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EC number: 700-342-7 | CAS number: 1163775-81-2
- 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
Biodegradation in water: screening tests
Two key studies for 1,2,4-Benzenetricarboxylic acid, mixed dodecyl and octyl triesters are reported for biodegradation:
The study from Chen Xiaoqian (2015 ) reports that 1,2,4-Benzenetricarboxylic acid, mixed dodecyl and octyl triesters was not readily biodegradable under the present test conditions.
The study from Zhang Jingji (2015) report that 1,2,4-Benzenetricarboxylic acid, mixed dodecyl and octyl triesters was primarily biodegradable, but not ultimately biodegradable. Therefore, the test substance was inherently biodegradable according the OECD definition.
Biodegradation in water, sediment and soil simulation tests
Simulation studies are not required due to the fact microbial pathways exist for the degradation of 1,2,4-Benzenetricarboxylic acid, mixed dodecyl and octyl triesters, the degradation of substance will be limited due to limited bioavailability. Biodegradation Pathway A microbial pathway (ester hydrolysis) does exist in nature for degradation of esters (Otton et al., 2008). According to the trimellitate category test plan for the US EPAs HPV Chemical Challenge Program, the degradation of the trimellitates is expected to precede through the step-wise hydrolysis of the ester groups to free alcohols and mellitic acid (ExxonMobil Biomedical Sciences, 2001). Further, the test plan states that these metabolites are known to rapidly degrade and not persist. Evidence of the biodegradation potential for 1,2,4-Benzenetricarboxylic acid, mixed dodecyl and octyl triesters, can be observed with the results from two OECD 301B ready biodegradability studies of the structural related substance 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters . In both studies there is an extended time lag (14 to 24 days) before biodegradation begins to occur. However, once biodegradation is initiated, the substance is significantly degraded (>70%) within 48 days. Limited Bioavailablity 1,2,4-Benzenetricarboxylic acid, mixed dodecyl and octyl triesters is an extremely hydrophobic substance that will have limited bioavailability to microorganisms living in soil. The limited bioavailability of the substance will also limit the amount of biodegradation that can occur in the soil. The measured log Koc value of the structural related substance 1,2,4-Benzenetricarboxylic acid, mixed dodecyl and octyl triesters was greater than 5.67 (the log Koc of the most hydrophobic standard). Using the KOCWIN Program v2.00 embedded in the US EPAs EPI Suite software (EPIWEB 4.0), the calculated log Koc values for 1,2,4-Benzenetricarboxylic acid, mixed dodecyl and octyl triesters ranged from 8.4 (estimated from the log Pow) to 8.98 (estimated from MCI). The equivalent calculated Koc values were 260600000 L/kg to 9470000000 L/kg. Based on these results, 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters is expected to be immobile in soil (Koc >5000, classification according to McCall et al., 1980). Conclusion The data requirement for further biodegradation studies is waived based on the weight of evidence supporting the conclusion that, while pathways exist for the degradation of 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters, the degradation of substance will be limited due to limited bioavailability.
Additional information
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