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EC number: 211-746-3 | CAS number: 693-23-2
- 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:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: Abstract, test duration 24 h instead of 48 h.
- Principles of method if other than guideline:
- Method: DIN 38412 part 11
- GLP compliance:
- no
- Analytical monitoring:
- yes
- Vehicle:
- no
- Details on test solutions:
- - Dispersion: saturated solution
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- - Common name: Daphnia magna
- Strain: Daphnia magna (Strauss) - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 24 h
- Post exposure observation period:
- none
- Reference substance (positive control):
- not specified
- Duration:
- 24 h
- Dose descriptor:
- EC0
- Effect conc.:
- >= 27.6 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Key result
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 27.6 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Test parameter: immobilization
- Behavioural abnormalities: no - Validity criteria fulfilled:
- not specified
- Conclusions:
- The EC50 (24h) based on nominal concentration was determined as > 27.6 mg/L indicating that the test substance is not harmful to aquatic invertebrates.
- Executive summary:
An acute toxicity study with Daphnia magna was performed according to the DIN 38412 part 11 method, under static conditions (24 h incubation period). An analytical monitoring was included. No toxic reference or control treatment group was included in the test. There was no immobilization, toxic effects or abnormal responses. Thus the EC50 (24 h) was >27.6 mg dodecanedioic acid /L.
- Endpoint:
- short-term toxicity to aquatic invertebrates
- Type of information:
- experimental study
- Adequacy of study:
- weight of evidence
- Reliability:
- 4 (not assignable)
- Rationale for reliability incl. deficiencies:
- other: No analytic was performed. Nominal test concentrations exceeded the solubility of the test item, test duration 24 h instead of 48 h.
- Principles of method if other than guideline:
- Static screening method
- GLP compliance:
- no
- Analytical monitoring:
- no
- Vehicle:
- no
- Test organisms (species):
- Daphnia magna
- Details on test organisms:
- - Common name: Daphnia magna (Strauss)
- Strain: strain identical with the strain of the Bundesgesundheitsamt/Inst. Wasser-Boden-Luft
- Source: own breed
- Feeding during test: no - Test type:
- static
- Water media type:
- freshwater
- Limit test:
- yes
- Total exposure duration:
- 24 h
- Post exposure observation period:
- none
- Hardness:
- about 14 ºdH
- Test temperature:
- Room temperature
- Nominal and measured concentrations:
- Nominal: 1000 mg/l
- Details on test conditions:
- - Test vessel: glass beaker, covered with glass plate, 20 ml liquid volume
- Number of daphnids per vessel: about 20
- Photoperiod: about 16 hours illumination per day
- Food type: Chlorella kessleri
- Number of replicates: 1 - Reference substance (positive control):
- no
- Duration:
- 24 h
- Dose descriptor:
- EC0
- Effect conc.:
- >= 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Key result
- Duration:
- 24 h
- Dose descriptor:
- EC50
- Effect conc.:
- > 1 000 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- mobility
- Details on results:
- - Test parameter: immobilization
- Behavioural abnormalities: no - Validity criteria fulfilled:
- not specified
- Conclusions:
- The EC50 (24h) based on nominal concentration was determined as > 1000 mg/L indicating that the test substance is not harmful to aquatic invertebrates.
- Executive summary:
An acute toxicity study with Daphnia magna was performed according to the screening method (differing from OECD-Guideline 202, part 1 in: number of daphnids per concentration and fact that the substance concentration was not followed by chemical analysis), under static conditions (24 h incubation period). About 20 daphnids in one replicate were exposed to 1000 mg dodecanedioic acid /L nominal concentration. No toxic reference or control treatment group was included in the test. No analytical monitoring was included. There was no immobilization, toxic effects or abnormal responses. Thus the EC50 (24 h) was >1000 mg dodecanedioic acid /L.
Referenceopen allclose all
Description of key information
An acute daphnia test (24 h) conducted by Scholz N. (1988) studied the toxicity of dodecanedioic acid on Daphnia magna (determined in a static test according to the DIN 38412 part 11 method). The second acute toxicity study conducted by Wind T. and Mühlberg B. (1982) with Daphnia magna (about 20 daphnids in 1000 mg dodecanedioic acid /L nominal concentration) was performed according to the screening method (differing from OECD-Guideline 202), under static conditions (24 h incubation period) with one replicate per concentration level.
Key value for chemical safety assessment
Additional information
The results are summarised in the following table:
Species | Endpoint (exposure duration) | Exposure concentration | Reference |
Daphnia magna | EC50 (24 h) | > 27.6 mg/L | Scholz N. (1988) |
Daphnia magna | EC50 (24 h) | > 1000 mg/L | Wind T., Mühlberg B. (1982) |
The available studies indicate that dodecanedioic acid concentrations up to 1000 mg/L are not toxic to aquatic invertebrates. However, taking into considaration that no analytical monitoring was conducted and that the water solubilty is between 30 mg/L and 40 mg/L the endpoint that should be considered for risk assessment purposes is >27.6 mg/L.
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