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EC number: 701-257-8 | CAS number: -
- 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
- Type of information:
- experimental study
- Adequacy of study:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: non-standard study; non-GLP
- Objective of study:
- toxicokinetics
- Principles of method if other than guideline:
- other: toxicokinetic study
Mesamoll concentration was measured in fat and liver tissue at different timepoints during / after dosing - GLP compliance:
- not specified
- Species:
- rat
- Strain:
- Wistar
- Sex:
- male
- Route of administration:
- other: gavage/feed
- Vehicle:
- other: Lutrol
- Duration and frequency of treatment / exposure:
- Experiment1)
Single dose; 100 mg/kg; animals were killed 1, 3, 7, 14, 21 and 34 days after dosing
Experimet 2)
Single dose 1000 mg/kg; animals were killed 1, 3, 7, 14, 21 and 34 days after dosing
Experiment 3)
rats were fed diet containing 100 ppm compound for 49 days. Animals were sacrificed on day 1,3, 7, 14, 21 and 43 day.
Experiment 4a)
rats were fed diet containing 1000 ppm compound for 49 days. Animals were sacrificed on day 1,3, 7, 14, 21, 28, 35, 42 and 49. (see experiment 3)
Experiment 4b)
rats were fed diet conaining 1000 ppm compound for 27 days; thereafter rats were fed a diet without Mesamoll. Animals were sacrificed on day 1,3, 7, 14, 21, 28, and 43. - Remarks:
- Doses / Concentrations:
100 mg/kg bw and 1000 mg/kg bw. (gavage study); 100 ppm and 1000 ppm feeding studies. - No. of animals per sex per dose / concentration:
- 30/sex/dose (gavage study); 30/sex/dose (feeding study 100 ppm); 50/sex/dose (feeding study 1000 ppm).
- Control animals:
- yes
- Details on excretion:
- 20 - 30 % of the dose was excreted in the feces within 24 h.
- Toxicokinetic parameters:
- half-life 1st: The half-life of Mesamoll in fat tissue after single oral application 1000 mg/kg was 8 days.
- Toxicokinetic parameters:
- half-life 2nd: The half-life of Mesamoll in fat tissue after repeated oral application of 1000 mg/kg was 15 days.
- Toxicokinetic parameters:
- other: No accumulation was observed in the liver. 20 - 30 % of the dose was excreted in the feces within 24 h.
- Executive summary:
The half-life of Mesamoll in fat tissue after single oral application and repeated oral application of 1000 mg/kg was 8 days and 15 days, respectively. No accumulation was observed in the liver. 20 - 30 % of the dose was excreted in the feces within 24 h.
Reference
Mesamoll concentration in the liver was low in all experiments (actual concentration below or slidely above LOD)
Mesamoll concentrations in fat:
Experiment 1) Cmax 22 µg/g fat (day 3); Mesamoll concentration below LOD on day 14
Experiment 2) Cmax 65 µg/g fat (first timepoint measured; day 1); elemination half-life 8 days; 20 -30% of dose eleminated by feces during the first 24 h.
Experiment 3) Mesamoll concentrations in fat increased linear over time until the end of the experiment
Experiment 4a) Mesamoll concentrations in fat increased linear over time until day 21 (ca. 235 µg/g fat) and slightly increased therafter (ca. 290 µg/g fat on day 49).
Experiment 4b) Elemination half-life: approx. 15 days
Description of key information
The half-life of Mesamoll in fat tissue after single oral application
and repeated oral application of 1000 mg/kg was 8 days and 15 days,
respectively.
No accumulation was observed in the liver. 20 - 30 % of the dose was excreted in the feces within 24 h.
Key value for chemical safety assessment
- Bioaccumulation potential:
- high bioaccumulation potential
Additional information
Mesamoll concentration in the liver and fat were investigated in limited experiments by Schmidt 1975. Rats were dosed with Mesamoll by gavage in acute experiments and in feeding experiments up to 49 days. No significant Mesamoll concentrations were reported in the liver in any experiment. After single dosing with 1000 mg/kg the Cmax concentration in fat was 65 µg/g fat (day 1) and the elimination half-life reported was 8 days; 20 -30% of dose was eliminated by feces during the first 24 h. Cmax value increased to 235 µg/g fat with a half-life of 15 days after exposure to 1000 ppm Mesamoll in the diet for 27 days. The feeding studies showed an increase of tissue concentrations after prolonged exposure. In the 1000 ppm dose group a concentration of 280 µg/g fat tissue was measured after 7 weeks of exposure (Schmidt U., Bayer AG, 1975). There are no toxicokinetic studies after the dermal application of Mesamoll. Based on low water solubility (0.002 g/l; 22 oC) and the high logPow value dermal absorption is anticipated to be low. This assumption is in line with an acute dermal toxicity experiment in which no symptoms of toxicity were reported up to the highest dose tested to (1055 mg/kg). Conclusion: Overall, based on the limited data available Mesamoll is absorbed after oral intake and there is an accumulation potential which is in line with the high logPow > 6.
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