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EC number: 214-185-2 | CAS number: 1111-78-0
- 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
Link to relevant study record(s)
Description of key information
Key value for chemical safety assessment
Additional information
When ammonium carbonate, ammonium hydrogencarbonate, ammonium carbamate, or ammonium chloride with sodium carbonate dissolves in water, several equilibrium reactions establish (Wen, N. & Brooker, J. Phys. Chem. 1995, 99, 259-268):
NH4+(aq) + H2O(l)↔NH3(aq) + H3O+(aq)
CO32-(aq) + H2O(aq) ↔ HCO3-(aq) + OH-(aq)
CO32-(aq) + NH4+(aq) ↔ HCO3-(aq) + NH3(aq)
HCO3-(aq) + NH3(aq) ↔ H2NCOO-(aq) + H2O(l)
H2NCOO-(aq) + H2O(l) ↔ CO32-(aq) + NH4+(aq)
The overall equilibrium among the carbonate, bicarbonate, carbamate, ammonium and free ammonia can be expressed as:
H2NCOO-(aq) + H2O(l) ↔ CO32-(aq) + NH4+(aq) ↔ HCO3-(aq) + NH3(aq)
It was shown that aqueous solutions of ammonium carbonate,
ammonium bicarbonate and ammonium carbamate give very similar Raman
spectra. It was confirmed that the solutions contain common species such
as CO32-(aq), HCO3-(aq), H2NCOO-(aq),
NH4+(aq) and solvent H2O(l).
Furthermore,13C-NMR studies conducted with these solutions
provided complementary evidence for the same equilibrium (Wen & Brooker,
1995).
Furthermore, a number of
publications describe a shift of the equilibrium depending on the pH of
the solution:
Even at weakly acidic conditions (acetic acid/acetate) a complete
decomposition of ammonium carbamate into ammonia and carbon dioxide
occurs in less than a second (Faurholt, C., Dan. Vidensk. Selsk.,
Mat.-Fys.Medd. 3 (1921) 20; Roughton,
F. J. W., J. Amer. Chem. Soc. 63, 1941, 2930-2934). Gradual
decomposition of carbamate to bicarbonate/carbonate with decreasing pH
(≤9.93) has also been shown by Mani et al. (Green Chemistry, 2006, 8,
995-1000)..
A rate constant for decomposition of
carbamate at pH 9.05 is reported to be 0.038 sec-1at 0 °C and
0.22 sec-1at 25 °C (Blakeley et al., 1969; Roughton, 1941),
which corresponds to half-lives of about 20 and 3 seconds, respectively.
These results are also confirmed by the analysis of13C{1H}-NMR
spectra obtained dissolving ammonium carbamate in D2O, in
which signals referred to the ions carbamate and bicarbonate/carbonate
have been observed (BASF SE, analytics report, order number 14Y00397,
2014). The data show that a 1:1 equilibrium between ammonium carbamate
and bicarbonate/carbonate establishes after approximately 2 hours
without further concentration shifts after that point.
In a follow-up experiment,13C{1H}-NMRof a 10%
solution of ammonium carbamate in D2O (pH 9-9.5) were
recorded (BASF SE, analytics report, order number 14E00249). Two signals
at 166.6 ppm (ammonium carbamate) and 163 ppm (ammonium
hydrogencarbonate), respectively, were detected after 32 scans (2:16
minutes), the ratio being 1:0.4. After >12 hours, a ratio of 1:1.5 had
established. The experiment was repeated with a 1% solution of ammonium
carbamate in D2O (pH 9-9.5), which was also the lowest
concentration at which NMR signals could be obtained that were
distinctive enough for interpretation. Here, the ammonium
hydrogencarbonate signal was the only detected signal after 10 minutes,
indicating complete decomposition of the carbamate anion.
The results above indicate that the hydrolysis rate of ammonium
carbamate increases with decreasing concentrations. Physiological
concentrations can be anticipated to be much lower than the
concentrations tested above, and thus it can be expected that
decomposition will take place even faster under physiological conditions.
The instability of ammonium carbamate under acidic conditions has also been demonstrated by13C{1H}-NMR. After recording a spectrum of a 10% solution of ammonium carbamate in D2O, the solution was acidified with 20% DCl and another spectrum was recorded (pH 1). As expected, no13C signals were detected after acidification as ammonium carbamate and ammonium hydrogencarbonate had completely decomposed.
The pH of lung-lining fluid in humans is approx. 6.6 (Bodem et al., Am Rev Respir Dis., 1983 Jan; 127(1):39-41), that of human skin usually below 5 (Lambers et al., In J Cosmet Sci., 2006 Oct;28(5):359-70), and that of gastric acid in the stomach 1-2. Based on the literature data in combination with13C{1H}-NMR spectra, it can be anticipated that decomposition of ammonium carbamate into its hydrolysis products takes place upon inhalative, dermal or oral uptake of the substance, because the equilibrium will be shifted towards the right side. Thus, the systemic toxicological effects of ammonium carbamate can be predicted from its dissociation products. As a result, a read-across approach using data from ammonium ions or ammonia, as well as bicarbonate or carbonate ions, is considered applicable to cover those endpoints where no data for ammonium carbamate is available. This strategy is in accordance with section 1.5 of Annex XI of the REACH Regulation.
The systemic fates of ammonium/ammonia and carbonate/bicarbonate
are described in the following:
At physiological pH in aqueous media, the ammonium ion is in equilibrium
with un-ionised ammonia. An ammonium ion via the equilibrium with
ammonia is readily taken up. Some evidence exists also for an active
transport of the ammonium ion from the intestinal tract. It has been
shown that ammonia transport by the human colon still occurred when the
luminal pH was reduced to 5, where non-ionised ammonia would be
virtually absent (WHO, 1986). Non-ionised ammonia (NH3)
passes tissue barriers with ease. Once absorbed, ammonium is transported
to the liver where it is metabolised to urea and excreted via the
kidneys. Minor amounts of nitrogen are incorporated in the physiological
N-pool (WHO, 1986). The ammonium ion serves a major role in the
maintenance of the acid-base balance. In the normal pH range of blood,
the NH4+/ NH3is about 100 (WHO, 1986).
Carbonate is a normal intermediate in the metabolism of endogenous carbon compounds. Physiologically, it plays an integral role in the extracellular buffering system of blood and the interstitial fluid of vertebrates as seen in the following equation:
H2O + CO2<=> H2CO3<=> H++ HCO3-
At low systemic pH, the concentration of hydrogen ions is high. As a consequence, the equilibrium of the equation is shifted to the left; hence as a compensatory response CO2is exhaled (hyperventilation). When on the other hand pH is high, the concentration of hydrogen ions in the blood is low, so the kidneys excrete bicarbonate (HCO3−). This causes the equation to shift to the right, essentially increasing the concentration of hydrogen ions, causing a more acidic pH.
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