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EC number: 201-964-7 | CAS number: 90-05-1
- 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
There was not a treatment related increase in stomach tumor incidence (papilloma and carcinoma) in rats orally exposed to 1000 mg/kg/day of
gaiacol when compared to controls in a study described by Hirose et al. (1989). Therefore no NOAEL can be identified for carcinogenic effect.
Key value for chemical safety assessment
Carcinogenicity: via oral route
Link to relevant study records
- Endpoint:
- carcinogenicity: oral
- Type of information:
- experimental study
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: The purity of the test substance was known. The protocol was described in details. The results concerning the forestomach and the glandular stomach were detailed but the other organs were not examined. The GLP were not mentioned.
- Qualifier:
- according to guideline
- Guideline:
- OECD Guideline 451 (Carcinogenicity Studies)
- Deviations:
- yes
- Remarks:
- only male were tested, only 1 dose instead of 3, small number of animals (16 instead of 50), and for 51 weeks (instead of 2 years). Moreover only forestomach and glandular stomach were examined.
- GLP compliance:
- not specified
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS:
- Source: Charles River Japan, Inc., Atsugi, Japan.
- Age at study initiation: 6 weeks old
- Weight at study initiation: no data
- Fasting period before study: no data
- Housing: 4 to 5 in plastic cage with wood chips for bedding
- Diet: Oriental MF basal diet (Oriental Yeast Co., Tokyo, Japan), ad libitum
- Water: tap water, ad libitum
- Acclimation period: no data
ENVIRONMENTAL CONDITIONS:
- Temperature (°C): 22-24°C
- Humidity (%): no data
- Air changes (per hr): air-conditioned room
- Photoperiod: 12h dark / 12h light
IN-LIFE DATES: no data - Route of administration:
- oral: feed
- Vehicle:
- not specified
- Details on exposure:
- - Diet preparation
Rate of preparation of diet (frequency): once a month
Mixing appropriate amounts with (Type of food): Oriental M powdered diet
Storage temperature of food: no data
- Vehicle: none - Analytical verification of doses or concentrations:
- not specified
- Duration of treatment / exposure:
- For 51 weeks
- Frequency of treatment:
- no data
- Post exposure period:
- no data
- Remarks:
- Doses / Concentrations:
1000 mg/kg bw/ day (estimated by calculation)
Basis:
nominal in diet - No. of animals per sex per dose:
- 16
- Control animals:
- yes, concurrent no treatment
- Observations and examinations performed and frequency:
- - body weights of animals and food consumption were measured once every 2 or 4 weeks.
- Cage side observations: No data
- Detailed clinical observations: No
Time schedule for examinations of morbidity and mortality: rats becoming moribund were killed for necropsy and all surviving animals were
sacrified under ether anesthesia at the end of week 52.
- Body weight: Yes
Time schedule for examinations: every 2 or 4 weeks
- Food consumption and compound intake: no data
Food consumption for each animal determined and mean daily diet consumption calculated as g food/kg body weight/day: No data
Compound intake calculated as time-weighted averages from the consumption and body weight gain data: No data
- Ophthalmoscopic examination: no data
- Haematology: no data
- Clinical chemistry: no data
- Urinalysis: no data
- Neurobehaviour: no data
- Organ weights: no data - Sacrifice and pathology:
- Sacrifice and pathology:
- Gross pathology: yes
- Histopathology: yes - Other examinations:
- Stomach, esophagus, intestines, liver, and kidney were removed. The liver and kidneys being weighed and fixed in 10% buffered formalin solution. The esophagus, stomach, and intestines were injected with formalin and later opened via an incision along the greater curvature. After fixation, six
sections each were cut from the anterior and posterior walls of the forestomach and glandular stomach.
Tissues were processed routinely for histopathological examination.
Animals which survived until the end of experiment were included in the effective numbers. - Statistics:
- Student's test and Fisher's exact test were used for statistical evaluation of the data.
- Body weight and weight changes:
- no effects observed
- Gross pathological findings:
- effects observed, treatment-related
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Details on results:
- Mild and moderate forestomach hyperplasia was found in 93.8% of the rats received guaiacol but papilloma and carcinoma were not detected.
Forestomach lesions were focal and characterized by downward basal cell growth.
However, no glandular stomach lesions in fundic or pyloric region were observed in rats given guaiacol. The authors concluded that guaiacol did not enhance forestomach and glandular stomach carcinogenesis. - Dose descriptor:
- NOAEL
- Sex:
- male
- Remarks on result:
- not determinable
- Remarks:
- no NOAEL identified. Effect type:carcinogenicity (migrated information)
- Conclusions:
- No treatment related increase in stomach tumor incidence.
- Executive summary:
In a carcinogenicity study (Hirose et al., 1989) 1.5% (corresponding to 1000 mg/kg bw/day) of guaicol in diet was administered to 16 male rats (Fisher 344) for 51 weeks. Mild and moderate forestomach hyperplasia was found in 93.8 % of the rats received guaiacol but papilloma and carcinoma were not detected. Forestomach lesions were focal and characterized by down ward basal cell growth. The LOAEL for non-carcinogenic effects is 1000 mg/kg bw/ day, based on calculation regarding forestomach lesions and hyperplasia.
At the dose tested, there was not a treatment related increase in stomach tumor incidence (papilloma and carcinoma) when compared to controls.
Reference
Summary of the study with other chemical agents:
Modifying effects of resorcinol, hydroquinone, p-tert-butylcatechol(PTBC), p-methylcatechol (PMC), and o-methylcatechol (guaiacol) on N-methyl-N'-nitro-N-nitrosoguanidine(MNNG)-induced forestomach and glandular stomach carcinogenesis were investigated in F344 rats. Groups of 15 to 16 male 6-wk-old animals were given a single intragastric administration of 150 mg/kg of body weight of MNNG and starting 1 wk later were administered powdered diet containing 0.8% resorcinol, 0.8% hydroquinone, 1.5% PTBC, 1.5% o-methylcatechol (guaiacol), 1.5% PMC, or basal diet alone for 51 wk. Additional groups of 10 to 15 rats each were treated with the phenolic compounds or received basal diet without prior carcinogen exposure. Histological examination after sacrificeat Wk 52 revealed that squamous cell carcinoma development in the forestomachs of rats treated with MNNG followed by PTBC (75%, P 0.001) or MNNG followed by PMC (100%, P 0.001) was significantly greater than in animals receiving MNNG alone (20%). Treatment with PMC alone also resulted in a 40% yield of papilloma. In the glandular stomach, incidences of adenomatous hyperplasias in rats treated with MNNG followed by PTBC (31.3%, P 0.05) or PMC (100%, P 0.001) and the incidence of adenocarcinomas in rats treated with MNNG followed by PMC (100%, P 0.001) were significantly higher than in controls. In addition, PMC alone induced a 100% yield of adenomatous hyperplasias and 6.7% of adenocarcinomas. Thus, the results demonstrated that PTBC and PMC treatment significantly enhances forestomach and glandular stomach carcinogenesis and that PMC itself may possess weak carcinogenic potential in these organs. The ortho-position appears to be important for this dihydroxybenzene activity
Justification for classification or non-classification
Additional information
Two studies were available, but only one, with reliability 2 was selected as a key study. The other one has the reliability 3 and was not taken into account. In this carcinogenicity study (Hirose et al., 1989) according to the OECD guideline 451, 1.5% (corresponding to 1000 mg/kg/day) of gaiacol in diet was administered to 16 male rats (Fisher 344) for 51 weeks. Mild and moderate forestomach hyperplasia was found in 93.8 % of the rats received guaiacol but papilloma and carcinoma were not detected. Forestomach lesions were focal and characterized by down ward basal cell growth.The LOAEL for non-carcinogenic effects is 1000 mg/kg bw/day, based on calculation, regarding forestomach lesions and hyperplasia.
At the dose tested, there was not a treatment related increase in stomach tumor incidence (papilloma and carcinoma) when compared to controls.
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