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EC number: 203-571-6 | CAS number: 108-31-6
- 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
Link to relevant study record(s)
- Endpoint:
- basic toxicokinetics in vivo
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Reason / purpose for cross-reference:
- reference to same study
- Objective of study:
- distribution
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- Plasma was obtained from dogs on a 90 day feeding study at 60 mg/kg/day of maleic anhydride. The plasma levels of maleic anhydride was determined and the data analyzed by a nonlinear parameter estimation program.
- GLP compliance:
- not specified
- Radiolabelling:
- no
- Species:
- dog
- Strain:
- not specified
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- not specified
- Route of administration:
- oral: feed
- Vehicle:
- not specified
- Details on exposure:
- not specified
- Duration and frequency of treatment / exposure:
- 90 days
- Dose / conc.:
- 60 mg/kg bw/day (nominal)
- No. of animals per sex per dose / concentration:
- 4
- Control animals:
- no
- Details on study design:
- The plasma samples were obtained after a 12 hours fast at approximately 8 AM on days 3, 12, 29, and 90 of the 90 day feeding study.
Measurements of plasma concentration of maleic anhydride were made by gas chromatography/mass spectrometry using the method of Hermann and Braun . - Details on absorption:
- An uptake rate constant (Ka) of 0.00349 per day was calculated assuming an one-compartment model.
- Details on excretion:
- An elimination rate constant (Ke) of 0.0832 per day was calculated assuming an one-compartment model.
- Toxicokinetic parameters:
- other: Ka
- Remarks:
- Uptake rate constant (Ka) = 3.49 x 10^-3 ± 6.82 x 10^-4 per day
- Toxicokinetic parameters:
- other: Ke
- Remarks:
- Clearance (Ke) = 8.32 x 10^-2 ± 2.00 x 10^-2 per day
- Metabolites identified:
- not measured
- Conclusions:
- Under the conditions of the study, no bioaccumulation potential was observed. An uptake rate constant of 0.00349 per day and an elimination rate constant of 0.0832 per day were calculated assuming an one-compartment model.
- Executive summary:
In a toxicokinetic study, dogs (n= 4/sex) were fed 60 mg/kg/day maleic anhydride for 90 days. The plasma levels of maleic anhydride were determined by gas chromatography/mass spectrometry using the method of Hermann and Braun. An uptake rate constant of 3.49 x 10-3per day and an elimination rate constant of 8.32 x 10-2per day were calculated assuming a one-compartment model. According to the model, 99% of steady state was reached by day 55 of the study. The dogs were maintained at steady state for the final 35 days of study.
Reference
Table 1: Maleic anydride plasma concentration (ppm), dogs fed 60 mg/kg/day:
mean maleic anhydride plasma levels in ppm | |||||
mean | Day 1 | Day 3 | Day 12 | Day 29 | Day 90 |
males | 0.44 | 0.84 | 1.35 | 2.03 | 2.43 |
females | 0.39 | 0.69 | 1.65 | 2.33 | 2.8 |
Table 2: Time to "x" Percent of steady state:
x | Time (Days) |
50 | 8.3 +/- 2.0 |
75 | 16.7 +/- 4.01 |
90 | 27.6 +/- 6.65 |
95 | 36.0 +/- 8.66 |
99 | 55.3 +/- 13.3 |
99.5 | 64.0 +/- 15.3 |
Table 3: Percentage of steady state after "x" Days:
x | % |
20 | 81 +/- 7.6 |
40 | 96.4 +/- 2.9 |
60 | 99.3 +/- 0.80 |
90 | 99.94 +/- 0.10 |
100 | 99.976 +/- 0.04 |
Description of key information
Under the conditions of the study, no bioaccumulation potential was observed. An uptake rate constant of 0.00349 per day and an elimination rate constant of 0.0832 per day were calculated assuming an one-compartment model.
Key value for chemical safety assessment
- Bioaccumulation potential:
- no bioaccumulation potential
Additional information
The distribution of maleic anhydride in dogs was tested in a 90-day feeding study (60 mg/kg bw maleic anhydride). The plasma levels of maleic anhydride were determined by gas chromatography/mass spectrometry using the method of Hermann and Braun.
On day 1, the maleic anhydride plasma levels in the males ranged from 0.19 ppm to 0.78 ppm and in the females from 0.1 ppm to 0.88 ppm. Interpolation revealed that the blood concentration reached a plateau on day 55.After 90 days the plasma levels in the males ranged from 1.8 to 3.4 ppm and in the females from 1.9 to 3.5 ppm. The uptake rate constant (Ka) was calculated to be 0.00349 per day, the elimination rate (Ke) 0.0832 per day.
Considering the chemical structure of maleic anhydride, metabolism may consist of the hydrolysation to maleic acid in aqueous solutions and epoxidation of the double bond (hydrolysis; Bunton et al, 1963). These reactions lead to more polar and more water soluble products than the parent chemical (maleic acid is soluble in water (400 g/L at 20°C) and has a log Po/w of -2.61 at 25°C (experimental value; OECD SIDS, 2004) and are expected to be excreted predominantly via the urine. The epoxide is a reactive metabolite, but studies on genotoxicity (Ames test, chromosomal aberration test in vivo) were negative, i.e. there is no indication of a reactivity of maleic anhydride or its metabolites under the test conditions.
The toxicokinetic study showed, that maleic anhydride was ingested and distributed in the body. However, the elimination rate was considerably higher than the uptake rate. Taking also into account the log Po/w, the water solubility of the hydrolysation product maleic acid and the considerations on the metabolism, accumulation of maleic anhydride is considered to be unlikely.
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