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EC number: 212-266-7 | CAS number: 774-55-0
- 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
Short-term toxicity to aquatic invertebrates
Administrative data
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- 29 September 2017 - 01 November 2017
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 2 018
- Report date:
- 2018
Materials and methods
Test guidelineopen allclose all
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Version / remarks:
- 13 April 2004
- Deviations:
- no
- Qualifier:
- according to guideline
- Guideline:
- other: Guidance document on aquatic toxicity testing of difficult substances and mixtures, OECD series on testing and assessment number 23
- Version / remarks:
- 2000
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
Test material
- Reference substance name:
- 1-(5,6,7,8-tetrahydro-2-naphthyl)ethan-1-one
- EC Number:
- 212-266-7
- EC Name:
- 1-(5,6,7,8-tetrahydro-2-naphthyl)ethan-1-one
- Cas Number:
- 774-55-0
- Molecular formula:
- C12H14O
- IUPAC Name:
- 1-(5,6,7,8-tetrahydronaphthalen-2-yl)ethan-1-one
- Test material form:
- liquid
- Details on test material:
- Appearance: Colourless to pale yellow liquid
Constituent 1
- Specific details on test material used for the study:
- - The test item is isoluble in water.
- Specific gravity/density: 1.059 (20ºC) and 1.057 (25ºC)
Sampling and analysis
- Analytical monitoring:
- yes
- Details on sampling:
- Samples were taken from all test concentrations and the control according to the schedule below.
Frequency: at t=0 and t=48 h
Volume: 2.0 mL from the approximate centre of the test vessels
Storage: Samples were stored in a freezer (≤ -15°C) until analysis.
At the end of the exposure period, the replicates were pooled at each concentration before sampling.
Test solutions
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION:
- Method: Direct application to test medium. The test solution was prepared at a loading rate of 100 mg/L applying a 3-day period of stirring to ensure maximum dissolution of the test item in medium. The obtained aqueous mixture was allowed to settle for a period of one hour. Thereafter, the clear and colourless Saturated Solution (SS) was collected by means of siphoning and used as the highest test concentration. Lower test concentrations were prepared by subsequent dilutions of the SS in test medium.
- Controls: test medium without test item or other additives (blank-control)
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna
- Strain: Straus, 1820
- Source: in-house laboratory culture with a known history. At least third generation, obtained by a cyclical parthenogenesis under specified breeding conditions.
- Age of parental stock: Daphnids originated from a healthy stock, 2nd to 5th brood, showing no signs of stress such as mortality >20%, presence of males, ephippia or discoloured animals and there was no delay in the production of the first brood.
- Age at study initiation: < 24 hours, from parental daphnids of more than two weeks old.
- Feeding during test: no
ACCLIMATION
- Acclimation period: no
BREEDING:
- Method: each batch was started with newborn daphnids, i.e. less than 3 days old, by placing about 250 of them into 5 litres of medium (M7) in an all-glass culture vessel. After 7 days of cultivation half of the medium was renewed twice a week.
- Feeding: daily, a suspension of fresh water algae.
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
Test conditions
- Hardness:
- 180 mg CaCO3/L
- Test temperature:
- 19-20 °C (throughout the test)
- pH:
- 7.9-8.1 (throughout the test)
- Dissolved oxygen:
- At the start of the test: 9.6-10 mg O2/L
At the end of the test: 8.8-9.0 mg O2/L - Nominal and measured concentrations:
- Nominal concentrations: 1.0, 2.2, 4.6, 10, 22, 46 and 100% of a saturated solution prepared at a loading rate of 100 mg/L
Measured concentrations: at t=0: 0.906, 2.01, 4.05, 9.09, 20.1, 42.0 and 91.4 mg/L; at t=48: 0.840, 1.91, 3.94, 8.79, 19.3, 40.6 and 88.9 mg/L, respectively to above stated nominal concentrations. - Details on test conditions:
- TEST SYSTEM
- Test vessel: 60 ml, all-glass
- Fill volume: 50 mL
- Aeration: no
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
TEST MEDIUM / WATER PARAMETERS
- Standard medium used: yes, adjusted ISO medium
- Source/preparation of dilution water: tap water purified by reverse osmosis
- Culture medium different from test medium: yes, M7 was used as culture medium
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: 16 hours, daily
EFFECT PARAMETERS MEASURED: mobility at 24 and 48 hours.
- Additional measurements: pH and dissolved oxygen at the beginning, after 24 hours of exposure and at the end of the test, for all concentrations and the control. Temperature of the medium: continuously in a temperature control vessel.
RANGE-FINDING STUDY
- Test concentrations: 0.10, 1.0, 10 and 100% of a saturated solution (SS) prepared at 100 mg/L
- Results used to determine the conditions for the definitive study: yes, after 48 hours of exposure, all daphnids became immobile in the highest concentration, while 20% immobility occurred at a test concentration of 10% of a SS prepared at 100 mg/L. Therefore, the expected EC50 was between 10 and 100% of a SS at 100 mg/L. - Reference substance (positive control):
- yes
- Remarks:
- potassium dichromate (September 2017)
Results and discussion
Effect concentrations
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 12 mg/L
- Nominal / measured:
- meas. (initial)
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Analysis showed that test concentrations remained stable during the exposure concentrations: test concentrations after 48 hours were 93-97% of the initial measured concentrations at t=0 (see table 1). Therefore, effect parameters were based on initial measured concentrations.
- At the end of the exposure concentration, all daphnids in the three highest test solutions were immobile, while no daphnids were immobile in the lowest three test concentrations and 5 and 15% immobility occurred in the 4.1 mg/L and 9.1 mg/L, respectively (see table 2).
- Microscopic observations showed no test item attached to the daphnids.
- The pH and temperature during the study remained within the limits prescribed by the study plan. - Results with reference substance (positive control):
- - Results with reference substance valid? Yes
- Tested concentrations: 0.10, 0.18, 0.32, 0.56, 1.0 and 1.8 mg/L
- 48h-EC50: 0.41 mg/L, 95%-confidence interval: 0.34-0.46 mg/L
- Other: results fell within the historical range. - Reported statistics and error estimates:
- The EC50-values were calculated from the weibits of the percentages affected daphnids and the logarithms of the corresponding test item concentrations (initially measured) using the maximum likelihood estimation method.
ToxRat Professional v 3.2.1 (ToxRat Solutions® GmbH, Germany) was used to perform the analyses.
Any other information on results incl. tables
Table 1 Measured concentrations during the final test
Time of sampling [hours] |
Date of sampling |
Date of analysisa |
Percentage of SSb [%] |
Analyzed concentration [mg/L] |
Relative to initial [%] |
0 |
23 Oct 2017 |
01 Nov 2017 |
0 |
n.d. |
|
|
|
|
1.0 |
0.906 |
|
|
|
|
2.2 |
2.01 |
|
|
|
|
4.6 |
4.05 |
|
|
|
|
10 |
9.09 |
|
|
|
|
22 |
20.1 |
|
|
|
|
46 |
42.0 |
|
|
|
|
100 |
91.4 |
|
48 |
25 Oct 2017 |
01 Nov 2017 |
0 |
n.d. |
n.a. |
|
|
|
1.0 |
0.840 |
93 |
|
|
|
2.2 |
1.91 |
95 |
|
|
|
4.6 |
3.94 |
97 |
|
|
|
10 |
8.79 |
97 |
|
|
|
22 |
19.3 |
96 |
|
|
|
46 |
40.6 |
97 |
|
|
|
100 |
88.9 |
97 |
a Samples were stored in the freezer (≤ -15°C) until the day of analysis.
b Percentage of a saturated solution (SS) prepared at a loading rate of 100 mg/L.
n.d.Not detected.
n.a.Not applicable.
Table 2 Number of Introduced Daphnids and Incidence of Immobility in the Final Test
Time (h) |
Replicate |
Test item initial concentration (mg/L) |
|||||||
Control |
0.91 |
2.0 |
4.1 |
9.1 |
20 |
42 |
91 |
||
0 |
A |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
B |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
|
C |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
|
D |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
5 |
|
Total introduced |
20 |
20 |
20 |
20 |
20 |
20 |
20 |
20 |
|
|
|
||||||||
24 |
A |
0 |
0 |
0 |
0 |
1 |
5# |
5 |
5 |
B |
0 |
0 |
0 |
0 |
1 |
5 |
5 |
5 |
|
C |
0 |
0 |
0 |
0 |
0 |
5 |
5 |
5 |
|
D |
0 |
0 |
0 |
0 |
1 |
5 |
5 |
5 |
|
Total immobilised |
0 |
0 |
0 |
0 |
3 |
20 |
20 |
20 |
|
Effect % |
0 |
0 |
0 |
0 |
15 |
100 |
100 |
100 |
|
|
|
|
|
|
|
|
|
||
48 |
A |
0 |
0 |
0 |
1 |
1 |
5 |
5 |
5 |
B |
0 |
0 |
0 |
0 |
1 |
5 |
5 |
5 |
|
C |
0 |
0 |
0 |
0 |
0 |
5 |
5 |
5 |
|
D |
0 |
0 |
0 |
0 |
1 |
5 |
5 |
5 |
|
Total immobilised |
0 |
0 |
0 |
1 |
3 |
20 |
20 |
20 |
|
Effect % |
0 |
0 |
0 |
5 |
15 |
100 |
100 |
100 |
#Microscopic observation revealed no test item attached to the daphnids
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- In an acute toxicity study, performed according to OECD 202 and GLP principles, the 48-h EC50 of the test substance towards Daphnia magna was determined to be 12 mg/L (based on initial concentrations).
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