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EC number: 285-561-1 | CAS number: 85117-09-5 Mixtures of chemical substances produced by burning (below 1200°C) natural variants of limestone or chalk containing from 10 to 20%, or more, of clayey or siliceous materials which are predominantly SiO2, Al2O3 and iron oxide. Consist primarily of 2CaOsb.2, Ca(OH)2, CaO and 2CaOsb.2O3. 3CaO.2SiO2, 4CaOsb.2O3. Fe2O3, 2CaOsb.2O3sb.2, CaCO3 and SiO2 may also be included.
- 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
Description of key information
Human data support the finding that effects of lime are limited to the external surfaces of the body (local irritation) and no systemic effects are anticipated. If inhaled, the critical effects of hydraulic lime dust can be expected to be sensory irritation and a decrease of lung function parameters at long-term exposure, by read-across from CaO and Ca(OH)2.
Calcium supplementation during pregnancy is not adverse, but instead may be beneficial both to the mother and to the offspring.
Calcium appears to reduce the risk of recurrent colorectal adenomas
Toxicokinetics of calcium has been investigated in a range of human studies, which are summarised in section 7.1.1 of the technical dossier.
Case reports underline the irritating properties (skin and eye) of Ca(OH)2, being the main constituent of lime (chemical) hydraulic.
Additional information
Studies summarised in section 7.10.1 report individual cases or epidemiological data regarding human exposure to lime (or cement as surrogate for the alkaline effects of lime). Cain (2004), Torén (1996), Lahaye (1987), Wegman (1991), Vestbo (1991), Fell (2003), Yang (1996), and Eid (1969) form the basis of the SCOEL recommendation of occupational exposure limits (inhalation). Cain (2008) is provided as a supplementary reference to Cain (2004), confirming the nature of effects upon short-term exposure to CaO, which are described as sensory irritation and slightly increased secretion from the nasal mucosa. Meo (2003), and Al-Neaimi (2001) are provided as additional references describing typical symptoms of long-term over-exposure to cement dust, typically being reduced pulmonary function, pleural thickening and chronic bronchitis. Since the primary effect of both CaO/Ca(OH)2 and hydraulic lime upon inhalation are anticipated to be equivalent (local irritation due to pH shift), the above studies are used in support of hydraulic lime by read-across.
Villar (1990), Levine (1997), Koo (1999) are used as supportive data for the endpoint "developmental toxicity/teratogenicity" (section 7.8.2), demonstrating either a beneficial effect of lack of adverse effects of calcium in pregnancy, both to mothers and their offspring.
Belizán (1991) reports a protective effect of calcium against hypertensive disorders in pregnant women.
Baron (1999) reports that calcium supplementation is associated with a significant - though moderate - reduction of the risk of recurrent colorectal adenomas.
The references Johnston (1992), Lloyd (1993), Elders (1994), Reid (1993), Moser-Veillon (2001), Rosado (2005), Wastney (2000), Braun (2008), Minihane (1998), Sokoll (1992), Kalkwarf (1998), Peacock (2000), Dawson-Hughes (2002), and Bonjour (1997) are dealing with toxicokinetic parameters of calcium and are therefore reflected in section 7.1.1, together with SCF and FAO/WHO documents in a weight-of-evidence approach.
No relevant classical epidemiological data (section 7.10.2) have been identified.
Studies summarised in section 7.10.3 provide examples of human cases of eye irritation due to accidental exposure to calcium hydroxide (Schmidt, 2008), and skin corrosion due inadvertent exposure to wet cement over several hours (Rados, 2005). In the latter case, it is important to note that aqueous cement slurry has been found to result in substantially higher pH values (>13.5) than CaO or Ca(OH)2 alone. Therefore, the corrosive phenomena reported this case study should not be extrapolated to lime. Overall, the two human case studies summarised in this section demonstrate that exposure to hydrated lime or mixtures based upon lime may result in eye or skin irritation, particularly upon prolonged skin contact.
No sensitisation data in humans were retrieved (section 7.10.4).
Relevant exposure-related observation (section 7.10.5) other than those addressed in section 7.10.1 and 7.10.3 were not identified.
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.
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