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EC number: 907-672-2 | 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
Endpoint summary
Administrative data
Description of key information
Additional information
Test result on different species covering different trophic levels and different durations of exposure are available for the test substance of concern (DBPP).
Short-term toxicity data (96h LC50) on 5 different fish species are available, based on 4 different studies. The most recent study (Goodband and Mullee, 2011) is regarded as key study with and LL50 (96h) of 1.8 mg/L. Additionally, there is one 14 -day test with survival and loss of equilibrium as endpoints (Thompson and Forbis, 1979). Effect values were in the same range as those determined after 96 hrs of exposure. With regard to long-term toxicity, there is an ELS-test available in which the fish were exposed for 60 days with the aim to find a Maximum Allowable Tolerance Concentration, based on the evaluation of hatchability of eggs, percentage survival of the fry, growth and growth rate of the fry (both as length and as weight), morphology and behavioural aspects (Boudreau and McAllister, 1980). From that study it was concluded that the NOEC was above 0.11 mg/L as there were no signficant effects up to the highest tested dose.
With regard to invertebrates, different tests assessing the acuteaquatic toxicity towards Daphnia magna are available (Goodband and Mullee, 2011; McAllister et al., 1978; Heidolph et al., 1982; LeBlanc, 1980). The most recent study was determined as the Key study with an EL50 (48h) of 1.4 mg/L as this study is performed according to the most recent guidelines. Additionally, one long-term (21-day) study with Daphnia magna was carried out in 1980 (Altshul et al., 1980) to find the Maximum Tolerable Concentration (MTC) of DBPP for Daphnia magna. The study was carried out according to then existing guidelines and can be regarded as a well-performed study (K2). There were no effects on any of the sublethal endpoints evaluated. Based on the effects on survival (21-days), an EC10 of 0.106 mg/L was determined.
Two algal studies are available, one carried out in 1978 according to then existing guidelines (Hollister and Shuba, 1978) and a recent study (2011) carried out according to existing guidelines and under GLP (Vrijenhoef and Mullee, 2011). The latter study is regarded as the key study and the results from that study is used in further risk assessment. The relevant EC50 value for algae (& DBPP) was 9.6 mg/L, the EC10 was 3.5 mg/L.
Based on the described acute and chronic toxicity information for aquatic organisms it can thus be concluded that Daphnia magna (thus invertebrates) are the most sensitive organisms with an EL50 of 1.4 mg/L (48hr) and an EC10 of 0.106 mg/L (21-days).
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