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Cadmium cycle

The cadmium cycle is a biogeochemical cycleofdispersion and deposition of cadmium through the atmosphere, biosphere, pedosphere, and hydrosphere. Cadmium typically exists in the environment with an oxidation state of +2 but can be found with an oxidation state of +1 (though quite uncommon).^[1]

Sources

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Part of a series on
Biogeochemical cycles
Water cycle Water cycle deep water cycle
Carbon cycle Global atmospheric terrestrial oceanic Sequestration carbon sink deep carbon cycle soil carbon mycorrhizal fungi Boreal forests
Nutrient cycle Hydrogen cycle Nitrogen cycle human impact nitrification nitrogen and lichens fixation assimilation Oxygen cycle Phosphorus cycle assimilation Sulfur cycle assimilation
Rock cycle Calcium cycle Silica cycle Carbonate–silicate cycle
Marine cycle Marine biogeochemical cycles Biological pump microbial loop viral shunt Calcareous ooze Siliceous ooze
Methane cycle Atmospheric methane Methane clathrate clathrate gun hypothesis Arctic methane emissions
Other cycles aluminum arsenic boron bromine cadmium chlorine chromium copper fluorine gold iodine iron lead lithium manganese mercury ozone–oxygen selenium vanadium zinc
Related topics Biogeochemistry geochemical cycle chemical cycling environmental chemistry Biosequestration Deep biosphere Ocean acidification acid rain Biogeochemical planetary boundaries
Research groups DAAC GEOTRACES IMBER NOBM SOLAS
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Atmospheric sources are dominated by anthropogenic emissions (non-ferrous metal production, fossil fuel combustion, iron and steel production, waste disposal, and cement production), with minor introduction of cadmium through natural emissions (volcanoes, dust, biomass burning, and sea spray).^[1] Cadmium introduced as powders and aerosols through anthropogenic sources and natural sources can be detected in almost all corners of the globe. Cadmium is highly soluble and cadmium concentrations are rapidly depleted after wind transport as particles, aerosols, and water droplets.^[1] Typically, cadmium deposition decreases latitudinally from the source.

The majority of cadmium deposition to soils and freshwater is due to anthropogenic atmospheric emissions, contaminantsinbiosolids, and contaminants in fertilizers. Dry deposition accounts for 30-70% of terrestrial inputs.^[1] Cadmium is highly mobile in soils and becomes mineral-associated over time. Higher pH and temperature favor cadmium incorporation into minerals, while lower pH and temperature makes cadmium more soluble. Dissolved cadmium circulates through freshwater systems before introduction to larger bodies of water. In rivers, dissolved cadmium ranges from nanomolar to micromolar concentrations.^[1]

The vast majority of marine cadmium (80-90%) comes from wet deposition.^[1] Cadmium behaves similarly to nutrients such as phosphate and zinc: dissolved concentrations depend heavily on uptake, assimilation, and deposition by phytoplankton and diatoms.^[2] Dissolved cadmium concentrations are sub-nanomolar in the surface ocean and increase with depth, with a maximum in the thermocline.^[1] Like other nutrients, cadmium is lowest in the North Atlantic (~0.3 nM). Higher concentrations (up to 1 nM) occur in the deep Indian, Southern, and Pacific oceans due to water mass aging during thermohaline circulation.^[1] Coastal waters range from 0.2 to 0.9 nM, denoting a significant terrestrial input.^[1]

• Cadmium
• Carbonic anhydrase
• Diatoms