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EC number: 214-874-8 | CAS number: 1204-28-0
- 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
The registered substance trimellitic anhydride mono-chloride (TMAC) is not stable as its complete hydrolysis occured in less than 0.5 hour.
TMAC is expected to mobile as its Koc is estimated between 10 and 20 L/kg, it consequently has a low tendency to adsorb to soils and sediments. However this data must be taken with caution because the QSAR estimation of Koc value is not fully reliable.
The registered substance is considered as readily biodegradable according to read-across results.
Based on these data, the registered substance, trimellitic anhydride mono-chloride (TMAC), is not considered as persistent (P) nor very persistent (vP).
Additional information
Abiotic processes
Since trimellitic anhydride mono-chloride (TMAC) has been considered as readily biodegradable (Point 5.2.1), a study of its hydrolysis under a range of pH conditions is not strictly necessary.
However, a study of the hydrolysis trimellitic anhydride acid chloride (TMAC) has been performed in the context of the requirements for substances that may come into contact with food via packaging material. This study examined the behaviour of trimellitic anhydride acid chloride (TMAC) in unbuffered distilled water as a simple food simulant. TMAC was found to hydrolyse completely at 40 °C in less than 0.5 hour to trimellitic acid (TMLA) and hydrogen chloride. Hydrolysis of the monomer TMAC was virtually instantaneous.
Biodegradation
One of the three available studies was performed on the registered substance trimellitic anhydride mono-chloride (TMAC, target substance), while the two others were performed in its analogue trimellitic anhydride (TMA, source substance).
The first disregarded study (Environmental Biological Life Science Research Center, 1996) was performed on the registered substance trimellitic anhydride mono-chloride(target substance), according to a test similar to MITI test. The degradation of the substance after 28 days was found to be -11% while the degradation of the reference substance (Aniline) was 65% after 7 days of exposure. The blank inoculum control (containing only test medium) had greater oxygen consumption than the test substance throughout the study period. No toxicity test (with both test substance and reference substance) was performed and no sufficient data are available on the inoculum and flasks preparation, thus it is not possible to find the cause of these results. Moreover, no specific chemical analysis was performed to assess primary degradation while it is mandatory for the MITI test. Furthermore, one of the validity criteria is not fulfilled as the difference between extremes degradation values of replicates at the end of the test were more than 20%.Thus the study is considered as not reliable and was disregarded.
Trimellitic anhydride (TMA, source substance) was tested for ready biodegradability by two respirometric methods where the degradation "pass" level that conventionally represents complete mineralisation is 60%.
In the first biodegradation study (Lebertz, 1991) trimellitic anhydride was tested for ready biodegradability according to the 1984 OECD 301B (Sturm Test) procedure, at concentrations of approximately 10 and 20 mg/L. 98.7% and 77.4% degradation occurred within 28 days at concentrations of 10 and 20 mg trimellitic anhydride/L respectively and the 60% pass level was exceeded within 7 days.Recovery of CO2 provides a direct and unambiguous indication of the mineralisation of the test substance.
In the second biodegradation study (CITI, 1988) of reliability 2, TMA (100 mg/L) was tested for biodegradability by the Chemicals Inspection and Testing Institute of Japan to fulfil the requirements of the Japanese Chemical Substances Control Law. A composite inoculum (applied at 30 mg suspended solids/L) originating from ten specified locations around Japan, not deliberately adapted to the test substance, fed with peptone and glucose prior to use and renewed at regular intervals (see OECD Guideline 301C 1984 and 1992 for details) was employed as standard practice at CITI for these investigations. An automated respirometer was used to make continuous measurements of biochemical oxygen demand (BOD) and recorded BOD was compared to the theoretical oxygen demand (ThOD) calculated assuming the complete mineralisation of trimellitic anhydride to its terminal oxidation products. This comparison provides a measure of ultimate biodegradation. Measured BOD expressed as %ThOD reached 96% within 28 days in this study.Confirmatory indications are provided by total organic carbon (TOC) analyses - this non-specific technique showed 99% loss of the test substance (ultimate degradation) and are consistent with the figure of 96% for ultimate biodegradation based on BOD measurement. The pass-level of 70% was exceeded.
These results show that trimellitic anhydride (TMA, source substance), rapidly hydrolysed into trimellitic acid (TMLA) under test conditions, is readily biodegradable and not persistent (not P).
Both studies demonstrate that trimellitic anhydride (TMA) is readily biodegradable and this result signifies that trimellitic anhydride (TMA) will degrade rapidly and completely, without the formation of stable metabolites, under aerobic conditions in a variety environmental compartments (aquatic and terrestrial) and that extensive biodegradation may be anticipated in aerobic biological wastewater treatment processes.
Due to close strutural similarity between the source and target substances, these results indicate that the registered substance (TMAC, target substance) is expected to be readily biodegradable.
Transport and distribution
Adsorption / desorption
(Q)SAR-modelled adsorption coefficient (Koc) values for trimellitic anhydride mono-chloride (TMAC) obtained with the KOCWIN v2.00 model of the US EPA range from ca. 10 to 20 L/kg. Based on these values, TMAC is classed as mobile and is expected to have a low tendency to adsorb to soils and sediments.
However it should be noted that this data is given only for information and must be taken with caution, because these values are not fully reliable (out of the applicability domain for one criteria).
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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