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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

Exposure related observations in humans: other data
Administrative data
- Endpoint:
- exposure-related observations in humans: other data
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
Cross-reference
- Reason / purpose for cross-reference:
- reference to same study
Data source
Reference
- Reference Type:
- publication
- Title:
- Exposure assessment and sensitization in workers exposed to organic acid anhydrides
- Author:
- Drexler, H. et.al.
- Year:
- 2 000
- Bibliographic source:
- Int. Arch. Environ. Health, (2000) 73 228-234
Materials and methods
- Type of study / information:
- Biomonitoring (Human urine)
- Endpoint addressed:
- respiratory sensitisation
Test guideline
- Qualifier:
- no guideline available
- Principles of method if other than guideline:
- No information on guideline. For details on method please refer to IUCLID5 dossier.
- GLP compliance:
- no
Test material
- Reference substance name:
- Tetrahydromethylphthalic anhydride
- EC Number:
- 234-290-7
- EC Name:
- Tetrahydromethylphthalic anhydride
- Cas Number:
- 11070-44-3
- IUPAC Name:
- 3a-methyl-3a,4,5,6-tetrahydro-2-benzofuran-1,3-dione
- Details on test material:
- - Name of test material (as cited in study report): MTHPA
Constituent 1
Method
- Ethical approval:
- not specified
- Details on study design:
- no details given
- Exposure assessment:
- measured
- Details on exposure:
- TYPE OF EXPOSURE: inhalation at the factory
TYPE OF EXPOSURE MEASUREMENT: Biomonitoring (urine)
Results and discussion
- Results:
- Two hundred and nineteen workers form three plant exposed tetrahydromethyl-1,3-isobenzofuranedione (MTHPA) used as a hardener in an epoxy resin system were reported. The exposure assessment included stationary and ambient air monitoring and biological monitoring (metabolites in urine). In plant A 20, in plant B 86 and in plant C 113 workers were examined by a physician. The ambient air concentration of MTHPA were 37.2 and 58.5 ug/m3 in plant A (n=2), ranged from <0.5-26.2 in plant B (n=5) and from 2.1-57.9 in plant C with stationary collecting, and from 8-45 (n=6), from <4.7-35.7 (n=3), and from 2-37.8 (n=3) with personal air collection. The metabolites of MTHPA in urine (in nmol/nmol creatinine) ranged from 5.7-645 in plant A, from <1-213 in plant B and from 0.1-830 in plant C. The prevalence of sensitization was 35% in plant A, 21% in plant B and 29% in plant C. Comparing the prevalence of sensitization and the results of biological monitoring, between the three plants, it is found that sensitization increased with increasing exposure. Therefore, biological monitoring is a useful tool in the exposure assessment of MTHPA.
Applicant's summary and conclusion
- Conclusions:
- Comparing the prevalence of sensitization and the results of biological monitoring, between the three plants, it is found that sensitization increased with increasing exposure. Therefore, biological monitoring is a useful tool in the exposure assessment of MTHPA.
- Executive summary:
Two hundred and nineteen workers form three plant exposed tetrahydromethylphthalic anhydride (MTHPA) used as a hardener in an epoxy resin system were reported. The exposure assessment included stationary and ambient air monitoring and biological monitoring (metabolites in urine).
In plant A 20, in plant B 86 and in plant C 113 workers were examined by a physician. The ambient air concentration of MTHPA were 37.2 and 58.5 ug/m3 in plant A (n=2), ranged from <0.5-26.2 in plant B (n=5) and from 2.1-57.9 in plant C with stationary collecting, and from 8-45 (n=6), from <4.7-35.7 (n=3), and from 2-37.8 (n=3) with personal air collection. The metabolites of MTHPA in urine (in nmol/nmol creatinine) ranged from 5.7-645 in plant A, from <1-213 in plant B and from 0.1-830 in plant C. The prevalence of sensitization was 35% in plant A, 21% in plant B and 29% in plant C. Comparing the prevalence of sensitization and the results of biological monitoring, between the three plants, it is found that sensitization increased with increasing exposure. Therefore, biological monitoring is a useful tool in the exposure assessment of MTHPA.
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