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Diss Factsheets
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EC number: 204-673-3 | CAS number: 124-04-9
- 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:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- guideline study without detailed documentation
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 202 (Daphnia sp. Acute Immobilisation Test)
- GLP compliance:
- not specified
- Analytical monitoring:
- yes
- Remarks:
- HPLC
- Details on sampling:
- At the start of exposure and at the end of exposure
- Vehicle:
- not specified
- Test organisms (species):
- Daphnia magna
- Test type:
- static
- Water media type:
- freshwater
- Limit test:
- no
- Total exposure duration:
- 48 h
- Test temperature:
- 20 +- 1°C
- pH:
- no data
- Dissolved oxygen:
- no data
- Nominal and measured concentrations:
- nominal: 100, 76.9, 59.2, 45.5, 35 mg/L (ratio 1.3), control
- Details on test conditions:
- - Number of organisms: 20 animals / concentration (5 animals per test vessel)
- Exposure period: 48 h
- Exposure method: static
- Test concentration: 100, 76.9, 59.2, 45.5, 35 mg/L (ratio 1.3), control
- Number of vessels: 4 vessels per concentration
- Test volume: 200 mL / vessel
- Test water temperature: 20 +-1°C
- Lighting: Room light, 16 hours light / 8 hours dark - Duration:
- 48 h
- Dose descriptor:
- LC50
- Effect conc.:
- 46 mg/L
- Nominal / measured:
- nominal
- Conc. based on:
- test mat.
- Basis for effect:
- other: immobilization
- Details on results:
- The effect concentrations relate to nominal concentrations.
- Conclusions:
- A 48h-EC50 of 46 mg/L was determined for the adipic acid towards daphnids under exposure conditions.
- Executive summary:
A study was performed to assess the acute toxicity of adipic acid to Daphnia magna STRAUS under static conditions in accordance with the OECD Guideline for Testing of Chemicals No. 202 'Daphnia sp., Acute Immobilisation Test'.
Daphnia magna were exposed to a range of concentrations (nominal: 100, 76.9, 59.2, 45.5, 35 mg/L) and a control for 48 h. 20 daphnis (4 vessels, 5 animals/vessel) were exposed per concentration. The test temperature was 20 +- 1°C.
After 48 h an EC50 of 46 mg/L was determined for adipic acid towards daphnids under exposure conditions.
Reference
Description of key information
A study was performed to assess the acute toxicity of adipic acid to Daphnia magna STRAUS under static conditions in accordance with the OECD Guideline for Testing of Chemicals No. 202 'Daphnia sp., Acute Immobilisation Test'.
Daphnia magna were exposed to a range of concentrations (nominal: 100, 76.9, 59.2, 45.5, 35 mg/L) and a control for 48 h. 20 daphnis (4 vessels, 5 animals/vessel) were exposed per concentration. The test temperature was 20 +- 1°C.
After 48 h an EC50 of 46 mg/L was determined for adipic acid towards daphnids under exposure conditions.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 46 mg/L
Additional information
With the invertebrate Daphnia magna one acute test according to the European guideline 79/831/EEC, method C.2 is available. For a test period of 24 hours an EC50 value of 85.6 mg/l was obtained. The same effect concentration was reported after a test period of 48 hours (BASF AG 1988b). pH values in the test solutions ranged from 4 (500 mg/l) to 7.7 (15.6 mg/l) and pH related effects on the daphnids cannot be excluded.
This study on daphnids was characterized by a concentration-dependant decrease of pH. During the test on Daphnia, the treatments testing adipic acid's concentrations near the EC50 value presented a pH markedly inferior to the control treatment. At the end of the 48-hour exposure period, the pH in the control treatment was 7.95, whereas it decreased from 7.2 to 5.26 in the range of concentrations (62.5 - 125 mg/L) covering the EC50 value (85.6 mg/L). Furthermore, it should be noticed that the pH value in the control treatment is high compared to the guideline's requirements. Based on this observation, a pH effect cannot be ruled out when considering the toxicity reported in this study.
Describing the toxicity towards aquatic invertebrates, the study conducted by the National Institute of Technology and Evaluation, Japan is preferred, despite deficiencies in study documentation concerning pH.
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