Registration Dossier
Registration Dossier
Data platform availability banner - registered substances factsheets
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.
The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.
Diss Factsheets
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 200-362-1 | CAS number: 58-08-2
- 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)
Description of key information
Key value for chemical safety assessment
Additional information
- Humans are characterized by the importance of 3-methyl demethylation leading to the formation of paraxanthine and especially metabolites thereof through subsequent metabolic steps. The main urinary metabolites in humans are 1-methyluric acid, 1-methylxanthine, and 1,7-dimethyluric acid.
- In rats and mice, the metabolism of caffeine is predominantly via theobromine and theophylline. The main urinary metabolites are 1,3-dimethyluracil, paraxanthine, trimethyluric acid, theophylline, and theobromine.
Data on toxicokinetics, absorption, distribution, metabolism, and excretion of caffeine have been well summarized in reviews/review-like-publications of good reliability Arnaud, 1993; IARC, 1991). However; it cannot be stated whether the studies/results cited in these publications and listed herein do satisfy the requirements of current guidelines.
METABOLISM
The main urinary metabolites of caffeine in humans are 1-methyluric acid, 1-methylxanthine, and 1,7-dimethyluric acid.
The main urinary metabolites of caffeine in rats and mice are 1,3-dimethyluracil, paraxanthine, trimethyluric acid, theophylline, and theobromine.
Caffeine metabolism is qualitatively relatively similar in animals and humans. The main metabolic pathways are demethylation and hydroxylation of the 8-position leading to the formation of the respective uracil and uric acid derivatives. There are, however, some quantitative differences in the metabolic profile:
Caffeine metabolism decreases during pregnancy, resulting in higher serum concentrations.
Caffeine absorption and distribution from gastrointestinal tract is rapid and complete and it is distributed to all body fluids and appeared in all tissues within 5 minutes.
There is no accumulation of caffeine or its metabolites in any organ even after high doses.
No blood-brain barrier or placental barrier was detected.
The fraction bound to plasma albumin varies from 10 to 30%.
Caffeine is metabolized by liver microsomal mixed-function oxidases and can increase metabolizing enzymes at high doses (75 mg/kg).
EXCRETION / ELIMINATION
In both humans and rats, excretion of caffeine mainly occurs via urine (about 90% dose in rats; > 95% in humans).
It is eliminated by various species by first-order kinetics, described by a one-compartment open model system.
The half-life for several species ranged between 0.7 to 12 h (rats to baboons) and a mean volume of distribution of 0.8 l/kg has been reported for various species. Decreased as well as increased half-lives were found in pregnant animals.
Caffeine is eliminated in animals by biotransformation to dimethylxanthines, dimethyl- and monomethyluric acids and uracil derivatives. Differences in formation and elimination of metabolites were noted in rats, mice and Chinese hamsters and mainly in monkeys, where it is almost completely metabolized to theophylline. In contrast, the acetylated uracil derivative, 5-acetylamino-6-formylamino-3-methyluracil, one of the most important metabolites in human, was not found in rodents or other species.
DEMRMAL ABSORPTION
In vitro percutaneous absorption of caffeine through human and rat skin was investigated in the study of van de Sandt et al., 2004. The maximum absorption rate through rat skin (6.82µg/cm²/h) was clearly higher than the mean value for human skin (2.24 ± 1.43 µg/cm²/h). The amount in the receptor fluid after 24 h was 24.5 ± 11.6% and53.7 %of the dose applied in human and rat skin, respectively. The total penetration (% of dose) through rat skin (61.3 ± 4.0 %) was also higher than the mean value for human skin (26.75 ± 10.9 %). Skin thickness only slightly influenced the absorption of caffeine.
In conclusion there is a total absorption of the human skin of about 25 %.
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.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.