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EC number: 215-138-9 | CAS number: 1305-78-8
- 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
Calcium (when administered orally in feed as Ca-lactate) is not carcinogenic. Neither toxicity nor carcinogenic activity was observed in rats.
The NOAEL of calcium oxide, converted from Ca taking into account the respective molecular weights, has been determined at 391 mg/kg bw/d.
Key value for chemical safety assessment
Carcinogenicity: via oral route
Link to relevant study records
- Endpoint:
- carcinogenicity: oral
- Type of information:
- migrated information: read-across from supporting substance (structural analogue or surrogate)
- Adequacy of study:
- key study
- Reliability:
- 2 (reliable with restrictions)
- Rationale for reliability incl. deficiencies:
- other: see 'Remark'
- Remarks:
- Under physiological conditions, the hydroxyl-ions released from burnt dolomitic lime following oral adminstration have been neutralised in the GI tract and are therefore not relevant for consideration of systemic toxicity. Therefore for assessment of any systemic effects of burnt dolomitic lime following administration via the oral route, the calcium ion Ca2+ is the chemical species of interest. In the current study, calcium was administered in the form of calcium lactate, the lactate ion being an integral component of mammalian energy metabolism and therefore toxicologically not relevant. The objective of the study was the evaluation of any effects of calcium. In view of the the limited relevance of the anionic counter-ions discussed here, calcium released both from calcium magnesium oxide and calcium lacatate can be considered as structurally equivalent, and the results of the study can be used by read-across.
- Qualifier:
- no guideline followed
- Principles of method if other than guideline:
- The long-term toxicity/carcinogenicity of calcium lactate, a food additive, was examined in F344 rats. Calcium lactate was given ad lib. in the drinking water at levels of 0, 2.5 or 5 % to groups of 50 male and 50 female rats for two years.
- GLP compliance:
- not specified
- Species:
- rat
- Strain:
- Fischer 344
- Sex:
- male/female
- Details on test animals or test system and environmental conditions:
- TEST ANIMALS
- Source: Charles River Japan Inc. (Kanagawa, Japan)
- Age at study initiation: 6 weeks old
- Housing: Rats were housed three (or four) males or five females per plastic cage
- Diet (ad libitum): Basal diet (CRF-1; Oriental Yeast Inc., Tokyo, Japan)
- Water (ad libitum): Distilled water containg calcium lactate
ENVIRONMENTAL CONDITIONS
- Temperature: 24 +/- 1 °C
- Relative humidity: 55 +/- 5 %
No further information on the test animals was stated. - Route of administration:
- oral: drinking water
- Vehicle:
- water
- Details on exposure:
- PREPARATION OF DOSING SOLUTIONS: Calcium lactate was dissolved in distilled water at levels of 0 (control), 2.5 or 5 %.
No further information on the exposure was stated.
- Analytical verification of doses or concentrations:
- not specified
- Details on analytical verification of doses or concentrations:
- No data
- Duration of treatment / exposure:
- 104 weeks
- Frequency of treatment:
- ad libitum
- Post exposure period:
- 9 weeks
- Remarks:
- Doses / Concentrations:
0, 2.5 or 5 % calcium lactate in distilled water
Basis:
nominal in water - No. of animals per sex per dose:
- 50 males / 50 females
- Control animals:
- yes, concurrent vehicle
- Details on study design:
- - Dose selection rationale: These dose levels were selected based on a 13-week subchronic toxicity study conducted prior to the present study (Matsushima et al., 1989)
- Positive control:
- No data
- Observations and examinations performed and frequency:
- CAGE SIDE OBSERVATIONS: Yes
- Time schedule: Daily
- Cage side observations included: Clinical signs and deaths were recorded
DETAILED CLINICAL OBSERVATIONS: No data
BODY WEIGHT: Yes
- Time schedule for examinations: Body weights were measured once a week for the first 13 week of the study, and every 4 weeks thereafter.
FOOD CONSUMPTION AND COMPOUND INTAKE (if feeding study):
- 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
FOOD EFFICIENCY:
- Body weight gain in kg/food consumption in kg per unit time X 100 calculated as time-weighted averages from the consumption and body weight gain data: No data
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study): Yes
- Time schedule for examinations: The calcium lactate solutions were replaced with freshly prepared solutions three times a week, on which occassions the amount of solution consumed was measured in order to calculate the intake of calcium lactate.
OPHTHALMOSCOPIC EXAMINATION: No data
HAEMATOLOGY: Yes
- Time schedule for collection of blood: At week 113
CLINICAL CHEMISTRY: Yes
URINALYSIS: No data
NEUROBEHAVIOURAL EXAMINATION: No data
No further information on observations and examinations performed and frequency was stated. - Sacrifice and pathology:
- GROSS PATHOLOGY: Yes
HISTOPATHOLOGY: Yes
At week 113, all survivng animals were killed and autopsied. An autopsy was immediatley performed on rats that died (or were killed when moribund) during the study and those killed at the end of the study. The animals were then examined macro- and mircoscopically for the presence of non-neoplastic and neoplastic lesions. All organs and / or tissues were routinely fixed in 10 % buffered formalin, sectioned and stained with haematoxylin and eosin.
No further information on sacrifice and pathology was stated. - Statistics:
- Statistical analyses were performed using Fisher's exact probability test and/or the chi-square test, and also the age-adjusted statistical test recommended by Peto et al. (1980).
- Clinical signs:
- no effects observed
- Mortality:
- no mortality observed
- Body weight and weight changes:
- effects observed, treatment-related
- Food consumption and compound intake (if feeding study):
- not specified
- Food efficiency:
- not specified
- Water consumption and compound intake (if drinking water study):
- no effects observed
- Ophthalmological findings:
- not specified
- Haematological findings:
- no effects observed
- Clinical biochemistry findings:
- no effects observed
- Urinalysis findings:
- not specified
- Behaviour (functional findings):
- not specified
- Organ weight findings including organ / body weight ratios:
- no effects observed
- Gross pathological findings:
- not specified
- Histopathological findings: non-neoplastic:
- no effects observed
- Histopathological findings: neoplastic:
- no effects observed
- Details on results:
- CLINICAL SIGNS AND MORTALITY
The mortality rate in high-dosed females was slightly higher than those in the two other groups. This difference, however, was not significant.
BODY WEIGHT AND WEIGHT GAIN
Calcium lactate inhibited the growth of rats of both sexes dose-dependently. A 13% decrease was observed in male and female rats of the high-dose group.
WATER CONSUMPTION AND COMPOUND INTAKE (if drinking water study)
Throughout the administration period, daily water consumption was almost constant in all groups of both sexes. From the water consumption data, total calcium lactate intakes (g/rat/2yr) were calculated:
Mean total calcium lactate intake:
5% dose: 625.4 g/rat
2.5 % dose: 329.4 g/rat
0 % dose: 0 g/rat
HAEMATOLOGY
No specific dose-related changes of haematological parameters were observed.
CLINICAL CHEMISTRY
No specific dose-related changes of biochemical parameters were observed.
ORGAN WEIGHTS
Females of the high-dose group exhibited slightly, but significantly, higher kidney weights. Histologically, however, there was no difference in the severity of chronic nephropathy. A significant dose-dependent increase was observed in the relative brain weights of both male and female rats although no histological change was detected.
HISTOPATHOLOGY: NON-NEOPLASTIC
A number of non-neoplastic lesions (e.g myocardial fibrosis, bile-duct proliferation, hepatic microgranulomas and chronic nephropathy) were observed in all groups, with no difference in their incidence and/or degrees.
HISTOPATHOLOGY: NEOPLASTIC
None of the experimental groups showed a significant increase in the incidence of any specific tumors compared with the corresponding control value, and also no positive trend was noted in the occurence of any tumour. However, male rats of the high-dose group showed a slightly higher incidence of pheochromocytomas and adrenal medullary hyperplasia. However, there were no carcinogenic effects observed. - Relevance of carcinogenic effects / potential:
- Calcium lactate did not cause toxicicity or carcinogenic activity in F344 rats.
This finding can be used for read-across to burnt dolomitic lime based on structural equivalence. - Dose descriptor:
- NOAEL
- Effect level:
- 2 150 mg/kg bw/day
- Sex:
- male
- Basis for effect level:
- other: This is the 5% calcium lactate dose level. The daily calcium lactate intakes of males in the 5 % group was 860 mg per rat. Assuming an average weight of 400 g for male rats, this intake would correspond to calcium lactate dose of 2150 mg/kg bw/day.
- Remarks on result:
- other: Effect type: carcinogenicity (migrated information)
- Dose descriptor:
- NOAEL
- Effect level:
- 2 280 mg/kg bw/day
- Sex:
- female
- Basis for effect level:
- other: This is the 5% calcium lactate level. The daily calcium lactate intakes of females in the 5 % group was 570 mg per rat. Assuming an average weight of 250 g for female rats, this intake would correspond to calcium lactate dose of 2280 mg/kg bw/day.
- Remarks on result:
- other: Effect type: carcinogenicity (migrated information)
- Dose descriptor:
- NOAEL
- Effect level:
- 279.5 mg/kg bw/day
- Sex:
- male
- Basis for effect level:
- other: Calculated as Ca2+.
- Remarks on result:
- other: Effect type: carcinogenicity (migrated information)
- Dose descriptor:
- NOAEL
- Effect level:
- 296.4 mg/kg bw/day
- Sex:
- female
- Basis for effect level:
- other: Calculated as Ca2+.
- Remarks on result:
- other: Effect type: carcinogenicity (migrated information)
- Conclusions:
- Calcium lactate did not cause toxicity or carcinogenic activity in F344 rats. Thus, the high dose of 5 % represents the NOAEL for tumour formation in this study. The concentration of 5 % corresponds to calcium lactate doses of 2150 and 2280 mg/kg bw/d to male and female rats, respectively, which are equivalent to calcium doses of approximately 279.5 and 296.4 mg Ca/kg bw/d for male and female rats.
Reference
Endpoint conclusion
- Endpoint conclusion:
- no adverse effect observed
- Dose descriptor:
- NOAEL
- 391 mg/kg bw/day
- Study duration:
- chronic
- Species:
- rat
Carcinogenicity: via inhalation route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Carcinogenicity: via dermal route
Endpoint conclusion
- Endpoint conclusion:
- no study available
Justification for classification or non-classification
Neither calcium, calcium dihydroxide nor calcium carbonate are carcinogenic. Classification for carcinogenicity is not warranted.
Additional information
The long term toxicity/carcinogenicity of calcium lactate was examined in F344 rats. Calcium lactate was given ad libitum in the drinking water at levels of 0, 2.5 or 5% to groups of 50 male and 50 female rats for two years. Animals were examined daily for clinical signs and mortality. Body weights were measured once a week for the first 13 weeks and every four weeks thereafter. Water intake was measured three times a week, when the calcium lactate solutions were replaced with freshly prepared solutions. Haematology and clinical chemistry analyses were performed at the end of the study. At week 113, all surviving animals were killed and autopsied. An autopsy was performed immediately on rats that died (or were killed when moribund) during the study and those killed at the end of the study. The animals were then examined macro- and microscopically for the presence of non-neoplastic and neoplastic lesions. All organs and / or tissues were routinely fixed in 10 % buffered formalin, sectioned and stained with haematoxylin and eosin. The mortality rate in high-dosed females was slightly higher than those in the two other groups, but the difference was not statistically significant. There was a dose-dependent decrease in body weight gain for both males and females. No specific dose-related changes of haematological or biochemical parameters were observed. Females of the high-dose group exhibited slightly, but significantly, higher kidney weights. Histologically, however, there was no difference in the severity of chronic nephropathy. A significant dose-dependent increase was observed in the relative brain weights of both male and female rats although no histological change was detected. A number of non-neoplastic lesions (e.g. myocardial fibrosis, bile-duct proliferation, hepatic microgranulomas and chronic nephropathy) were observed in all groups, with no difference in their incidence and/or degrees. None of the experimental groups showed a significant increase in the incidence of any specific tumours compared with the corresponding control value, and no positive trend was noted in the occurrence of any tumour. Male rats of the high-dose group showed a slightly higher incidence of pheochromocytomas and adrenal medullary hyperplasia, however there were no carcinogenic effects observed. Calcium lactate did not cause toxicity or carcinogenic activity in F344 rats. Thus, the high dose of 5 % represents the NOAEL for tumour formation in this study. The concentration of 5 % corresponds to calcium lactate doses of 2150 and 2280 mg/kg bw/d to male and female rats, respectively, which are equivalent to calcium doses of approximately 279.5 and 296.4 mg Ca/kg bw/d for male and female rats. Accordingly, the lower NOAEL value of 279.5 mg Ca/kg bw/d (male rats) is established as a NOAEL for carcinogenicity hazard assessment.
Considering the molecular weight of calcium (40.078) and calcium oxide (56.077 g/mol), this NOAEL can be converted into a NOAEL of 391 mg/kg bw/d.
Similarly, for calcium carbonate (100.0869 g/mol) the NOAEL would be 698 mg/kg bw/day.
A human clinical study (Baron, 1999; section 7.10.1) suggests a beneficial effect of calcium supplementation on cancer risk: Calcium supplementation is associated with a significant - though moderate - reduction of the risk of recurrent colorectal adenomas.
Furthermore, epidemiological data on cement workers (cement used as a surrogate for lime; s_Vestbo_1991_cement dust) indicate no increased overall cancer risk due to inhalation of cement dust in this population.
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