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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
Toxicity to terrestrial arthropods
Administrative data
Link to relevant study record(s)
Description of key information
For DBP, adult reproduction was a more sensitive endpoint than was survival, with an EC10 and EC50 of 14 and 68 mg/kg, respectively.
Juvenile molting frequency seems to be a sensitive parameter, because number of cuticles produced by young springtails was reduced at 1 mg/kg.
Toxicitywas reduced when soil spiked with DBP was stored at 20°C for a period of up to 28 d before adding the animals. Reduction in
toxicity of DBP may be due a combination of degradation, evaporation, and adsorption of DBP to soil material.
Key value for chemical safety assessment
- Short-term EC50 or LC50 for soil dwelling arthropods:
- 10 mg/kg soil dw
- Long-term EC10, LC10 or NOEC for soil dwelling arthropods:
- 0.5 mg/kg soil dw
Additional information
Jensen et al. (2001) studied the effects of DEHP and DBP on the collembolan Folsomia fimetaria. Survival and reproduction on adult individuals (aged 23-26 days) were investigated by the use of small microcosms. The organisms were exposed for 21 days to DBP in moist soil (< 1.5% organic carbon) at the nominal concentrations of 0, 100, 250, 500, 750 and 1000 mg/kg dwt.
The DBP was added in acetone to dry soil. The acetone was evaporated and the soil remoistened with water before start of the experiment. Effects of the two phthalates on newly hatched collembolans were also tested in a multidish system. The endpoints were juvenile mortality, growth, and development (number of cuticles), the nominal test concentrations were 0, 1, 5, 10, and 25 mg DBP/ kg soil (dwt), and the test duration was six weeks.
To study the time course of observed DBP toxicity and to link DBP toxicity with its chemical fate in soil, soil spiked with DBP was stored at 20°C for 3, 7, 14, or 28 d before adding animals. After adding animals, tests were conducted as for the 21-d reproduction test described above. Four replicates of the test concentrations of DBP at 0, 50, 100, 200, 300, and 500 mg/kg were made.
DBP caused increased adult mortality at 250 mg/kg and juvenile mortality at 25 mg/kg. For DBP, adult reproduction was a more sensitive endpoint than was survival, with an EC10 and EC50 of 14 and 68 mg/kg, respectively.
Juvenile molting frequency seems to be a sensitive parameter, because number of cuticles produced by young springtails was reduced at 1 mg/kg ( EC10 = 0.5 mg/kg dry wt and EC50 was more than 10 mg/kg dry wt).
Toxicity was reduced when soil spiked with DBP was stored at 20°C for a period of up to 28 d before adding the animals. Reduction in toxicity of DBP may be due a combination of degradation, evaporation, and adsorption of DBP to soil material. This was confirmed by chemical analyses, which showed a rapid initial disappearance followed by a much slower disappearance. The results lead to the overall conclusion that significant adverse effects of phthalates on collembolans are not likely to occur as a result of normal sewage sludge application.
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