear part of the respiration curve, which was generally between 2 and 7 mg O2/l.
TEST CONCENTRATIONS
- Test concentrations: combined limit/range-finding test: at 10, 100 and 1000 mg/l (loading rates). - Reference substance (positive control):
- yes
- Remarks:
- 3,5-dichlorophenol
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- (loading rate)
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Remarks:
- (loading rate)
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Details on results:
- In the combined limit/range-finding test no inhibition of the respiration rate of the sludge was recorded at the highest loading rate tested, 1000 mg silsequioxanes, phenyl per litre.
There was no oxygen uptake from abiotic processes and the results at 1000 mg/l with a nitrification inhibitor showed that the heterotrophic inhibition of the respiration rate was comparable to the total inhibition. - Results with reference substance (positive control):
- The EC50 of 3,5-dichlorophenol was in the accepted range of 2 to 25 mg/l for total respiration (4.0 mg/l).
- Reported statistics and error estimates:
- ECx
For the reference substance the percentage inhibition was plotted against the logarithm of the concentrations and the EC50 was determined using linear regression analysis.
For silsequioxanes, phenyl no EC50 could be calculated because the test substance proved to be non-toxic (EC50 > a loading rate of 1000 mg/l).
NOEC estimation
Since no inhibition of the respiration rate was observed at the highest loading rate tested, no statistical analysis of the data was performed. - Validity criteria fulfilled:
- yes
- Conclusions:
- Under the conditions of this present test silsequioxanes, phenyl was not toxic to waste water (activated sludge) bacteria up to and including a loading rate of 1000 mg/l (NOEC).
The EC50 exceeded a loading rate of 1000 mg/l.
Reference
Description of key information
Toxicity to microorganisms: 3-hour EC50 >1000 mg/l; NOEC >=1000 mg/l (OECD 209), read-across from phenyl silsesquioxanes ( EC 939-487-8).
Key value for chemical safety assessment
Additional information
There are no microorganism toxicity data available for 1,1,1,5,5,5-hexamethyl-3,3-bis[(trimethylsilyl)oxy]trisiloxane (M4Q, CAS 3555-47-3).
A category approach is applied to this endpoint and is detailed in the Siloxane Category report (PFA, 2017at). The hypothesis for read-across is that siloxane substances exhibit no evidence of significant toxicity to sewage treatment plant microorganisms. This is consistent with a non-polar narcosis mode of action. Therefore, good quality data for the structurally-related substance phenyl silsesquioxanes (EC 939-487-8), have been read across to M4Q.
M4Q and phenyl silsesquioxanes are members of the Reconsile Siloxanes Category within which, in general, the substances exhibit no evidence of significant toxicity to microorganisms.
The table below presents microorganism toxicity data available for substances within the Siloxanes Category.
It is therefore considered valid to read-across the results for phenyl silsesquioxanes to fill the data gap for the registered substance.
Microorganism toxicity data available for substances within the Siloxanes Category
CAS |
Name |
Result: E(I)C50(mg/l) |
Result: NOEC (or EC10/ EC20) (mg/l) |
Guideline Number |
Test method |
Duration (h) |
Reliability |
540-97-6 |
Dodecamethylcyclohexasiloxane |
>100 mg/l |
|
OECD 209 |
ASRI |
3 |
1 |
541-05-9 |
Hexamethylcyclotrisiloxane |
>100 mg/l |
>100 mg/l |
OECD 209 |
ASRI |
3 |
1 |
541-02-6 |
Decamethylcyclopentasiloxane |
>2000 mg/l |
|
C11 |
ASRI |
3 |
1 |
107-46-0 |
Hexamethyldisiloxane |
>>100 |
≥100 |
OECD 209 |
ASRI |
3 |
1 |
141-62-8 |
Decamethyltetrasiloxane |
>100 mg/l |
|
OECD 209 |
ASRI |
3 |
1 |
352230-22-9 |
Siloxanes and Silicones, di-Ph, Ph (trimethylsilyl)oxy |
>1000 mg/l |
≥1000 mg/l |
OECD 209 |
ASRI |
3 |
1 |
2627-95-4 |
1,1,3,3-tetramethyl-1,3-divinyldisiloxane |
>1000 mg/l |
≥1000 mg/l |
OECD 209 |
ASRI |
3 |
1 |
2554-06-5 |
2,4,6,8-tetramethyl-2,4,6,8-tetravinylcyclotetrasiloxane |
>1000 mg/l |
≥1000 mg/l |
OECD 209 |
ASRI |
3 |
1 |
N/A (EC 939-487-8) |
phenyl silsesquioxanes |
>1000 |
≥1000 |
OECD 209 |
ASRI |
3 |
1 |
99363-37-8 |
dimethyl, methyl(3-aminopropyl) siloxane, trimethylsiloxy-terminated |
> water soluble fraction |
≥ water soluble fraction |
OECD 209 |
ASRI |
3 |
1 |
71750-79-3 |
dimethyl, (aminoethylaminopropyl)methyl siloxane, trimethylsiloxy-terminated |
> water soluble fraction |
≥ water soluble fraction |
OECD 209 |
ASRI |
3 |
1 |
Additional information is given in a supporting report (PFA, 2017) attached in Section 13 of the IUCLID dossier.
Under the conditions of this present test, phenyl silsesquioxanes was not toxic to waste water (activated sludge) bacteria up to and including a loading rate of 1000 mg/l (NOEC).
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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