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EC number: 251-823-9 | CAS number: 34090-76-1
- 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
Endpoint summary
Administrative data
Description of key information
Oral:
A NOAEL of 100 mg/kg bw/day was determined in a combined repeated dose/reproduction toxicity study (OECD 422) in rats based on changes in clinical chemistry parameters, changes in organ weights and inflammation of the forestomach mucosa.
Dermal and inhalation:
In accordance with column 2 of REACH Annex IX, the test repeated dose toxicity after dermal exposure (required in section 8.6) does not need to be conducted because there is another repeated toxicity robust study available for the oral route.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Endpoint conclusion
- Dose descriptor:
- NOAEL
- 100 mg/kg bw/day
- Study duration:
- subacute
- Species:
- rat
Additional information
Oral:
In the key study (Izumi, 1997), tetrahydromethylphthalic anhydride (MTHPA) was administered by gavage at doses of 0, 30, 100 and 300 mg/kg/day for 49 days in males and from 14 days before mating to day 3 of lactation in females (total number of 38 days). All animals survived at all treated group, except three animals died by accident (one female in 30 mg/kg, one male in 300 mg/kg and one female in 300 mg/kg group). Salivation was transiently observed in males of 300 mg/kg group at the day 36-49. Histopathological examination revealed squamous hyperplasia of the forestomach in both sexes of the 300 mg/kg group, epithelial vascular change, edema and cellular inflammation of the forestomach in males of the 300 mg/kg group, and erosion of the forestomach in females of 300 mg/kg group. There were no adverse effects on body weight and food consumption. There were no alterations related to tetrahydromethyl-1, 3-isobenzofuranedione on hematological examination. Decreased total cholesterol and BUN and increased triglyceride were observed in males of the 300 mg/kg. As a gross finding, mucosal thickening of the forestomach was found in both sexes of the 300 mg/kg group. Increased adrenal weights were observed in males of the 300 mg/kg group.
The major toxicity was inflammation of stomach mucosa. On the basis of this study, NOEL is 30mg/kg/day (male), 100mg/kg/day (female) and NOAEL is considered to be100 mg/kg/day for both sexes.
No 90 day toxicity study with tetrahydromethylphthalic anhydride (MTHPA) is available. Taken all data from MTHPA and structural analogue substances together, a new 90 day toxicity study with MTHPA is not required and not in line with animal welfare ideas. The data available for chemically almost identical substances in different species and for exposure periods of 90 days support the findings noted in OECD 422 study taking the time extrapolation factor into account. Therefore, the OECD 422 study is considered to represent a reliable basis for DNEL derivation for MTHPA.
Dermal and inhalation:
In accordance with column 2 of REACH Annex IX, the test repeated dose toxicity after dermal exposure (required in section 8.6) does not need to be conducted because there is another repeated toxicity robust study available for the oral route (see IUCLID5 section 7.5.1).
The most relevant exposure route of this substance to investigate systemic toxic effects is oral. In case of inhalation or dermal exposure, sensitising and irritating effects occur before systemic toxicity becomes relevant.
Repeated dose toxicity: via oral route - systemic effects (target organ) digestive: stomach
Justification for classification or non-classification
On the basis of the data submitted, classification of tetrahydromethylphthalic anhydride (MTHPA) as harmful and labelling with Xn, R 48/22 (Harmful: danger of serious damage to health by prolonged exposure if swallowed) according to the criteria given in Directive 67/548/EEC and with STOT rep. exp. cat 2 according to CLP (GHS) is not justified.
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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