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EC number: 207-838-8 | CAS number: 497-19-8
- 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
Endpoint summary
Administrative data
Description of key information
Additional information
Degradation
The high water solubility and low vapour pressure indicate that sodium carbonate will be found predominantly in the aquatic environment. In water, sodium carbonate dissociates into sodium and carbonate and both ions will not adsorb on particulate matter or surfaces and will not accumulate in living tissues. An emission of sodium carbonate to water will result in an increase in alkalinity and a tendency to raise the pH value.
The carbonate ions will react with water, resulting in the formation of bicarbonate and hydroxide, until an equilibrium is established (McKee et al., 1963). It is obvious that both the sodium and bicarbonate ion have a wide natural occurrence (UNEP, 1995).
Sodium carbonate is an inorganic substance which cannot be oxidized or biodegraded by micro-organisms.
The degradation and environmental fate of sodium carbonate have been described on page 9 of the OECD SIDS dossier (2002). Please find hereafter the text:
The sodium ion is ubiquitously present in the environment and it has been measured extensively in aquatic ecosystems. Sodium and chloride concentrations in water are tightly linked. They both originate from natural weathering of rock, from atmospheric transport of oceanic inputs and from a wide variety of anthropogenic sources. The sodium concentration was reported for a total number of 75 rivers in North and South America, Africa, Asia, Europe and, with a 10th-percentile of 1.5 mg/L, mean of 28 mg/l and 90th-percentile of 68 mg/L (UNEP, 1995).
If carbonate is dissolved in water, a re-equilibration takes place according to the following equations:
HCO3-↔ CO32-+ H+ pKa = 10.33
CO2+ H2O ↔ HCO3- + H+ pKa = 6.35
The carbonate will finally be incorporated into the inorganic and organic carbon cycle.
Only a small fraction of the dissolved CO2is present as H2CO3, the major part is present as CO2. The amount of CO2in water is in equilibrium with the partial pressure of CO2in the atmosphere. The CO2/ HCO3-/ CO32-equilibriums are the major buffer of the pH of freshwater throughout the world.
Based on the above equations, CO2is the predominant species at a pH smaller than 6.35, while HCO3-is the predominant species at a pH in the range of 6.35-10.33 and CO32-is the predominant species at a pH higher than 10.33.
The natural concentration of CO2/ HCO3-/ CO32- in freshwater is influenced by geochemical and biological processes. Many minerals are deposited as salts of the carbonate ion and for this reason the dissolution of these minerals is a continuous source of carbonate in the freshwater environment. Carbon dioxide is produced in aquatic ecosystems from microbial decay of organic matter. On the other hand, plants utilise dissolved carbon dioxide for the synthesis of biomass (photosynthesis). Because many factors influence the natural concentration of CO2/ HCO3-/ CO32-in freshwater, significant variations of the concentrations do occur.
If the pH is between 7 and 9 then the bicarbonate ion is the most important species responsible for the buffer capacity of aquatic ecosystems. UNEP (1995) reported the bicarbonate concentration for a total number of 77 rivers in North-America, South-America, Asia, Africa, Europe and the 10th-percentile, mean and 90th-percentile were 20, 106 and 195 mg/L, respectively.
Environmental distribution
Sodium carbonate is an inorganic substance and therefore standard computer models cannot be used to determine the transport or distribution between environmental compartments.
The environmental distribution of sodium carbonate has been described already on page 8, 9 and 37 of the OECD SIDS dossier (2002). Please find hereafter the text:
If sodium carbonate is emitted to water it will remain in the water phase. If the pH is decreased then carbonic acid (H2CO3or CO2) can be formed. If the concentration of carbon dioxide water is above the water solubility limit, the carbon dioxide will distribute to the atmosphere.
If sodium carbonate is emitted to soil it can escape to the atmosphere as CO2(see above), precipitate as a metal carbonate, form complexes or stay in solution.
The high water solubility and low vapour pressure indicate that sodium carbonate will be found predominantly in the aquatic environment. In water, sodium carbonate dissociates into sodium and carbonate and both ions will not adsorb on particulate matter or surfaces and will not accumulate in living tissues. An emission of sodium carbonate to water will result in an increase in alkalinity and a tendency to raise the pH value.
The carbonate ions will react with water, resulting in the formation of bicarbonate and hydroxide, until equilibrium is established (McKee and Wolf, 1963). It is obvious that both the sodium and bicarbonate ion have a wide natural occurrence (UNEP, 1995).
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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