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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
Carcinogenicity
Administrative data
Description of key information
In a carcinogenicity study (Mohr et al., 1984), food grade Caffeine (purity not further stated) was administered to male and female Sprague-Dawley rats in water at dose levels of 0, 200, 430, 930, or 2000 ppm for 104 weeks.
A NOAEL / LOAEL was not established.
At the doses tested, there was not a treatment related increase in tumor incidence when compared to controls. Exposure to caffeine for 2 years did not enhance or induce neoplasia in the Sprague-Dawley rats.
Key value for chemical safety assessment
Justification for classification or non-classification
There is no need to classify Caffeine for carcinogenicity according to the Directive 67/548/EC or GHS criteria.
Additional information
In a carcinogenicity study (Mohr et al., 1984), food grade Caffeine (purity not further stated) was administered to male and female Sprague-Dawley rats in water at dose levels of 0, 200, 430, 930, or 2000 ppm (0, 12, 26, 49, 102 mg/kg bw/d for males; 0, 15, 37, 80, 170 mg/kg bw/d for females) for 104 weeks, with interim sacrifices being conducted after 3, 6, and 12 months of treatment. 50 rats/sex/dose were used for the dosed groups; 100 rats/sex were used for the control group.
There were no compound related effects in mortality, clinical signs, hematology, clinical chemistry, or gross and histologic pathology. Body-weight gain was considerably depressed by high caffeine intake (especially at 930 and 2000 mg/litre). Terminal body weights of treated animals were lower than terminal control weights by 25% at the highest dose and by approximately 11% at the next lower level. There was no difference between the sexes in this respect. Although food consumption was somewhat lower at the highest caffeine dose, there was no effect on the efficiency of food utilization. No data are reported on organ weights.
A NOAEL / LOAEL was not established.
At the doses tested, there was not a treatment related increase in tumor incidence when compared to controls. No unusual tumours or sites of origin for neoplastic growth were found in any animal receiving caffeine. Neoplasms found in various organs showed incidences not exceeding those seen in controls. Thus, exposure to caffeine for 2 years did not enhance or induce neoplasia in the Sprague-Dawley rats.
This carcinogenicity study in the rat is acceptable and does satisfy the guideline requirement for a carcinogenicity study (OECD 451) in rats.
HUMAN DATA:
Heavy coffee consumption tends to be associated with other risk factors for various types of cancer, e.g. smoking, alcohol, physical inactivity (Giovannucci, 1998). Residual confounding might explain weak positive associations between caffeine consumption and lung, bladder, or pancreas cancer.
Based on the currently available literatureNehlig and Debry’s(1996)conclusion that in the doses usually consumed by man, coffee does not have any potential carcinogenic effect can still be supported.
Whether the consumption of doses higher than 4 mg/kg/day slightly enhances or lowers the risk for some cancer types is currently not clear.
The IARC evaluates the carcinogenicity in humans of caffeine as inadequate evidence (IARC 1991).
Different sites
The effect of caffeine consumption (av. 317 mg/day) on mortality was evaluated in a historical cohort study of 10,064 diagnosed hypertensive individuals participating in the Hypertension Detection and Follow-up Program from 1973 to 1979. No evidence was found for an association between increased level of caffeine consumption (up to > 428 mg/day) and increased cancer mortality during the following four years(Martin et al., 1988).
Breast
Several case-control studies provided no association between coffee intake (up to³7 cups/day) and breast cancer risk(IARC, 1991).Also new case-control studies confirmed this result(Hunter, 1992, McLaughlin et al., 1992, Folsom et al., 1993, Levi et al., 1993, Smith et al., 1994, Tavani et al., 1998).
Colon
Cohort studies that addressed the issue of coffee drinking (up to³3 cups/day) and risk of cancer of the colon have generally been interpreted as showing no association. There are case-control studies that indicated inverse associations and others find a risk. Bias and confounding could not be excluded as the source of the apparent associations(IARC, 1991). In recent case-control and cohort studies no increased risk of colorectal cancer from caffeine intake (up to³7 cups/day) was found(Cipriani and Geddes, 1996, Giovannucci, 1998, Hartman et al., 1998, Tavani et al., 1997).The lower risk of colorectal cancer with high vs. low coffee consumption as determined in the meta-analysis byGiovannucci (1998)might be due to an avoidance of coffee by unidentified high-risk individuals, or due to enhanced colonic motility induced by coffee, or due to antimutagenic components in coffee (not necessarily caffeine).
Bladder
In cohort studies on coffee consumption neither an increase nor a decrease risk for bladder cancer was found. Several case-control studies showed a weak positive association, while others did not. Taken as a whole, the data are consistent with a weak positive relationship between coffee consumption (up to >5 cups/day) and the occurrence of bladder cancer, but the possibility that this is due to bias or confounding cannot be excluded(IARC, 1991).
Non-Hodgkin lymphoma, lung, pancreas
Cohort studies on the relationship between coffee consumption and pancreatic cancer did not report a significant association with increased consumption; any nonsignificant increase was reduced after adjustment for smoking. In an early case-control study a positive relationship between coffee consumption (up to³5 cups/day) and pancreatic cancer was reported. Several subsequent reports (coffee intake³7 cups/day) have been less positive overall. Potential biases associated with the comparability of case and control groups also complicate interpretation, and methodological problems were noted in some studies(IARC, 1991). A recent case-control study showed a U-shaped dose-response relationship between coffee intake (never, occasionally, and 3+ cups/day) and the relative risk for pancreatic cancer, suggesting a preventive effect of small amounts of coffee. However, the authors did no present data to verify this suggestion (Nishi et al., 1996).
In a case-control study no association between coffee consumption (up to 4 cups/day , resp. 2 or more cups/day) and non-Hodgkin´s lymphoma was found (Tavani et al., 1994). Concerning lung cancer, there have been reports of studies showing no or weak associations with the consumption of caffeine-containing drinks (Mendilaharsu et al., 1998, and others quoted byMendilaharsu et al., 1998,Jacobsen et al., 1986).Data are inadequate for an assessmentInformation 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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