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EC number: 907-235-6 | 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
Short-term toxicity to aquatic invertebrates
Administrative data
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Study period:
- test start: 06 Aug. 1990; test end: 08 Aug. 1990
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: Guideline study
Data source
Reference
- Reference Type:
- study report
- Title:
- Unnamed
- Year:
- 1 990
Materials and methods
Test guideline
- Qualifier:
- according to guideline
- Guideline:
- other: 79/831/EEC
- GLP compliance:
- no
Test material
- Reference substance name:
- Undecanal
- EC Number:
- 203-972-6
- EC Name:
- Undecanal
- Cas Number:
- 112-44-7
- Molecular formula:
- C11H22O
- IUPAC Name:
- undecanal
- Details on test material:
- - Name of test material (as cited in study report): undecanal
- Physical state: liquid
- Analytical purity: ca. 65%
- Impurities (identity and concentrations): decane, undecanol, 2- methyl decanal
- Lot/batch No.: product no. 072525, lot no. 5/89
Constituent 1
Sampling and analysis
- Analytical monitoring:
- no
Test solutions
- Vehicle:
- yes
- Details on test solutions:
- PREPARATION AND APPLICATION OF TEST SOLUTION (especially for difficult test substances)
- Method: stock solution: The stock solution (100 mg/L test item) was prepared with Cremophor RH 40. A dilution series was prepared with dilution water. 10 mL of the prepared diluted solutions were added to the test vessels.
- Controls: negative control, solvent control
- Chemical name of vehicle (organic solvent, emulsifier or dispersant): Cremophor RH 40
- Concentration of vehicle in test medium (stock solution and final test solution): stock solution 100 mg/L Cremophor RH 40
- Evidence of undissolved material (e.g. precipitate, surface film, etc): no
Test organisms
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- TEST ORGANISM
- Common name: Daphnia magna Straus
- Source: originally supplied from 'Institut National de Recherche Chimique appliquee, France', and has been bred from 1978 in the Laboratories of BASF
- Age at study initiation (mean and range, SD): 2-26 h
- Feeding during test: no
Study design
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
Test conditions
- Hardness:
- test start: 2.88 mmol/L
- Test temperature:
- 20±1 °C
- pH:
- test start: 7.6 to 8.1
test end: 7.5 to 8.0 - Dissolved oxygen:
- test start: 8.3 to 9.1 mg/L
test end: 6.1 to 9.1 mg/L - Nominal and measured concentrations:
- nominal (test material): 0 (control), 0 (solvent control), 0.78, 1.56, 3.13, 6.25, 12.5, 25, 50, and 100 mg/L
nominal (active ingredient): 0 (control), 0 (solvent control), 0.51, 1.01, 2.03, 4.06, 8.12, 16.25, 32.5, and 65 mg/L - Details on test conditions:
- TEST SYSTEM
- Test vessel: test tubes with flat bottom
- Type (delete if not applicable): open
- Material, size, headspace, fill volume: glas, 20-mL total volume, 10-mL fill volume
- Aeration: no
- No. of organisms per vessel: 5
- No. of vessels per concentration (replicates): 4
- No. of vessels per control (replicates): 4
- No. of vessels per vehicle control (replicates): 4
- Biomass loading rate: 1 animal/2 mL
TEST MEDIUM / WATER PARAMETERS
- Source/preparation of dilution water: according to guideline
- Alkalinity: 0.80 to 1.20 mmol/L
- Ca/mg ratio: 4:1
- Conductivity: 678 µSiemens/cm at test start
- Culture medium different from test medium: no
OTHER TEST CONDITIONS
- Adjustment of pH: no
- Photoperiod: continuous darkness
- Light intensity: not applicable
EFFECT PARAMETERS MEASURED (with observation intervals if applicable) :
- pH and dissolved oxygen: 0 and 48 h
- immobile animals: 0, 3, 6, 24, and 48 h
TEST CONCENTRATIONS
- Spacing factor for test concentrations: 2
- Justification for using less concentrations than requested by guideline: not applicable
- Range finding study
- Test concentrations: no data
- Results used to determine the conditions for the definitive study: no data - Reference substance (positive control):
- no
Results and discussion
Effect concentrationsopen allclose all
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 2.5 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- act. ingr.
- Basis for effect:
- mobility
- Remarks on result:
- other: calculated from purity data
- Duration:
- 48 h
- Dose descriptor:
- EC50
- Effect conc.:
- 3.85 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Behavioural abnormalities: not noted
- Mortality of control: 0%; solent control: 0%
- Abnormal responses: no
- Any observations (e.g. precipitation) that might cause a difference between measured and nominal values: no
- Effect concentrations exceeding solubility of substance in test medium: yes (solvent was used to dissolve test item)
Any other information on results incl. tables
Immobilised animals
Test item conc. |
Immobilised animals after |
|||
(mg/L) |
3 h |
6 h |
24 h |
48 h |
nominal (test material) |
|
|
|
|
0 (control) |
0 |
0 |
0 |
0 |
0 (vehicle control) |
0 |
0 |
0 |
0 |
0.78 |
0 |
0 |
0 |
0 |
1.56 |
0 |
0 |
0 |
0 |
3.13 |
0 |
0 |
0 |
15 |
6.25 |
1 |
1 |
11 |
20 |
12.5 |
2 |
2 |
20 |
20 |
25 |
18 |
19 |
20 |
20 |
50 |
20 |
20 |
20 |
20 |
100 |
20 |
20 |
20 |
20 |
pH and dissolved oxygen
Test item conc. |
pH |
Dissolved oxygen (mg/L) |
||
(mg/L) |
0 h |
48 h |
0 h |
48 h |
0 (control) |
8.1 |
8.0 |
8.5 |
9.5 |
0 (vehicle control) |
8.0 |
7.9 |
8.3 |
8.7 |
0.78 |
8.1 |
8.0 |
9.1 |
9.1 |
1.56 |
8.1 |
8.0 |
9.0 |
9.1 |
3.13 |
8.1 |
8.0 |
9.1 |
8.9 |
6.25 |
8.1 |
7.9 |
9.1 |
8.7 |
12.5 |
8.1 |
7.9 |
9.0 |
8.0 |
25 |
7.9 |
7.8 |
9.0 |
7.0 |
50 |
7.8 |
7.7 |
8.9 |
6.6 |
100 |
7.6 |
7.5 |
8.8 |
6.1 |
Effect concentrations
|
nominal concentration based on |
EC0 |
EC50 |
EC100 |
24 h |
test material |
3.13 |
6.16 |
12.50 |
active ingredient |
2.03 |
4.00 |
8.13 |
|
48 h |
test material |
1.56 |
3.85 |
6.25 |
active ingredient |
1.01 |
2.50 |
4.06 |
Applicant's summary and conclusion
- Validity criteria fulfilled:
- yes
- Conclusions:
- The acute toxicity of undecanal to aquatic invertebrates was 48 -h EC50: 2.5 mg/L and does not require classification for acute toxicity according to EU 286/2011, table 4.1.0
- Executive summary:
The toxicity of undecanal was tested according to EC Directive 79/831/EEC which is similar to OECD TG 202. The test material was undecanal with a purity of 65%, therefore the effect concentrations were recalculated on the basis of the given purity. The test item was dissolved using Cremophor RH 40 as vehicle. Starting from a stock solution of 100 mg/L, a dilution series was prepared. The following concentrations were tested: nominal (active ingredient): 0 (control), 0 (solvent control), 0.51, 1.01, 2.03, 4.06, 8.12, 16.25, 32.5, and 65 mg/L. No analytical verification of the test concentrations was performed. Based on the volatilization half-life (lake: 5.2 d; see Ch. 5.4.4), a decrease of the test item concentration can be expected over the test duration, but most animals died within the first 24 h of the test.
The 48 -h EC50 was determined to be 3.85 mg/L based on test material and 2.5 mg/L based on active ingredient.
This result can be read across to n-/iso-undecanal. A detailed justification of read across is provided in the field Discussion of the endpoint summary of this section. It should be noted that the experimental effect concentration (48 -h EC50: 2.5 mg/L) is significantly higher than the LC50 value predicted by ECOSAR (0.863 mg/L, cf. endpoint summary).
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