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EC number: 828-229-9 | CAS number: 7019-19-4
- 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
Link to relevant study record(s)
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Study period:
- Sept 2018
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- guideline study
- Justification for type of information:
- This is a Klimisch 1 rated OECD 202 study conducted on the registered substance according to GLP
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- Deviations:
- no
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Batch/Lot number: 1203/16/100
- Analytical monitoring:
- yes
- Details on sampling:
- Two samples of 6 mL were taken from both additional vessels (without test organisms in order to not disturb the TOC analysis) of treatment A, C, E and NC after 0 h, 24 h and 48 h exposure for TOC analysis. Of these 4 samples per treatment and sampling time, 2 were analysed directly after sampling and 2 were stored as retain samples in the freezer (≤ -18 °C) until finalisation of the study. For treatment C at 48 h, the two retain samples were measured, including the corresponding NC samples, because the wrong calibration curve was used for the first two samples which resulted in implausible data.
- Vehicle:
- no
- Details on test solutions:
- The stock solution was prepared by adding 99.5 mg test item to 1000 mL test medium and shaking for 0.5 h using an overhead shaker. This stock solution was used as highest test item concentration in the test.
Four replicates, with five daphnids each, were prepared for each test item treatment and the negative control (NC; test medium).
The further test item concentrations were prepared by diluting the stock solution with test medium according to the following scheme (dilution factor of 2):
Treatment Group NC A B C D E
Nominal test item concentration [mg/L]* 0 6.25 12.5 25 50 100
Stock solution [mL] 0 15.6 31.3 62.5 125 250
Test medium [mL] 250 234.4 218.7 187.5 125 0
Test vessels (replicates) 4 4 4 4 4 4
Test Solution/Test Medium [mL] 20 20 20 20 20 20
Additional Vessels for TOC analysis 2 2 - 2 - 2
Test Solution/Test Medium [mL] 40 40 - 40 - 40
"*Due to weighting tolerance and measuring inaccuracy of the analytical balance, the nominal test item concentrations
can deviate < 2 % from the target values." - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- The test organism Daphnia magna Straus originates from the clone breeding of the Federal Environment Agency, department IV 2.4, Berlin, and has been cultivated at Hydrotox GmbH since October 2012. The daphnids are cultured at 20 ± 2 °C with 16 h light : 8 h dark and placed into fresh Elendt M4 medium twice a week. They are kept at approx. 10 animals / 200 mL and fed on workdays with Desmodesmus subspicatus algae corresponding to 0.1 mg C × daphnid-1 × day-1. The test organisms used were 0.5 – 23 h old at the start of the test.
Quality assurance takes place at regular intervals by testing the sensitivity of the test organisms to the reference item potassium dichromate (Sigma, Steinheim, Germany; Lot no.: MKBF2111V). The recent quality testing was performed in April 2018 with EC50 (24h) = 1.8 mg/L (CL 95 %: 1.64 –2.02 mg/L), which is in the declared range of 0.6 – 2.1 mg/L (24 h) according to OECD 202. - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Test temperature:
- 20.0 – 21.2 °C
- pH:
- The pH was 7.7 – 8.1 in the control and 7.7 – 8.4 in the test item treatments (i.e. within recommended range of 6 –9)
- Dissolved oxygen:
- The dissolved oxygen concentration was 8.0 – 8.2 mg/L in the control and 8.0 – 8.3 mg/L in the test item treatment (i.e. meets requirements of ≥ 3 mg/L)
- Nominal and measured concentrations:
- Nominal Concentrations: 0; 6.25; 12.5; 25; 50; 100 mg/L
Geometric Mean Measured Concentrations (0h, 24h and 48h): X; 5.75; X; 23.88; X; 97.9 mg/L (only 3 out of 5 concentration series was subjected to TOC analysis)
The measured TOC concentrations in the test item treatments were 86.2 – 100.2 % of the nominal TOC concentrations - Details on test conditions:
- The test vessels are kept in an incubator (specified temperature 18 – 22 °C, constant within ± 1 °C) with 16 h light : 8 h dark. The pH and the O2-concentrations were measured at the start (0 h) and at the end of the test (48 h). The temperature was measured continuously.
- Key result
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 39.08 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Remarks:
- Immobilisation
- Duration:
- 48 h
- Dose descriptor:
- EC10
- Effect conc.:
- 23.5 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Remarks:
- Immobilisation
- Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- 12.5 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mortality
- Remarks:
- Immobilisation
- Details on results:
- The measured TOC concentrations in the test item treatments were 86.2 – 100.2 % of the nominal TOC concentrations.
As the measured test item concentrations are within ± 20 % of the nominal concentrations, according to OECD 202 (2004), all results are given in relation to the nominal test item concentrations. - Reported statistics and error estimates:
- See results table for 95% Confidence Limits on 48h EC50 and EC10 values
- Validity criteria fulfilled:
- yes
- Conclusions:
- The acute 48h EC50 value for invertebrates (daphnia magna) exposed to 1-hydroxyoctan-2-one was determined to be 39.1 mg/L (nominal).
As the measured test item concentrations are within ± 20 % of the nominal concentrations, according to OECD 202 (2004), all results are given in relation to the nominal test item concentrations. - Executive summary:
The acute toxicity of 1 -hydroxyoctan-2 -one towards the aquatic invertebrate daphna magna was investigated in an OECD 202 guideline study conducted in accordance with GLP including TOC chemical analysis to confirm exposure concentrations (Klimish 1).
The acute 48h EC50 value for invertebrates (daphnia magna) exposed to 1-hydroxyoctan-2-one was determined to be 39.1 mg/L (nominal). As the measured test item concentrations are within ± 20 % of the nominal concentrations, according to OECD 202 (2004), all results are given in relation to the nominal test item concentrations.
Reference
Nominal test item conc [mg/L] | Daphnia Introduced | Immobile Daphnia (replicates 1-4) | Immobility [%] | |||||||||||
0h | 24h | 48h | 24h | 48h | ||||||||||
1 | 2 | 3 | 4 | 1 | 2 | 3 | 4 | 1 | 2 | 3 | 4 | |||
NC | 5 | 5 | 5 | 5 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
6.25 | 5 | 5 | 5 | 5 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
12.5 | 5 | 5 | 5 | 5 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 |
25 | 5 | 5 | 5 | 5 | 0 | 0 | 0 | 0 | 0 | 1 | 1 | 1 | 0 | 15 |
50 | 5 | 5 | 5 | 5 | 0 | 1 | 1 | 0 | 4 | 3 | 4 | 3 | 10 | 70 |
100 | 5 | 5 | 5 | 5 | 5 | 5 | 5 | 5 | 5 | 5 | 5 | 5 | 100 | 100 |
Parameter |
Nominal test item concentration [mg/L] | |
24h | 48h | |
EC50 | 58.22 | 39.08 |
95% CL | n.d | 32.5-47.0 |
EC10 | 50 | 23.5 |
95% CL | n.d | 15.9-28.9 |
LOEC | 50 | 25 |
NOEC | 25 | 12.5 |
Description of key information
The acute toxicity of 1 -hydroxyoctan-2 -one towards the aquatic invertebrate daphna magna was investigated in an OECD 202 guideline study conducted in accordance with GLP including TOC chemical analysis to confirm exposure concentrations (Klimish 1).
The acute 48h EC50 value for invertebrates (daphnia magna) exposed to 1-hydroxyoctan-2-one was determined to be 39.1 mg/L (nominal). As the measured test item concentrations are within ± 20 % of the nominal concentrations, according to OECD 202 (2004), all results are given in relation to the nominal test item concentrations.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 39.1 mg/L
Additional information
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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