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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
Endpoint summary
Administrative data
Description of key information
Additional information
Biodegradation in water
Triethyl citrate was tested for its biodegradability potential according to EU method C.4 -D and OECD Guideline 301 F (Feil, 2010). Sodium benzoate (purity of 100 %) was used as reference compound. Also a toxicity control (test item and reference compound mixed) was run in parallel, to ensure, that the chosen test concentration was not inhibitory to microorganisms. The mean biodegradation after 28 days of the test substance was 78 % (ThOD NH4), further the 10 day window criterion was passed and therefore it is considered to be readily biodegradable. The reference item sodium benzoate was sufficiently degraded to 85 % after 14 days and to 88 % after 28 days of incubation, thus confirming the suitability of the aerobic activated sludge inoculum used. Furthermore, the test item was found to be not inhibitory to the aerobic activated sludge micro organisms and all validity criteria of the test method were met.
Biodegradation in water and sediment
Simulation testing on ultimate degradation in surface water, information requirement 9.2.1.2 in Annex IX, does not need to be conducted, as triethyl citrate (TEC) is considered to be readily biodegradable. The mean biodegradation after 28 days of the substance was 78%, the 10 day window criterion was passed from day 4 until day 14 [OECD Guideline 301 F, 2010].
Simulation testing on ultimate degradation in sediment, information requirement 9.2.1.4 in Annex IX, does also not need to be conducted, as it has been shown in soil biodegradation tests with the structural analogue acetyl tributyl citrate (CAS 77-90-7; ATBC) that the test substance is readily biodegradable.
The hazard assessment of TEC reveals neither a need to classify the substance as dangerous to the environment, nor is it a PBT or vPvB substance, nor are there any further indications that the substance may be hazardous to the environment. Therefore, a simulation test on biodegradation in surface water and sediment is scientifically not justified.
Biodegradation in soil
Two experimental results are available regarding biodegradation in soil for triethyl citrate. Both tests are conducted according to US Guidelines, whereby the methodological details, test conditions and results are reported in sufficient detail.
One experiment was conducted according to EPA OPPTS 835.3300 and ASTM D5988, concluding that the test substance can be considered as readily biodegradable in soil (Farrell, 2000). The required time for achieving 50 % mineralisation (t50) or 60 % mineralisation (t60) increased as the substance concentration in the soil increased. Nevertheless, at all substrate concentrations, net mineralisation of triethyl citrate 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.
Another experiment regarding ultimate biodegradation was conducted according to ASTM D5338 and ASTM D5988, whereby actively aerated compost was used as inoculum (Farrell, 2000), where the mineralisation of the test substance reached 64.9 % ThCO2in 45 days. Both the TEC and cellulose reference achieved total, net mineralisation 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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