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EC number: 201-557-4 | CAS number: 84-74-2
- 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)
Description of key information
Study was conducted in accordance with US EPA standard (and compliant with EU and OECD guidelines) on 3 species of invertebrates: Mysidposis bahia a marine species and two fresh water test species a Parantanytarsus parthogenetica and Daphnia magna. Tests were performed in static conditions. No solvent was used and care was taken to avoid remaining floating test chemical. EC50 (48 h) for Daphnia magna was 2.99 mg/L, EC50 (96 h) for Mysidposis bahia was 0.5 mg/L and LC50 (96 h) for Parantanytarsus parthogenetica was 6.29 mg/L. All reported effect concentrations are based on measured test concentration.
As the studies were performed according to standards and GLP procedure but no detailed information were given in the publication, therefore, the results are considered as reliable with acceptable restrictions.
Key value for chemical safety assessment
Fresh water invertebrates
Fresh water invertebrates
- Effect concentration:
- 2.99 mg/L
Marine water invertebrates
Marine water invertebrates
- Effect concentration:
- 0.5 mg/L
Additional information
Foster and Sanders, 1973 studied the toxicity for DBP in flow-through bioassay to fresh water organism. The 96-hr LC50 to scuds (Gammarus pseudolimnaeus) was 2.1 mg/l - the value is lower as reported in study withDaphnia magna, but in this publication are not published detailed information about material and methods, test organisms, statistical analysis etc., so the result with scud is used only as a supporting study.
In the European Union Risk Assessment Report for dibutyl phthalate, 2004 (EUR 19840 EN) are presented also other toxicity results for aquatic invertebrates (see table below). The lowest observed 50% effect concentration for freshwater species was established by Streufert et al., 1980. The 48 h EC50 forChironomus plumosuswas 0.76 mg/L
Method |
Results (95% C.I.) (mg/L) |
Remarks |
Reference |
EE92/69 |
3.4(48 h EC50) |
– Daphnia magna |
Hüls (1994b) |
Other |
5.2(4.7-5.6) - (48 h EC50) |
– Daphnia magna |
McCarthy and Whitmore (1985) |
Other |
17(24 h EC50) |
– Daphnia magna |
Kühn et al. (1989) |
EG&G Bionomics (1982) |
3.4(3.1-3.8) - (48 h EC50) |
– Daphnia magna |
CMA (1984) |
Other |
0.76(48 h EC50) |
– Chironomus plumosus |
Streufert et al. (1980) |
Other |
0.8(0.6-0.9) - (96 h LC(I)50) |
– Mysidopsis bahia |
EG&G Bionomics (1984a) |
Other |
1.7(1.3-2.2) - (96 h LC(I)50 |
– Nitocra spinipes – brackish water |
Lindén et al. (1979) |
APHA (1971) |
2.1(96 h LC50) |
– Gammarus pseudolimnaeus |
Mayer and Sanders (1973)
|
Other |
5.8(96 h EC50) |
– Paratanytarsus parthenogenetica |
EG&G Bionomics (1984b)
|
Other |
8(24 h LC50) |
– Artemia salina – seawater |
Hudson et al. (1981) |
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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