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Diss Factsheets
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EC number: 247-660-8 | CAS number: 26401-35-4
- 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
Stability
Hydrolysis
Tests need not be conducted, as diisotridecyl adipate is highly insoluble in water (see Sect. 4.8) (Annex VIII, Nr 9.2.2.1.)
In addition using the calculation program US EPA EPI Suite v4.00, the half-life of diisotridecyl adipate at 25°C and under neutral conditions was estimation to be 4.6 years.
Biodegradation
Biodegradation in water: screening tests
The test substance diisotridecyl adipate was demonstrated to be readily biodegradable in three OECD guideline 301-tests.
An OECD 301F-study (Flach, 2014, key study) (guideline suitable for poorly soluble and volatile substances) with the test substance has been conducted, showing that DITA is readily biodegradable (69 % biodegradation based on ThOD after 28 days). The inoculum used in this study was neither adapted, nor pre-exposed (confirmation of the test institute attached). Two more studies (OECD 301B) are available, showing that DITA is readily biodegradable. In the first OECD 301B study, 81 % biodegradation were achieved within 28 d, fulfilling the 10d-window criterion (although not required for an UVCB). A second OECD 301B-test resulted in a biodegradation extent of 69.6 % after 28 days. The other studies reported for DITA clearly indicate the ready biodegradability of the substance, by almost reaching the 60% biodegradation threshold. In the respective study according to OECD guideline 301B, a biodegradation of 56.6% within 28 days was obtained with DITA. Similar biodegradation was found in the other 301F study (58.53% biodegradation within 28 days). Supporting all these findings, the read-across substance diisotridecyl dodecanedioate was found readily biodegradable in an OECD 301B-test.
Biodegradation in water and sediment: simulation tests
In accordance with column 2 of REACH Annex IX Nr 9.2.1.2, the study does not need to be conducted as the substance is regarded as readily biodegradable and to be highly insoluble in water (see Sect. 4.8). DITA is readily biodegradable and therefore a sediment simulation test is not required. The available studies on the biodegradation behavior of DITA, particularly the key study of Flach (2014), clearly show that the substance fulfills the criteria for Ready biodegradability. The inoculum used in these studies was neither adapted, nor pre-exposed. This also applies to the latest OECD 301F study with DITA (Flach, 2014) and was confirmed by the respective test institute (please see attachment: " issue2_OECD301FcommentsInoculum_diisotridecyladipate __studyno892. pdf"). Based on the data, direct and indirect sediment deposition is unlikely.
Biodegradation in soil
In accordance with column 2 of REACH Annex IX Nr 9.2.1.2, the study does not need to be conducted as the substance is regarded as readily biodegradable. DITA is readily biodegradable and therefore a soil simulation test is not required. The available studies on the biodegradation behavior of DITA, particularly the key study of Flach (2014), clearly show that the substance fulfills the criteria for Ready biodegradability. The inoculum used in these studies was neither adapted, nor pre-exposed. This also applies to the latest OECD 301F study with DITA (Flach, 2014) and was confirmed by the respective test institute (please see attachment: " issue2_OECD301FcommentsInoculum_diisotridecyladipate __studyno892. pdf"). It is expected that direct and indirect soil exposition is unlikely.
Bioaccumulation
Bioaccumulation: aquatic/sediment
The log BCF of diisotridecyl adipate (log Pow = 13.03) was estimated to be 1.17 (BCF 14.8) using the program US EPA EPI Suite v4.00. In addition, a log BAF (upper trophic) of -0.008 (BAF = 0.982) was calculated using the method of Arnot-Gobas. The low BCF/BAF values indicate a low potential of diisotridecyl adipate for bioaccumulation in aquatic organisms (MWC, 2010).
Transport and Distribution
Adsorption/Desorption
Based on a calculated log Koc of 7.08 (MCI method) or 8.00 (log Kow method) diisotridecyl adipate is expected to have a high potential for accumulation in soil and sediment (MWC, 2010).
As additional information, the Koc of butyric acid was estimated to be 45.5 at pH 7 (log Koc = 1.66) (OXEA, 2010) indicating high mobility in soil.
Henrys Law constant
The Henry's law constant (HLC) of diisotridecyl adipate at 25°C was estimated by calculation methods (program US EPA EPI Suite v4.00) (MWC 2010).
Bond contribution method: HLC (25°C) = 89.9 Pa*m3/mol
Group contribution method: HLC (25°C) = 68.3 Pa*m3/mol
Diisotridecyl adipate will volatilize from water.
Distribution modelling
Estimates obtained from Level III fugacity distribution modeling using US EPA EPI Suite v4.00, indicate that emissions of diisotridecyl adipate will distribute mostly in soil (84.9%) and to a lesser extend in water (14.8%). The fractions in air (0.28%) and in sediment (0.02%) are minimal. The estimated persistence time is 1310 hr (ca. 55 days) (MWC 2010).
Other distribution data
Volatilization from Water
Using the calculated Henry's Law Constant (HLC) of 8.89 Pa*m³/mol at 25 °C, diisotridecyl adipate volatilization half-lifes from a model river and a model lake were estimated to 4.3 and 236 hours (ca. 0.2 and 10 days), respectively (MWC 2010).
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