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EC number: 500-066-5 | CAS number: 28961-43-5 1 - 6.5 moles ethoxylated
- 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:
- 2010-04-26 to 2010-04-27
- 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:
- yes
- Remarks:
- In contrast to the guideline, it was decided to use copper (II) suphate pentahydrate instead of the prescribed 3,5-dichlorophenol. The usage of dichlorophenol is unsuitable for routine lab use.
- GLP compliance:
- yes
- Analytical monitoring:
- no
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: Directly weighing, stirring for 24 hours
- Eluate: Synthetic waste water acc. to OECD 209
- Differential loading: 100 - 180 - 320 - 580 - 1000 mg/L
- Controls: 2 control samples without test item were included, one at the beginning and one at the end of the test. - Test organisms (species):
- activated sludge
- Details on inoculum:
- - Preparation of inoculum for exposure: Non adapted activated sludge from the sewage plant at Sarstedt (Municipal sewage treatment plant of 31157 Sarstedt, Germany)
- Pretreatment: Washed twice with autoclaved tap water and adjusted to a dry weight concentration of 4.0 g/L +/- 10 %
- Dry sludge concentration: 4.12 g/L - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 3 h
- Hardness:
- Not determined
- Test temperature:
- 20.8 °C
- pH:
- 6.72
- Salinity:
- Not determined
- Details on test conditions:
- TEST SYSTEM
- Test vessel: 500 mL Erlenmeyer flask, DIN 12380
- Aeration: Permanent
- No. of vessels per concentration (replicates): 1
- No. of vessels per control (replicates): 2
- Composition of test medium: 200 mL inoculum + 16 mL synthetic waste water (acc. to the guideline) + 284 mL autoclaved tap water + test substance concentration (directly weighing of 500 mg)
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
Determination of respiration rates subsequently to an incubation period of 3 h
TEST CONCENTRATIONS
- Range finding study
Inhibitions in the Preliminary Test
Nominal Test Item
Concentration [mg/L] Inhibition*[%]
10 -1
100 6
1000 43 - Reference substance (positive control):
- yes
- Remarks:
- Copper (II) sulphate pentahydrate p.a.
- Key result
- Duration:
- 3 h
- Dose descriptor:
- other: EC20
- Effect conc.:
- 292 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- inhibition of total respiration
- Remarks:
- respiration rate
- Details on results:
- - Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: None
- Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- Relevant effect levels: EC50: 115 mg/L - Reported statistics and error estimates:
- The EC20-value of the test item was calculated by sigmoidal dose-response regression using software GraphPad Prism4, GRAPHPAD SOFTWARE, INC. The EC50 and EC80-values could not be determined since these values were outside the tested concentration range.
The EC50-value of the reference item was calculated by probit analysis using software SIGMAPLOT (Windows), SPSS CORPORATION. Probit values were taken from WEBER (1986). - Validity criteria fulfilled:
- yes
- Conclusions:
- The test item is not toxic at concentrations = 292 mg/L to activated sludge of a municipal sewage treatment plant.
- Executive summary:
A Respiration Inhibition Test according to OECD Guideline No. 209 was performed with the test item. The test was performed under static conditions with the nominal concentrations 100 - 180 - 320 - 580 - 1000 mg/L. The respiration rates of control, reference and test item concentrations were measured after a contact time of three hours, and the inhibitory effects of the test and reference item were determined in comparison to the control respiration rates. The inhibition ranged from 6 % to 46 %. The EC20 value is given in Table 1, due to the low inhibitions, the EC50- and EC80-values of the test item could not be calculated (Table 1).
Table 1: EC-Values with Confidence Interval of the test item
EC-values
Confidence interval
[mg/L]
P = 95 [%]
[mg/L]
EC20
292
-
EC50
> 1000
n.d.
EC80
> 1000
-
n.d. = not determinable
In order to check the activity of the test system and the test conditions a reference test was carried out with copper (II) sulphate pentahydrate as reference item and the reference toxicity was determined. The EC50-value for the reference item was 115 mg/L.
Validity criteria of the test guideline were fulfilled.
Reference
From the oxygen depletion the respiration rates were calculated in mgO2/(L×h).
The inhibition of the respiration rates from the test and reference item concentrations in % was calculated in comparison with the respiration rates from the control.
Respiration Rates and Inhibition of Respiration of Test and Reference Item Concentrations
Concentration |
Respiration rate |
Inhibition |
|||||
[mg/L] |
[mgO2/(L×h)] |
[%] |
|||||
Test item |
1000 |
17.6 |
46 |
||||
580 |
21.2 |
35 |
|||||
320 |
25.6 |
21 |
|||||
180 |
27.6 |
15 |
|||||
100 |
30.4 |
6 |
|||||
Control 1 |
– |
32.0 |
– |
||||
Control 2 |
– |
32.8 |
– |
||||
Reference item |
180 |
10.8 |
67 |
||||
100 |
18.4 |
43 |
|||||
58 |
23.6 |
27 |
EC-Values with Confidence Interval of the test item
EC-values |
Confidence interval |
|
[mg/L] |
P = 95 [%] [mg/L] |
|
EC20 |
292 |
- |
EC50 |
> 1000 |
n.d. |
EC80 |
> 1000 |
- |
Raw Data and Respiration Rates of Test Item, Control and Reference Item
Concentration |
Oxygen-concentration* |
Measured distance** |
Respiration rate |
|
[mg/L] |
[mgO2/L] |
[mm/3 min] |
[mgO2/(L×h)] |
|
Test item |
1000 |
9.04 |
44 |
17.6 |
580 |
7.92 |
53 |
21.2 |
|
320 |
6.89 |
64 |
25.6 |
|
180 |
6.67 |
69 |
27.6 |
|
100 |
6.53 |
76 |
30.4 |
|
Control 1 |
– |
5.62 |
80 |
32.0 |
Control 2 |
– |
6.95 |
82 |
32.8 |
Reference item |
180 |
8.66 |
27 |
10.8 |
100 |
7.16 |
46 |
18.4 |
|
58 |
6.60 |
59 |
23.6 |
Description of key information
Toxicity to microorganisms - OECD 209 – EC20: 292 mg/l, EC50: >1000 mg/l, 3h - PARAD consortium, NOACK, 2010)
Key value for chemical safety assessment
- EC50 for microorganisms:
- 1 000 mg/L
Additional information
Toxicity to microorganisms - OECD 209 – EC20: 292 mg/l,EC50: >1000 mg/l, 3h - PARAD consortium, NOACK, 2010, S. Fiebig)
A Respiration Inhibition Test according to OECD Guideline No. 209 was performed with the test item Photomer 4149 F (batch-no. S700040031) from 2010-04-26 to 2010-04-27 at Dr.U.Noack-Laboratorien, D-31157 Sarstedt.
Test system was activated sludge of the municipal treatment plant of D-31157 Sarstedt. The test was performed under static conditions with the nominal concentrations 100 - 180 - 320 - 580 - 1000 mg/L. The respiration rates of control, reference and test item concentrations were measured after a contact time of three hours, and the inhibitory effects of the test and reference item were determined in comparison to the control respiration rates. The inhibition ranged from 6 % to 46 %. Due to the low inhibitions, the EC50- and EC80-values of the test item could not be calculated. The EC20 was determined to be EC20: 292 mg/l, whereas the EC50 was determined to be EC50: >1000 mg/l.
Evaluation: valid without restrictions, Klimisch-I , Key study
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