Cyanides act
quickly, they are taken up through the skin and mucous membranes (e.g. in the
mouth, stomach and intestines). They are quickly distributed throughout the
body. They destroy the normal metabolism in the cells so that oxygen cannot be
used, and thus cause a cellular choking as well as blocking the respiratory centres
in the brain. They also bind strongly to red blood cells and block the oxygen
uptake. The concentration in human tissues decreases rapidly after a single dose.
The cyanide ion is readily absorbed by the gastrointestinal tract and is rapidly converted into thiocyanate by the enzyme rhodanese. Cyanide may lower vitamin B12 levels and hence exacerbate vitamin B12 deficiency. Those with nutritional inadequacy or inborn metabolic errors are particularly vulnerable.
Cyanide toxicity in animals is essentially an inhibition of
oxygen metabolism, rendering tissues incapable of exchanging oxygen. The
toxicity of cyanides to marine and freshwater organisms is due mainly to the
presence of hydrocyanic acid, HCN and to a lesser degree to the cyanide ion,
CN.
The acute toxicity of free cyanide (expressed as CN) to aquatic organisms is highly variable, but may be as low as 0.005 mg/L.
Cyanides are highly susceptible to environmental degradation and residues are often extremely low in surface waters. Cyanides also accumulate in bottom sediments, but residues are generally low, <1 mg/kg, even near polluting sources. Many cyanides are presumed to be rapidly sorbed by sediments, clays and biological substances. They are also degraded by processes such as solar irradiation. The majority of an accidental release is volatilised to the atmosphere where it is quickly diluted and degraded. Cyanides are subject to significant biological transformation during anaerobic and aerobic sewage treatment. The processes are slower in surface waters, but are mediated by bacteria and rate-limited by nutrient levels and dissolved gases.
Many cyanide
compounds, including HNC, are rapidly metabolised in biological systems,
thereby limiting the potential for bioaccumulation. There is no evidence of
bioaccumulation in the food chain, and hence, secondary poisoning is not likely
For drinking water, based on long term
studies in animals a TD1 of 12 picograms/kg of body weight has been calculated.
This
results in a guideline value of 0.07 mg/litre (rounded figure), which is
considered to be protective for both acute and long-term exposure. In Canada
the drinking water quality guideline is 0.2 mg/L, and in the USA, it is 0.15
mg/L.
OSHA: TWA (time weighted average) 5 mg/m3
Germany: MAK 5
mg/m3
Sweden: Unfit for consumption 0.05 mg/L
WHO Drinking water quality guideline 0.07 mg/L
Freshwater aquatic life:
Canada 0.005
mg/L
USEPA, 4-day average 0.0052
mg/L
USEPA, 1-hour average 0.022 mg/L
European Union 0.005
mg/L
Saltwater organisms:
USEPA, 1-hour average 0.001
mg/L