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EC number: 952-655-5 | 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
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:
- weight of evidence
- Study period:
- 17 Oct 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
- GLP compliance:
- yes (incl. QA statement)
- Remarks:
- Landesanstalt für Umwelt, Messungen und Naturschutz Baden-Württemberg, Karlsruhe, Germany
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION
- Method: 586 µl of the test item were added into the test vessels to obtain final concentrations of 1000 mg/L. Three parallel vessels of the test item were prepared.
- Eluate: no
- Differential loading: yes
- Controls: yes, blank control - Test organisms (species):
- activated sludge of a predominantly domestic sewage
- Details on inoculum:
- - Source: Activated sludge from the municipal wastewater treatment plant Staufener Bucht (Germany) was used as test system. The treatment plant clarifies predominantly domestic wastewater of the region of Staufen and has a capacity of 140 000 inhabitant equivalents. Sampling date of activated sludge was 16 Oct 2012.
- Laboratory culture: no
- Preparation of inoculum for exposure: The activated sludge was kept aerated and fed with synthetic sewage (50 mL per litre and day) until use. Dry solids of the activated sludge was determined as 5.3 g/L by weight measurements before and after 3 h drying at 105°C (mean of triplicate measurements). The activated sludge was washed twice by settling the sludge, decanting the supernatant, and re-suspending the sludge in aerated tap water. Before using, the activated sludge was diluted to 3 g/L dry solids with tap water, in order to obtain a final concentration of 1.5 g/L dry solids in the test.
- Initial biomass concentration: 1.5 g/L (dry solids) - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 3 h
- Test temperature:
- 18 - 20 °C
- pH:
- 7.7
- Nominal and measured concentrations:
- nominal: blank, 1000 mg/L
- Details on test conditions:
- TEST SYSTEM
- Test vessel: BOD bottles
- Fill volume: 500 mL
- Aeration: All vessels were stirred and aerated throughout the contact time with room air at a rate of 0.5 - 1 L/min using a membrane pump.
- No. of vessels per concentration (replicates): 3
- No. of vessels per control (replicates): 6
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: according to guideline (demineralised water)
EFFECT PARAMETERS MEASURED: respiration rate was measured every 15 min to allow a contact time of 3 h - Reference substance (positive control):
- yes
- Remarks:
- 3,5-dichlorophenol
- 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
- Remarks:
- respiration rate
- Key result
- Duration:
- 3 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Results with reference substance (positive control):
- - Results with reference substance valid? yes
- Relevant effect levels: EC50 (3 h): 22.48 mg/L. The EC50 was calculated with ToxRat version 2.09 (ToxRat Solutions GmbH, Alsdorf, Germany) by probit analysis using linear max. likelihood regression. - Validity criteria fulfilled:
- yes
- Conclusions:
- The NOEC of dodecyl oleate (CAS No 36078-10-1), a constituent of the registration substance, is >/= 1000 mg/L, the EC50 > 1000 mg/L.
- Executive summary:
The present study with dodecyl oleate (CAS No 36078 -10 -1), constituent of the registration substance, was performed according to OECD 209 under GLP conditions. A limit test with a concentration of 1000 mg/L did not result in inhibition of respiration rate of activated sludge microorganisms (obtained from a sewage treatment plant treating predominantly domestic wastewater). An increase of respiration was observed in all three test vessels. Thus, a NOEC (3 h) of ≥ 1000 mg/L was derived.
- Endpoint:
- toxicity to microorganisms
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Data based on a ready biodegradability study. This approach is in accordance with the Guidance on information requirements and chemical safety assessment (Chapter R.7b: Endpoint specific guidance, ECHA 2008).
- Reason / purpose for cross-reference:
- reference to same study
- Qualifier:
- according to guideline
- Guideline:
- other: OECD Guideline 301 C (Ready Biodegradability: Modified MITI Test (I))
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: Circular on Test Methods of New Chemical Substances (Japan), biodegraadation test
- Deviations:
- no
- GLP compliance:
- yes
- Analytical monitoring:
- yes
- Vehicle:
- no
- Test organisms (species):
- other: mixture of activated sludge from STP with freshwater from rivers and lakes, marine water and marine sediment
- Details on inoculum:
- - Source of inoculum/activated sludge (location, sampling depth): location: 10 sites (4 sewage plants, 3 rivers, 1 lake and 2 bays) around Japan, sampling depth: return sludge in sewage plants, surface water and surface soil of foreshore
- Laboratory culture: Thirty minutes after stopping of aeration, discard about one third of the whole volume of supernatant and add an equal volume of a solution (pH adapted to 7.0 with NaOH) containing 0.1% each of glucose, peptone and potasium orthophosphate, to the settled material and re-commence aeration. This procedure was repeated once per day.
- Temperature: 25 ± 2 °C
- Storage conditions: appearance and general condition of sludge were observed with a light microscope, sediments, pH, temperature and dissolved oxygen
- Storage length: started to use: 15 Oct 1991
- Concentration of sludge: 5500 mg/L
- Water filtered: no - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 28 d
- Test temperature:
- 25 ± 2 °C
- Nominal and measured concentrations:
- nominal: 100 mg/L
- Details on test conditions:
- TEST CONDITIONS
- Composition of medium: recommended medium in the guideline
- Test temperature: 25 ± 1 °C
- Suspended solids concentration: 30 mg/L
- Continuous darkness: no data
TEST SYSTEM
- Culturing apparatus: closed oxygen consumption measuring machine
- Number of culture flasks/concentration: 1 (water + test substance), 3 (sludge + test sub.), 1 (sludge + reference sub.), 1 (sludge)
- Measuring equipment: Coulometer
- Details of trap for CO2 and volatile organics if used: soda lime
SAMPLING
- Sampling frequency: continuously until day 28
- Sterility check if applicable: no
- Sample storage before analysis: no data
CONTROL AND BLANK SYSTEM
- Inoculum blank: Yes - Reference substance (positive control):
- yes
- Remarks:
- aniline
- Key result
- Duration:
- 28 d
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: Result from a ready biodegradability test
- Results with reference substance (positive control):
- The oxygen consumption for aniline in the above used test system reached 58% and 75% degradation after 7 days and 14 days.
- Validity criteria fulfilled:
- yes
- Conclusions:
- The NOEC ot tetra decyl myristate (CAS No 3234-85-3), a constituent of the registration substance, is derived at >/= 100 mg/L (nominal).
- Executive summary:
The toxicity of tetradecyl myristate (CAS 3234-85-3), a constituent of the registration substance, to activated sludge microorganisms was investigated in a biodegradation study conducted according to OECD 301C under GLP conditions (Ministry of Economy, Trade and Industry, Japan, 1992). A test concentration of 100 mg/L (nominal) did not inhibit the biodegradation process of the test substance. Therefore, the test substance is not toxic to activated sludge microorganisms and the test concentration can be used as a NOEC value for the toxicity to activated sludge microorganisms. Thus, a NOEC (28 d) of ≥ 100 mg/L resulted.
Referenceopen allclose all
The validity criteria set out in the Guideline are met.
Table 1: Respiration rate of activated sludge after application of the test substance of the definite test.
Vessel |
O2 concentration [mg/L] |
Consumption rate [mg/(L*h)] |
Inhibition [%] |
|
First measurement |
Last measurement |
|||
Blank 1 |
7.77 |
6.15 |
38.9 |
|
Blank 2 |
7.50 |
6.07 |
34.3 |
|
Blank 3 |
7.88 |
6.66 |
29.3 |
|
Blank 4 |
7.44 |
6.15 |
31.0 |
|
Blank 5 |
7.80 |
6.53 |
30.5 |
|
Blank 6 |
8.59 |
7.77 |
19.7 |
|
Test item 1 |
5.22 |
3.65 |
37.7 |
-23 |
Test item 2 |
5.85 |
4.55 |
31.2 |
-2 |
Test item 3 |
8.09 |
3.75 |
32.2 |
-5 |
Coefficient of variation of blanks: 0.19
The results of a first test with a concentration of 1000 mg/L showed high negative inhibitions (until -53%) and a relative low start value of oxygen at the beginning of the measurement. Therefore, the aeration of the test was optimized and the test was repeated. The data of the first test are not shown in detail in the report. In the repetition the values of oxygen at the start of measurement were considerably higher and the evaluation showed conclusive results.
The test substance was degraded to an extent of 67% (O2 consumption) and 94% (Test material analysis) after 28 d.Since the substance was readily biodegradable it is with high probability not toxic to aquatic microorganisms. The test item concentration in the test vessels of 100 mg/L can be used as NOEC value for the toxicity to aquatic microorganisms.
Description of key information
NOEC (28 d) of ≥ 100 mg/L for activated sludge microorganisms (OECD 301C).
NOEC (3 h) of ≥ 1000 mg/L for activated sludge microorganisms (OECD 209).
Key value for chemical safety assessment
- EC50 for microorganisms:
- 1 000 mg/L
Additional information
Two GLP Guideline studies conducted according to OECD 301 C and 209 are available investigating the effects of tetradecyl myristate (CAS 3234-85-3) and dodecyl oleate (CAS No 36078-10-1), constituents of the registration substance. Microorganisms were exposed to test item concentrations of up to 1000 mg/L (nominal).
1. Result of study with tetradecyl myristate:
A test concentration of 100 mg/L (nominal) did not inhibit the biodegradation process of the test substance. Therefore, the test substance is not toxic to activated sludge microorganisms and the test concentration can be used as a NOEC value for the toxicity to activated sludge microorganisms. Thus, a NOEC (28 d) of ≥ 100 mg/L resulted.
.
2. Result with dodecyl oleate:
A limit test with a concentration of 1000 mg/L did not result in inhibition of respiration rate of activated sludge microorganisms (obtained from a sewage treatment plant treating predominantly domestic wastewater). An increase of respiration was observed in all three test vessels. Thus, a NOEC (3 h) of ≥ 1000 mg/L was derived.
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