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Diss Factsheets
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EC number: 201-070-7 | CAS number: 77-93-0
- 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
Biodegradation in soil
Administrative data
Link to relevant study record(s)
Description of key information
In a test according to EPA OPPTS 835.3300 & ASTM D5988 the biodegradation in soil was ≥79 % ThCO2 after 42 d, 60 % within 10-14 days (readily biodegradable);
t50 (0.8 mgC/g soil) = 6.6 d
t50 (3.2 mgC/g soil) = 9.4 d
t50 (12 mgC/g soil) = 43 d
In a further test according to ASTM D 5338 & ASTM D 598 the biodegradation in actively aerated compost was 64.9 % ThCO2 after 45 d (readily biodegradable);
t50 (17.2 mgC/g soil) = 33.4 d
Key value for chemical safety assessment
Additional information
In a test on biodegradation in soil according to EPA OPPTS 835.3300 and ASTM D5988 (Farrell, 2000) triethyl citrate (TEC) was found to be readily biodegradable. Decay rates decreased as a function of substrate concentration. Consequently, the time required to achieve 50 % mineralization (t50) or 60 % mineralization (t60) increased as the TEC concentration in the soil increased. Nevertheless, at all substrate concentrations, net mineralization of the TEC was greater than that of the positive control (cellulose). Moreover, biodegradation of the TEC met or exceeded the ‘pass levels’ defined in the ASTM, FDA, and EPA guidelines. That is, conversion of substrate-C into CO2exceeded 50 % ThCO2within the 64-day time limit set by the equivalent FDA soil biodegradation test (USFDA, 1987) and 60 % ThCO2within the time limits set by the equivalent ASTM (≤ 180 days) and USEPA (≤ 64 days) test methods (ASTM, 1999; USEPA, 1998b). These results – plus that fact that at substrate concentrations in the range recommended by the FDA and EPA tests (≤ 5 mg substrate-C g-1 soil), conversion of substrate-C into CO2exceeded 60 % ThCO2within a 10–14 day window following the lag period – indicate that TEC can be considered readily biodegradable (US EPA, 1998a).
In another test on ultimate biodegradation in actively aerated compost according to ASTM D 5338 and ASTM D 5988 (Farrell, 2000), mineralization of the test substance reached 64.9 % ThCO2in 45 days. Both the TEC and cellulose reference achieved total, net mineralization values ≥ 50 % ThCO2during the 45-day test exposure, cellulose was the only test material to exceed the 60 % ThCO2pass level defined in the ASTM guideline during the test exposure. Nevertheless, the calculated t60for the TEC was 53 days – well within the time limit defined in ASTM Standard D 6002 (i.e., during a test exposure of up to 180 days).
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