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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
Endpoint summary
Administrative data
Description of key information
Additional information
Screening test for environmental fate and pathways were conducted for triethyl citrate. Experimental results are available for biodegradation in water (Feil, 2010) and soil (Farrell, 2000), concluding that the substance is readily biodegradable. In consequence, no simulation test for biodegradation in water and sediment has to be conducted (in accordance with REACH, Annex IX, Section 9.2.1.2, Column 2) as well as the determination of hydrolysis of the substance is not necessary (in accordance with REACH, Annex VIII, Section 9.2.2.1, Column 2).
The QSAR software BCFBAF v3.01 predicts the BCF for the substance as 2.75 L/kg wet-wt, based on the LogPow. A BCF of 2.48 L/kg wet wt is predicted, based on mechanistic first principles (Arnot-Gobas method).
The substance specific partition coefficient (LogPow) was determined by the High Performance Liquid Chromatography (HPLC) method according to OECD Guideline 117 (Villa, 2011), resulting in a value of 1.17 and leading to the waiving of an experiment regarding soil adsorption in accordance with REACH regulation (Annex VIII, Section 9.3.1, Column 2). However, the organic-normalized sorption coefficient for soil (Koc) can be predicted with computer software, developed by US-EPA. The Koc was predicted with KOCWIN v2.00, using two different methods: the Sabljic molecular connectivity (MCI) method, resulting in a value of 21.02 L/kg and the traditional method, giving a Koc value of 10.71 L/kg. For the chemical safety assessment, the result of the MCI method is taken into account. These values reinforce the indicated very weak binding potential of the test substance to soil particles. Another QSAR prediction was performed for triethyl citrate regarding phototransformation in air, resulting in an overall gas-phase reaction constant of 7.33 E-12 cm³/molecules-sec (= 0.63 m³/molecules-day), with an half-life of 1.46 d (17.52 h) by assuming a 12 h day with an OH rate constant of 1.5E6 OH/cm³ and 25 °C. The Henry's Law Constant was calculated with the US-EPA computer program HENRYWIN (v3.20) to be 6.48 E-005 Pa*m3*mol-1 at 25°C.Due to the rapid biodegradation, no monitoring data or field study results are available for triethyl citrate. These types of experiments are also not mandatory under REACH.
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.
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