Registration Dossier
Registration Dossier
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 204-211-0 | CAS number: 117-81-7
- 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

Bioaccumulation: terrestrial
Administrative data
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
- BCF (terrestrial species):
- 1
Additional information
Terrestrial bioaccumulation
Two reliable studies are available on bioaccumulation of DEHP in terrestrial plants. Cai et al. (2008) studied the uptake of 5 polycyclic-aromatic hydrocarbons and 2 phthalic acid esters (including DEHP) in radish (Raphanus sativus). Radish were seeded in soil free of contamination and in soil amended with 1, 2 or 4 % of sewage sludge containing a mix of all these organic contaminants. Sludge contained 4.4 mg/kg dw of DEHP. Plants were grown during 64 days before harvest. Measurements of DEHP in substrate and roots and shoots lead to BCF estimations. In all cases BCF values where < 1. Therefore under the test conditions applied, DEHP did not bioaccumulate in radish. No new studies were identified for bioaccumulation in earthworms since the previous EU-RAR (2008). In their study, Peterson et al. studied the behaviour of DEHP during fertilization process and potential effect on plant by 3 different methods under field and greenhouse conditions (cf Section 5.2.4 in IUCLID)
The first experiment was a 3-year field study. The soils were amended once a year during 3 years with sewage sludges (SS), compost or manure containing DEHP. Assuming no biodegradation occurred the total amount input at the end of the study was 0.238, 0.092, 0.290 and 0.04 mg/kg in SShigh SSlow, compost and Manure trials respectively. Crops rotation over the duration of the test was performed with spring barley (1989), oat (1990) and spring barley (1991). On the 3rdyear, the crop harvest was analysed for their contaminant. Soil fertility, micro-arthropod population were also checked.
After 3 years, soil fauna showed no discernible differences between the two sludge treatment but densities were increased in compost and manure treatment. No grain samples showed DEHP, while green parts of the plants contained between 0.065 and 0.787 mg/kg of DEHP. No relationship of this content was seen with the amount of DEHP in the different treatment applied, therefore it was concluded that this amount mainly derived from atmospheric deposition.
In the third experiment of the same study (pot experiment with amended soil (SShigh) and soil spiked with DEHP at 55 mg/kg) seedling of oilseed rape was studied during 30 days. Plant uptake and soil concentrations were checked. No uptake was observed.
In conclusion, considering the results observed, a reasonable worst case BCF of 1 for terrestrial species is used in the present assessment.
Value used for CSA:Terrestrial BCF: 1 (L/kg ww or dimensionless)
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.

EU Privacy Disclaimer
This website uses cookies to ensure you get the best experience on our websites.