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EC number: - | CAS number: 2156594-77-1
- 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:
- 30 Nov 2015 to 2 Feb 2016
- 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 (Carbon and Ammonium Oxidation))
- Version / remarks:
- 2010
- Qualifier:
- according to guideline
- Guideline:
- EU Method C.11 (Biodegradation: Activated Sludge Respiration Inhibition Test)
- Version / remarks:
- 2008
- Principles of method if other than guideline:
- Because the test substance solution in the test vessel were foaming during aeration 25 μL/test vessel of Triisobutylphosphate was added to all test vessels.
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- - Name of test material (as cited in study report): Fatty acids, C12-14, a-sulfo, disodium salts
- Batch No.: Ra-He 2014-054
- Purity: 100 % UVCB
- Identity: confirmed by NMR, IR and UV spectroscopies
- Homogeneity: Homogeneous
- Expiry date: Oct 2016
- Date of production: Oct 2014
- Physical state/apperance: Solid / beige
- Storage conditions: Ambient at room temperature - Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- The test substance was weighed in the required amounts for the test concentrations directly to the test vessels.
- Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- - Origin: aeration tank of the wastewater treatment plant of Mannheim, Germany. Sludge was collected at 20 Jan 2016 and arrived in the test facility on the same date.
- Preparation of inoculum for exposure: After arrival of the activated sludge suspension in the test facility the suspension was sieved with a fine woven mesh (mesh size about 1 mm). This suspension was pre-aerated over night at room temperature. At the next day the sludge suspension was washed once with drinking water and the suspension was adjusted to 3 g/L Dw. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 3 h
- Test temperature:
- 19.8 - 20.5 °C
- pH:
- 7.1 - 7.9
- Dissolved oxygen:
- - Dissolved O2 at start of the test: 5.5 - 9.2 mg/L
- Dissolved O2 at termination of the test: 0.9 - 8.9 mg/L - Nominal and measured concentrations:
- - Nominal concentrations: 0 (control), 62.5, 125, 250, 500 and 1000 mg/L (based on test guidelines)
- Test concentrations were not analytically verified. - Details on test conditions:
- TEST SYSTEM
- Test vessel: Glas-beakers (nominal volume 1L)
- Volume: 500 mL, 16 mL/test vessel of 100-fold concentrated OECD medium
- Aeration: Yes
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
- No. of vessels per concentrations of the reference substance (replicates): 2
- Sludge concentration in the test vessel: 1.5 g/L (dry weight)
PREPARATION OF TEST
The test substance was added in the required amounts according to the test concentrations directly to the test vessels with 234 mL deionized water. Aliquots of the reference substance stock solution were dosed to the test vessels and made up with deionized water to a volume of 234 mL. 16 mL synthetic medium were dosed to each test vessel with test substance and reference substance afterwards. To prepare the blank control assays 234 mL of deionized water and 16 mL synthetic medium were mixed. The pH-values in all test vessels were checked and adjusted. After addition of 250 mL of inoculum suspension (3 g/L DW) the incubation was started by aeration of the test vessels with pressured air. The vessels for the blank control assays were prepared to the same procedure without addition of test- or reference substance.
EFFECT PARAMETERS MEASURED: respiration rate (oxygen consumption)
After 3 hours incubation at 20 ± 2°C the mixtures in the test vessels were placed subsequently for oxygen measuring. The temperature was measured for seven times in a separate vessel filled with deionized water. The content of oxygen at the start of the measurements was > 7 mg/L. No abiotic control was tested. The values of oxygen consumption of two test assays were set as outliers and were not used for test result calculation. The oxygen consumption was determined. Duration of the measurement was 8 - 10 minutes with some exceptions (see 'Any other information on materials and methods incl. tables'). Furthermore, the pH was determined. - Reference substance (positive control):
- yes
- Remarks:
- 3,5-dichlorophenol
- Key result
- Duration:
- 3 h
- Dose descriptor:
- EC10
- Effect conc.:
- 260 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks on result:
- other: 95% C.L.: 154.1 - 451.3 mg/L
- Key result
- Duration:
- 3 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Details on results:
- Inhibition of the respiration rate was 1% in the lowest test concentration and increased in a dose-dependent manner up to 41% inhibition at 1000 mg/L. See 'Any other information on results incl. tables'.
- Results with reference substance (positive control):
- The 3-h EC50 value for the reference substance was determined to be 6.8 mg/L. See 'Any other information on results incl. tables'.
- Reported statistics and error estimates:
- The consumption rates were used for the determination of the ECx by the probit method based on Finney (Finney, D.J., Probit Analysis; Cambr. Univ. Press, 3rd ed., 1971) with the software TOXRAT Professional 2.10. The effect concentrations weregiven with an accuracy of 2 significant digits.
- Validity criteria fulfilled:
- yes
- Remarks:
- See 'Any other information on materials and methods incl. tables'
Reference
Table: Measured data of oxygen content of the test assays at the start and end of the evaluation time
Test substance concentration [mg/L] |
0 (mean blank control) |
62.5 |
125 |
250 |
500* |
1000* |
mean O2 conc. Start [mg/L] |
6.7 |
6.4 |
6.8 |
6.4 |
6.6 |
7.0 |
mean O2 conc. End [mg/L] |
1.6 |
1.8 |
2.0 |
1.5 |
2.4 |
3.9 |
mean O2 consumption rate [mg/L] |
5.2 |
5.4 |
6.0 |
6.2 |
6.2 |
6.0 |
mean O2 consumption in minutes |
6.0 |
4.5 |
4.8 |
4.9 |
4.3 |
3.1 |
mean O2 consumption rate [mg/L*h], RT |
51.5 |
51.0 |
47.7 |
48.0 |
41.5 |
30.5 |
mean specific O2 consumption rate [mg/g*h] |
34.5
|
34.0 |
31.7 |
32.0 |
27.5 |
20.5 |
Calculation of mean inhibition respiration [%], IT |
|
1.0 |
7.7 |
7.0 |
19.0 |
41.0 |
IT= inhibition of the total respiration [%]
RT = oxygen consumption in the test assay [mg O2/L×h]
* The result of one of three test vessels was identified as outlier and not included in the calculation.
Table: Measured data of oxygen content of the reference subsstance
Reference substance concentration [mg/L] |
1 |
10 |
100 |
Mean O2 conc. Start [mg/L] |
6.85 |
8.65 |
9.1 |
Mean O2 conc. End [mg/L] |
2.2 |
6.65 |
8.75 |
Mean O2 consumption rate [mg/L] |
4.65 |
2 |
0.35 |
Mean O2 consumption in minutes |
6 |
6 |
5.75 |
Mean O2 consumption rate [mg/L*h], RT |
46.5 |
20 |
3.5 |
Mean specific O2 consumption rate [mg/g*h] |
31 |
13 |
2.5 |
Calculation of mean inhibition respiration [%], IT |
10 |
61 |
93 |
IT= inhibition of the total respiration [%]
RT = oxygen consumption in the test assay [mg O2/L×h]
ADDITIONAL TEST RESULTS TEST SUBSTANCE
- EC20: 680 mg/L
- EC80: >1000 mg/L
- EC90: 2600 mg/L
Description of key information
A key and a supporting study ae available:
In a key study according to OECD 209, the 3-h EC50 and 3-h EC10 values are 1000 and 260 mg/L, respectively, as observed in a respiration inhibition study with activated sludge of a predominantly domestic sewage.
In a supporting study according to OECD 209 the test substance, Fatty acids, C12-14, a-sulfo, disodium salts promoted the respiration rate of activated sewage sludge. No inhibition was observed. The EC50 of 3h respiration inhibition test was higher than 1000mg/L and the NOEC was not lower than 1000mg/L.
Key value for chemical safety assessment
- EC50 for microorganisms:
- 1 000 mg/L
- EC10 or NOEC for microorganisms:
- 260 mg/L
Additional information
The toxicity of the substance to microorganisms was investigated in an activated sludge respiration inhibition study according to OECD TG 209 and in compliance with GLP criteria. In this study activated sludge from a municipal wastewater treatment plant was exposed to nominal test substance concentrations of 0 (control), 62.5, 125, 250, 500 and 1000 mg/L for 3 hours. Test concentrations were not analytically verified. Oxygen consumption was measured over a period of 8 -10 minutes. The respiration rate was calculated using the measured oxygen consumption and compared to an unexposed control. Inhibition of the respiration rate was 1% in the lowest test concentration and increased in a dose-dependent manner up to 41% inhibition at 1000 mg/L. Based on these results, 3-h EC50 and EC10 values of > 1000 mg/L and 260 mg/L were derived, respectively.
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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