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EC number: 290-754-9 | CAS number: 90218-76-1
- 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 water and sediment: simulation tests
Administrative data
- Endpoint:
- biodegradation in water: sediment simulation testing
- Type of information:
- other: Literature weight of evidence
- Adequacy of study:
- weight of evidence
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- data from handbook or collection of data
Data source
Referenceopen allclose all
- Reference Type:
- publication
- Title:
- Biodegradation of mono-alkyl phthalate esters in natural sediments.
- Author:
- Otton, V., Sura, S., Blair, J., Ikonomou, M. and Gobas, F.
- Year:
- 2 008
- Bibliographic source:
- Chemosphere 71 (11): 2011-2016
- Reference Type:
- publication
- Title:
- Measurement of Sorption Coefficients of Organic Chemicals and Their Use in Environmental Fate Analysis, Test Protocols for Environmental Fate and Movement of Toxicants, proceedings 94th Annual Meeting
- Author:
- McCall, P.J., Laskowski, D.A., Swann, R.L. and Dishburger, H.J.
- Year:
- 1 980
- Bibliographic source:
- 94th Annual Meeting, Association of Official Analytical Chemists, Washington, D.C., October 21-22, 1980, pp. 89-109.
- Report date:
- 1980
- Reference Type:
- publication
- Title:
- High Production Volume (HPV) Chemical Challenge Program Test Plan for the Trimellitate Category
- Author:
- Exxon Biomedical Sciences.
- Year:
- 2 001
- Bibliographic source:
- Submitted to the US EPA on 13 Dec. 2001.
- Report date:
- 2001
Materials and methods
- Principles of method if other than guideline:
- Literature data weight of evidence review
- GLP compliance:
- not specified
Test material
- Reference substance name:
- 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters
- EC Number:
- 290-754-9
- EC Name:
- 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters
- Cas Number:
- 90218-76-1
- Molecular formula:
- C33H51O6 to C39H66O6
- IUPAC Name:
- tris(mixed decyl and octyl)benzene-1,2,4-tricarboxylate
- Test material form:
- liquid
- Remarks:
- Colorless
- Details on test material:
- Product name : LINPLAST 810 TM unstabilized (P0810TU)
Batch number: 05804/MA
Relative density at 20 °C: 0.972*
Water Solubility: < 28.3 µg/L
Expiry date: 2023-01-31
The test item and the information concerning the test item were provided by the sponsor.
* information was provided by the ECHA
1
Study design
- Inoculum or test system:
- not specified
Results and discussion
% Degradation
- Remarks on result:
- other: WoE
- Transformation products:
- not measured
- Details on results:
- There are no data for sediment biodegradation studies relating to 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters. Sediment biodegradation studies are not needed due to the fact that microbial pathways exist for the degradation of 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl trimesters and that significant biodegradation has been demonstrated even though the physico-chemical properties of the substance predict that degradation in standard guideline studies could be limited due to limited bioavailability. Poor bioavailability limiting the degradation rate of a substance has been noted in ECHA documentation (ECHA, 2017). Biodegradation Pathway and Rate 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 proceed through the step-wise hydrolysis of the ester groups to free alcohols and trimellitic acid (ExxonMobil Biomedical Sciences, 2001). Further, the test plan states that these metabolites are known to rapidly degrade and not persist. Evidence of the true biodegradation potential for 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters can be observed with the results from two OECD 301B ready biodegradability studies. 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 with >60% degradation occurring at 35 and 43 days in the studies. The slow but steady increase in degradation observed in the studies indicate that the microorganisms required time for accessing and degrading the substance (ECHA, 2017). Limited Bioavailablity 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters is an extremely hydrophobic substance that may have limited bioavailability to microorganisms living in sediments. The measured log Koc value 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 decyl and octyl triesters ranged from 7.87 (estimated from the log Pow) to 8.46 (estimated from MCI). The equivalent calculated Koc values were 74,000 L/kg to 290,000 L/kg. Based on these results, 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters is expected to be immobile in sediment (Koc >5000, classification according to McCall et al., 1980). No Toxicity to Sediment Organisms for Worst Case Read Across Substances Due to greater bioavailability (see table below), phthalates such as Diisononyl Phthalate (DINP) and Diisodecyl Phthalate (DIDP) are read across substances that represent a worst case for examining the potential toxicity to sediment organisms of 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters. In 10 day spiked sediment toxicity test with Hyalella azteca and Chironomus tentans, no adverse effects on survival or growth were observed with DINP or DIDP (Call et al., 2001). In addition, the effects of DIDP on the first larval stage to the adult emergence stage of Chironomus riparius was tested in a 28 day study using spiked sediments (Brown et al., 1996). DIDP did not have any effects on the survival, development and emergence of Chironomus riparius. Substance (1): 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters; Water Solubility: < 1 mg/L (measured)/0.0006 µg/L (calculated); log Kow: 12.79 (calculated); log Koc: >5.67 (measured)/7.87 to 8.46 (calculated) Substance (2): Diisononyl Phthalate (DINP); Water Solubility: 0.6 µg/L (measured); log Kow: 8.8 to 9.7 (measured); log Koc: 6 (calculated) Substance (3): Diisodecyl Phthalate (DIDP); Water Solubility: 0.2 μg/L (measured); log Kow: 8.8 (measured)/9.46 (calculated); log Koc: 5.46 (measured). Conclusion The data requirement for sediment biodegradation testing is waived based on the weight of evidence supporting the conclusion that there are established pathways for the degradation of 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters and the substance reached >60% degradation in two 301B studies after an extended lag period. In addition, the substance will not cause toxicity to sediment organisms based on read across substances. References Brown, D., K. M. Stewart, C. P. Croudace, E. Gillings, and R. S. Thompson. (1996). The Effect of Phthalate Ester Plasticisers on the Emergence of the Midge (Chironomus riparius) from Treated Sediments. Chemosphere 32 (11): 2177-2187. Call, D. J., Cox, D. A., Geiger, D. L., Genisot, K. I., Markee, T. P., Brooke, L. T., Polkinghorne, C. N., VandeVenter, F. A., Gorsuch, J. W., Robillard, K. A., Parkerton, T. F., Reiley, M. C., Ankley, G. T. and Mount, D. R. (2001). An Assessment of the Toxicity of Phthalate Esters to Freshwater Benthos: 2. Sediment Exposures. Environ Toxicol Chem. 20 (8): 1805-15. ECHA. (2017). Guidance on Information Requirements and Chemical Safety Assessment Chapter R.7b: Endpoint specific guidance. Version 4.0. June 2017. Exxon Biomedical Sciences. (2001). High Production Volume (HPV) Chemical Challenge Program Test Plan for the Trimellitate Category. Submitted to the US EPA on 13 Dec. 2001. McCall, P. J., Laskowski, D. A., Swann, R. L. and Dishburger, H. J. (1980). Measurement of Sorption Coefficients of Organic Chemicals and Their Use in Environmental Fate Analysis, Test Protocols for Environmental Fate and Movement of Toxicants, proceedings 94th Annual Meeting, Association of Official Analytical Chemists, Washington, D. C., October 21-22, 1980, pp. 89-109. Otton, V., Sura, S., Blair, J., Ikonomou, M. and Gobas, F. (2008). Biodegradation of mono-alkyl phthalate esters in natural sediments. Chemosphere 71 (11): 2011-2016
Applicant's summary and conclusion
- Conclusions:
- Conclusion The data requirement for soil biodegradation 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.
- Executive summary:
There are no data for sediment biodegradation studies relating to 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters. Sediment biodegradation studies are not needed due to the fact that microbial pathways exist for the degradation of 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl trimesters and that significant biodegradation has been demonstrated even though the physico-chemical properties of the substance predict that degradation in standard guideline studies could be limited due to limited bioavailability. Poor bioavailability limiting the degradation rate of a substance has been noted in ECHA documentation (ECHA, 2017). Biodegradation Pathway and Rate 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 proceed through the step-wise hydrolysis of the ester groups to free alcohols and trimellitic acid (ExxonMobil Biomedical Sciences, 2001). Further, the test plan states that these metabolites are known to rapidly degrade and not persist. Evidence of the true biodegradation potential for 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters can be observed with the results from two OECD 301B ready biodegradability studies. 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 with >60% degradation occurring at 35 and 43 days in the studies. The slow but steady increase in degradation observed in the studies indicate that the microorganisms required time for accessing and degrading the substance (ECHA, 2017). Limited Bioavailablity 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters is an extremely hydrophobic substance that may have limited bioavailability to microorganisms living in sediments. The measured log Koc value 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 decyl and octyl triesters ranged from 7.87 (estimated from the log Pow) to 8.46 (estimated from MCI). The equivalent calculated Koc values were 74,000 L/kg to 290,000 L/kg. Based on these results, 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters is expected to be immobile in sediment (Koc >5000, classification according to McCall et al., 1980). No Toxicity to Sediment Organisms for Worst Case Read Across Substances Due to greater bioavailability (see table below), phthalates such as Diisononyl Phthalate (DINP) and Diisodecyl Phthalate (DIDP) are read across substances that represent a worst case for examining the potential toxicity to sediment organisms of 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters. In 10 day spiked sediment toxicity test with Hyalella azteca and Chironomus tentans, no adverse effects on survival or growth were observed with DINP or DIDP (Call et al., 2001). In addition, the effects of DIDP on the first larval stage to the adult emergence stage of Chironomus riparius was tested in a 28 day study using spiked sediments (Brown et al., 1996). DIDP did not have any effects on the survival, development and emergence of Chironomus riparius. Substance (1): 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters; Water Solubility: < 1 mg/L (measured)/0.0006 µg/L (calculated); log Kow: 12.79 (calculated); log Koc: >5.67 (measured)/7.87 to 8.46 (calculated) Substance (2): Diisononyl Phthalate (DINP); Water Solubility: 0.6 µg/L (measured); log Kow: 8.8 to 9.7 (measured); log Koc: 6 (calculated) Substance (3): Diisodecyl Phthalate (DIDP); Water Solubility: 0.2 μg/L (measured); log Kow: 8.8 (measured)/9.46 (calculated); log Koc: 5.46 (measured). Conclusion The data requirement for sediment biodegradation testing is waived based on the weight of evidence supporting the conclusion that there are established pathways for the degradation of 1,2,4-Benzenetricarboxylic acid, mixed decyl and octyl triesters and the substance reached >60% degradation in two 301B studies after an extended lag period. In addition, the substance will not cause toxicity to sediment organisms based on read across substances. References Brown, D., K. M. Stewart, C. P. Croudace, E. Gillings, and R. S. Thompson. (1996). The Effect of Phthalate Ester Plasticisers on the Emergence of the Midge (Chironomus riparius) from Treated Sediments. Chemosphere 32 (11): 2177-2187. Call, D. J., Cox, D. A., Geiger, D. L., Genisot, K. I., Markee, T. P., Brooke, L. T., Polkinghorne, C. N., VandeVenter, F. A., Gorsuch, J. W., Robillard, K. A., Parkerton, T. F., Reiley, M. C., Ankley, G. T. and Mount, D. R. (2001). An Assessment of the Toxicity of Phthalate Esters to Freshwater Benthos: 2. Sediment Exposures. Environ Toxicol Chem. 20 (8): 1805-15. ECHA. (2017). Guidance on Information Requirements and Chemical Safety Assessment Chapter R.7b: Endpoint specific guidance. Version 4.0. June 2017. Exxon Biomedical Sciences. (2001). High Production Volume (HPV) Chemical Challenge Program Test Plan for the Trimellitate Category. Submitted to the US EPA on 13 Dec. 2001. McCall, P. J., Laskowski, D. A., Swann, R. L. and Dishburger, H. J. (1980). Measurement of Sorption Coefficients of Organic Chemicals and Their Use in Environmental Fate Analysis, Test Protocols for Environmental Fate and Movement of Toxicants, proceedings 94th Annual Meeting, Association of Official Analytical Chemists, Washington, D. C., October 21-22, 1980, pp. 89-109. Otton, V., Sura, S., Blair, J., Ikonomou, M. and Gobas, F. (2008). Biodegradation of mono-alkyl phthalate esters in natural sediments. Chemosphere 71 (11): 2011-2016
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