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EC number: 484-470-6 | CAS number: 623-40-5
- 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
- Reliability:
- 1 (reliable without restriction)
- Rationale for reliability incl. deficiencies:
- other: OECD guideline study conducted under GLP
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- GLP compliance:
- yes (incl. QA statement)
- Specific details on test material used for the study:
- Details on properties of test surrogate or analogue material (migrated information):
As noted in the hydrolysis section, oximesilanes quicky hydrolyze to the corresponding oxime and reactive silanols which spontaneously cross link to form high molecular weight silicone polymers. The relevant hydrolysis product is MPKO, the substance that was tested.
Data on selected oximes and oxime silanes are summarized in the attached Table. Although data for each endpoint is not available for all products, the available data show similarities between oxime silanes and their hydrolysis products (oxime). These materials show low toxicity to fish, and daphnia. For algal studies, the toxicity shows a structure activity relationship. The smaller oximes are more toxic to alga, the larger oximes and associated oxime silanes are less toxic. The similarities in response between the oximes and oxime silanes provide additional support of the silicone containing moieties do not contribute to the aquatic toxicity of these materials. Due to the rapid hydrolysis, it is appropriate to use the oxime as surrogate data for t he oxime silane. - Analytical monitoring:
- yes
- Details on sampling:
- The concentrations of methyl propyl ketoxime in the test solutions were measured at 0 and 48 hours using a high performance liquid chromatography with an UV/visible detector
- Vehicle:
- no
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method:
A primary stock concentrate of methyl propyl ketoxime, with a nominal concentration of 100 mg/l, was prepared by adding a nominal 0.1 g of test substance to 1 litre of dilution water. The concentrate was then inverted and stirred for 10 minutes. The resultant stock was observed to be clear and colourless. - Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna
- Source: continuous laboratory cultures held at the laboratory
- Age at study initiation (mean and range, SD): < 24 hours
- Feeding during test - No
Laboratory culture:
- conditions (same as test or not): same
- Type and amount of food: mixed algae diet of Chlorella vulgaris, strain CCAP 211/12 and Pseudokirchneriella subcapitata, strain ATCC 22662; ad libitum
- Feeding frequency: fed daily - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 48 h
- Post exposure observation period:
- none
- Test temperature:
- 20 +/- 1°C
- pH:
- 7.87 to 7.97
- Dissolved oxygen:
- 9.2 mg/l for both control and test article vessels
- Nominal and measured concentrations:
- Measured concentrations within 95% of nomimal (98% average). Results reported as nominal values
- Details on test conditions:
- TEST SYSTEM
- Test vessel: Glass beakers of 250 ml nominal capacity
- Fill volume: 200ml
- 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
- Culture medium different from test medium: no
- Intervals of water quality measurement: time 0 and 48 hours
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod:16 hours light:8 hours dark, with 20 minute dusk and dawn transition periods
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) : at 24 and 48 hours, daphnia were observed by eye for 15 seconds to determine movement and overt signs of toxicity
TEST CONCENTRATIONS
- limit test - 100 mg/l - Duration:
- 48 h
- Dose descriptor:
- NOEC
- Effect conc.:
- >= 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 100 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Behavioural abnormalities: none
- Other adverse effects control: 1 of 20 were immobile at 48hrs
- Abnormal responses: none observed - Reported statistics and error estimates:
- None needed - no immobilization was observed
- Validity criteria fulfilled:
- yes
- Remarks:
- Please refer to Table 1 at "Any other information on results incl. tables"
- Conclusions:
- MPKO is not toxic to daphnia. No immobilization was observed in daphnia exposed to 100 mg/l MPKO.
Reference
Table 1: Validity criteria for OECD 202.
Criterion from the guideline |
Outcome |
Validity criterion fulfilled |
In the control, including the control containing the solubilising agent, not more than 10% of the daphnids should have been immobilized. |
0% |
yes |
The dissolved oxygen concentration at the end of the test should be ≥ 3 mg/L in control and test vessels. |
9.2 mg/L |
yes |
Description of key information
EC50 (48 h) >100 mg/L (nominal, OECD 202).
Key value for chemical safety assessment
Additional information
One study investigating the acute toxicity of 2-Pentanone oxime to aquatic invertebrates is available. The study was performed according to OECD guideline 202 as a limit test (GLP). Daphnia magna were exposed to a limit concentration of 100 mg/L for 48 hours. The substance concentration was analytically verified by HPLC. The measured test substance concentrations were within 98% (average) of the nominal value. Immobilisation of the Daphnids was not observed. Thus, the determined EC50 (48 h) was >100 mg/L (nominal).
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