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EC number: 203-584-7 | CAS number: 108-45-2
- 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
Oral: NOAEL; 19/mo drinking water; mouse; no neoplastic effects were observed at any exposure level; reliability = 2.
NOT CLASSIFIED
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:
- supporting study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- study well documented, meets generally accepted scientific principles, acceptable for assessment
- Remarks:
- Non GLP. Only used 2 concentrations.
- Principles of method if other than guideline:
- Mice were administered test substance in drinking water for 78 weeks, after which all mice were given purified water until 83-85 weeks. Necropsy was performed on all mice and organ-weight ratios were determined. Histology was performed on selected tissues.
- GLP compliance:
- no
- Species:
- mouse
- Strain:
- B6C3F1
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Japan Inc.
- Age at study initiation: 4 weeks
- Housing: 6-10 mice housed in each aluminum cage, kept in an isorack
- Diet (e.g. ad libitum): Ad libitum
- Water (e.g. ad libitum):Ad libitum
- Acclimation period: 2 weeks
ENVIRONMENTAL CONDITIONS
- Temperature (°C): 24
- Humidity (%): 50% - Route of administration:
- oral: drinking water
- Vehicle:
- water
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: m-PDA dissolved in water, purified by the Milli-Q Reagent Water System, using a magnetic stirrer to prepare a 1% soultion. This solution was stored at 4 degrees C before use. Mice were given 0.04 or 0.02% m-PDA. Each cage of mice was given 30-50 ml (5 ml per mouse) of the solution daily except on Saturday, when double volume was given for 2 days. Remaining water was measured daily so that the mean daily water consumption for each cage of mice could be calculated and these means were averaged to give the daily consumption by mice of each sex in each treatment group. Dosages were increased to 6 mL per mouse at week 39 and then increased to 7 mL at week 45. Treatment continued for 78 weeks, after which all groups were given purified water until 83-85 weeks.
- Duration of treatment / exposure:
- 78 weeks
- Frequency of treatment:
- Once daily except on Saturdays when double the volume was given for 2 days.
- Post exposure period:
- 5-7 weeks
- Remarks:
- Doses / Concentrations:
0.02 or 0.04%
Basis: nominal in water - Remarks:
- Doses / Concentrations:
23 mg/kg bw/day for females and 19.8 mg/kg bw/day for males at the 0.02 % dose level and 41.8 mg/kg bw/day for females and 38.2 mg/kg bw/day for males at the 0.04 % dose level.
Basis: calculated intake - No. of animals per sex per dose:
- 59 female and 56 male were used for the 0.04 % concentration and 50 for each sex for the 0.02 % concentration.
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: On the basis of the results of a preliminary 25 week subchronic test using levels of 0.01-0.16 % in the drinking water.
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: No data.
DETAILED CLINICAL OBSERVATIONS: No data.
BODY WEIGHT: Yes.
- Time schedule for examinations was once a week for the first month and once a month for the remainder of the study.
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): Yes.
- Time schedule for examinations was daily.
- Sacrifice and pathology:
- Autopsy performed on all mice. The organ-weight ratios were determined. The liver, lungs, spleen, bone marrow, lyph nodes, pancreas, kidneys, stomach, small and large intestines, heart, urinary bladder, thymus adrenals, slaivary glands, thyroid, brain, pituitary, ovaries, testes, sternum, skin and tumours were fixed in 10% formalin solution, embedded in paraffin, cut into 5um sections and stained routinely with haematoxylin and eosin for histological examination.
- Statistics:
- The significance of differences in the incidences of tumours, mean values for daily intake of m-PDA, body weights, weights for organs and organ-weight indices were evaluated by the chi-square test.
- Clinical signs:
- effects observed, treatment-related
- Mortality:
- mortality observed, treatment-related
- Description (incidence):
- Survival rates at the end of the experiment were more than 86% in all groups. Two to seven mice from each group were killed a few weeks before the end of the treatment mainly due to morbidity from tumours.
- Body weight and weight changes:
- effects observed, treatment-related
- Description (incidence and severity):
- Mice in the 0.04% groups of both sexes showed lower rates of weight gain than the controls and the mean weights at the end of treatment were 66 and 83% of the control values, in females and males. Female mice in the 0.02% group also showed lower weight gains than the controls.
- Water consumption and compound intake (if drinking water study):
- effects observed, treatment-related
- Description (incidence and severity):
- Daily intake of drinking water was reduced in mice of the treated groups of both sexes when compared with that of the controls. There was, however, no significant difference in drinking water intake between mice of the 0.02 and 0.04 % groups for either sex. The calculated intake of test substance was 23 mg/kg bw/day for females and 19.8 mg/kg bw/day for males at the 0.02 % dose level and 41.8 mg/kg bw/day for females and 38.2 mg/kg bw/day for males at the 0.04 % dose level.
- Organ weight findings including organ / body weight ratios:
- effects observed, treatment-related
- Description (incidence and severity):
- Increases of the weight of the liver and spleen relative to body weight in the treated female mice.
- Gross pathological findings:
- effects observed, treatment-related
- Description (incidence and severity):
- None that significantly differed from control, in most cases numbers were lower for treated groups. The incidences of hepatocellular tumours were significantly lower in all the groups ingesting m-PDA than in the control groups and the incidences of hyperplastic liver nodules and lung adenomas were significantly lowere than those in controls, in control males alone.
- Histopathological findings: non-neoplastic:
- effects observed, treatment-related
- Description (incidence and severity):
- Macroscopically, the skin, liver, spleen, kidneys and bone marrow were darker in colour in mice receiving 0.04% of the test substance.
- Histopathological findings: neoplastic:
- no effects observed
- Dose descriptor:
- NOAEL
- Effect level:
- 38.2 mg/kg bw/day
- Sex:
- male
- Basis for effect level:
- other: No neoplastic effects observed at any dose level. The calculated intake of test substance was 38.2 mg/kg bw/day for males at the 0.04 % dose level.
- Dose descriptor:
- NOAEL
- Effect level:
- 41.8 mg/kg bw/day
- Sex:
- female
- Basis for effect level:
- other: No neoplastic effects observed at any dose level. The calculated intake of test substance was 41.8 mg/kg bw/day for females at the 0.04 % dose level.
- Conclusions:
- No significant differences in carcinogenic effects was noted between treated and control groups.
- Executive summary:
Male and female mice were exposed to the test substance in drinking water for 78 weeks at either 0.02 % or 0.04%. The calculated intake of test substance was 23 mg/kg bw/day for females and 19.8 mg/kg bw/day for males at the 0.02 % dose level and 41.8 mg/kg bw/day for females and 38.2 mg/kg bw/day for males at the 0.04 % dose level. No significant differences in carcinogenic effects was noted between treated and control groups. The NOAEL for males was 38.2 mg/kg bw/day and for females was 41.8 mg/kg bw/day.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 38.2 mg/kg bw/day
Justification for classification or non-classification
Based on results of a repeated drinking water study, the substance does not need to be classified for carcinogenicity according to EU Classification, Labelling and Packaging of Substances and Mixtures (CLP) Regulation (EC) No. 1272/2008.
Additional information
Male and female mice were exposed to the test substance in drinking water for 78 weeks at either 0.02% or 0.04%. The calculated intake of test substance was 23 mg/kg bw/day for females and 19.8 mg/kg bw/day for males at the 0.02% dose level and 41.8 mg/kg bw/day for females and 38.2 mg/kg bw/day for males at the 0.04% dose level. No significant differences in carcinogenic effects was noted between treated and control groups. Based on this information, the NOAEL for carcinogenicity in males was 38.2 mg/kg bw/day and in females was 41.8 mg/kg bw/day.
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