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Diss Factsheets
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EC number: 247-094-1 | CAS number: 25550-51-0
- 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
![](https://echa.europa.eu./o/diss-blank-theme/images/factsheets/A-REACH/factsheet/print_toxicological-information.png)
Endpoint summary
Administrative data
Description of key information
Following a read-across on data available for 4-MHHPA obtained in a subchronic oral toxicity study in rats according to EU test methods and OECD guidelines the NOAEL for MHHPA for males and females was determined to be 450 mg/kg bw/day.
Key value for chemical safety assessment
Repeated dose toxicity: via oral route - systemic effects
Link to relevant study records
- Endpoint:
- sub-chronic toxicity: oral
- Type of information:
- read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Justification for type of information:
- REPORTING FORMAT FOR THE ANALOGUE APPROACH
Please refer to IUCLID Section 13. - Reason / purpose for cross-reference:
- read-across source
- Key result
- Dose descriptor:
- NOAEL
- Effect level:
- 450 mg/kg bw/day (nominal)
- Based on:
- test mat.
- Sex:
- male/female
- Basis for effect level:
- other: No adverse effects observed.
- Key result
- Critical effects observed:
- no
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 450 mg/kg bw/day
- Study duration:
- subchronic
- Species:
- rat
- Quality of whole database:
- Well described GLP compliant study conducted to recognized international test guidelines.
Repeated dose toxicity: inhalation - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: inhalation - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - systemic effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Repeated dose toxicity: dermal - local effects
Endpoint conclusion
- Endpoint conclusion:
- no study available
Additional information
Long-term toxicity of MHHPA following repeated oral administration was assessed from read-across data available for the structural analogue 4-MHHPA as similar chemical and toxicological properties were assumed.
Key study:
The structural analogue 4-MHHPA was examined for its possible health hazards after repeated exposure in a sub-chronic GLP compliant study according to OECD 408. A four weeks recovery period in the high dose and control dose animals was included in order to assess reversibility, persistence or delayed occurrence of potential toxicological effects.
The test item was administered orally (by gavage) to male and female Han: WIST rats (n=15 animals/sex in the control and high dose groups, n= 10 animals/sex in the low and middle dose groups) once a day at 0 (vehicle control), 50,150 and 450 mg/kg bw/day doses (dose volume of 5 mL/kg bw) for 90 or 91 days. Five animals/ sex in the control and high dose groups assigned to the recovery groups were treated identically up to Day 89 then they were observed without administration for four weeks (recovery observations). Concentrations of the test item in the dosing formulations varied between ranges of 93 % and 108 % of nominal concentrations at each analytical occasion confirming proper dosing.
Animals were observed for mortality twice a day during the course of the study. Daily general clinical observations and weekly detailed clinical observations were performed. A functional observation battery was conducted in the last week of treatment. The body weight was determined twice weekly for four weeks (weeks 1-4) then once weekly during the course of the treatment and recovery periods. Food consumption was measured and evaluated weekly. The estrous cycle of each female animal was examined for two weeks before necropsy and for two weeks before the end of the recovery period. Clinical pathology examinations (including hematology, blood coagulation and clinical chemistry) and gross pathology were conducted one day after the last treatment and at the end of the recovery period. The absolute and relative weights of selected organs were measured. Sperm examinations were conducted in animals of the control and high dose groups at termination of the treatment. Full histopathology was performed on the preserved organs or tissues of the animals of the control and high dose groups including recovery groups. Additionally, liver and seminal vesicles in single male animals at 150 mg/kg bw/day were processed and evaluated histologically on the basis of necropsy observations.
No animals died during the course of the study and no signs of toxicity related to the test item were detected at any dose level at the daily and detailed weekly clinical observations or in the course of the functional observation battery. The behavior and physical condition of animals were normal during the entire observation period. Test item related nuzzling up the bedding material and salivation were observed in male animals at 50, 150 and 450 mg/kg bw/day with different incidence and duration during the treatment period. Animals salivated shortly after the daily administration of the test item and it ceased shortly thereafter and was therefore judged to be not adverse. The body weight development was unaffected by the test item at 50, 150 and 450 mg/kg bw/day (male and female animals) during the 3-month treatment period. The mean body weight was similar to the control in male and female animals at 450 mg/kg bw/day during the recovery period. Slight changes in the mean body weight gain were detected in male recovery animals. As the mean body weight remained similar to the control group, the changes were considered to be toxicologically not relevant. The mean daily food consumption was comparable in animals of the control and test item treated groups and no abnormalities in the eyes of animals in the high dose group at termination of the treatment were observed. No test item related influence on the estrous cycle was detected and hematological investigations did not reveal test item or treatment related changes in the examined parameters in male or female animals at any dose level. No pathologic test item effect was detected at the evaluation of clinical chemistry parameters and T4 and TSH levels were comparable in the control and test item treated groups at the end of the treatment and recovery periods. Test item induced macroscopic changes and changes in organ weights were not detected at termination of the treatment period or at the end of the recovery period. Sperm analysis did not reveal any test item related influence on the sperm parameters (count, motility and morphology) at 450 mg/kg bw/day. Histological examination did not reveal severe or permanent test item related lesions in the organs or tissues of animals administered with 450 mg/kg bw/day dose at termination of the treatment or at the end of the recovery period. Slight vacuolation of hepatocytes in the centrilobular region (hepatic lipidosis) in 3/10 female animals at 450 mg/kg bw/day was detected. As no such effect was observed in the recovery group, the observation was considered a mild, reversible and non-adverse test item related lesion.
Under the conditions of the present study, the test item did not cause adverse effects in male or female Han: WIST rats after consecutive 90/91-day oral (by gavage) administration at 50, 150 or 450 mg/kg bw/day. Vacuolation of hepatocytes in the centrilobular region (hepatic lipidosis) in some female animals at 450 mg/kg bw/day was assumed to be indicative of test item influence and was considered as a mild, reversible lesion in the female liver. Based on these observations the No Observed Adverse Effect Level (NOAEL) was determined to be 450 mg/kg bw/day for male and female Han:WIST rats.
Supporting study:
The sub-acute oral toxicity of 4-MHHPA was investigated in rats according to EU test methods and OECD guidelines. No signs of toxicity were observed during the "in-life" phase of the study. Post mortem macroscopic observations, absolute and relative organ weights and microscopic examination did not show any changes indicating systemic toxicity of the substance. Thickening of the forestomach mucosa (non-glandular region) was noted in the majority of animals treated with 450 mg/kg bw/day and in 1 female treated with 150 mg/kg bw/day. Microscopic examination of these lesions revealed a slight to mild squamous hyperplasia of the forestomach mucosa (non-glandular region), often associated with submucosal oedema, inflammatory reaction or erosion of the gastric mucosa. These changes were no longer present after 2 weeks of recovery. According to the results of the read across the NOAEL for MHHPA was considered 450 mg/kg bw/day and the NOEL for MHHPA was considered 50 mg/kg bw/day.
Conclusion:
As an overall conclusion no adverse effects regarding repeated dose toxicity have been identified and the NOAEL was determined to be 450 mg/kg bw/day for the structural analogue hexahydro-4 methylphthalic anhydride (4-MHHPA). According to the results of the read across the NOAEL of 450 mg/kg bw/d is considered for the registration substance MHHPA for repeated dose toxicity.
Justification for classification or non-classification
Based on the results obtained from repeated dose toxicity testing, MHHPA was not classified and labelled according to Regulation (EC) No. 1272/2008 (CLP).
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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