Trace metals readily form "Complex (chemistry)") complexes with major ions in the ocean, including hydroxide, carbonate, and chloride, and their changes in chemical speciation depend on whether the environment is oxidized or reduced. Benjamin (2002) defines complexes of metals with more than one type of ligand, other than water, as mixed-ligand complexes. In some cases, a ligand contains more than one donor atom, forming very strong complexes, also called chelates (the ligand is the chelator). One of the most common chelators is EDTA (ethylenediaminetetraacetic acid), which can replace six water molecules and form strong bonds with metals that have a charge of more than two. A consequence of the lower reactivity of complexed metals compared to the same concentration of free metal is that chelation tends to stabilize the metals in aqueous solution rather than in solids.[38].
The concentrations of some trace metals—cadmium, copper, molybdenum, manganese, rhenium, uranium, and vanadium—in certain sediments record the redox history of the oceans. In aquatic environments, cadmium(II) can be in the form CdCl in oxic waters or CdS(s) in a reduced environment. Therefore, higher concentrations of Cd in marine sediments may indicate conditions of low redox potential in the past. For copper (II), a prevalent form is CuCl(aq) in oxic environments and CuS(s) and CuS in reduced environments. The reduced seawater environment leads to two possible oxidation states of copper, Cu(I) and Cu(II). Molybdenum is present as the oxidation state of Mo(VI) as MoO in oxic environments. Rhenium is present as the oxidation state Re (VII) as ReO under oxic conditions, but is reduced to Re (IV) which can form ReO or ReS Uranium is in the oxidation state VI in UUO(CO)(aq) and is found in the reduced form UO(s). Vanadium occurs in various forms in the oxidation state V (V) and HVO; This relative predominance of these species depends on pH.
In the water column of the ocean or deep lakes, the vertical profiles of dissolved trace metals are characterized by following the following distributions: conservative type (conservative–type), nutrient type (nutrient–type) or scavenged–type*. Across these three distributions, trace metals have different residence times and are used to different extents by planktonic microorganisms. Trace metals with conservative distributions have high concentrations relative to their biological use. An example of a trace metal with a conservative distribution is molybdenum. It has a residence time in the oceans of about 8 x 10 years and is generally present as the anion molybdate (MoO). Molybdenum interacts weakly with particles and shows a nearly uniform vertical profile. in the ocean. Relative to the abundance of molybdenum in the ocean, the amount required as a metal cofactor for enzymes in marine phytoplankton is negligible.[39].
Trace metals with nutrient-like distributions are strongly associated with the internal cycles of particulate organic matter, especially assimilation by plankton. The lowest dissolved concentrations of these metals are found at the ocean surface, where they are assimilated by plankton. As dissolution and decomposition occur at greater depths, the concentrations of these trace metals increase. The residence times of these metals, such as zinc, are several thousand to one hundred thousand years. Finally, an example of a swept-type trace metal is aluminum, which has strong interactions with particles and a short residence time in the ocean. Residence times for sweep-type trace metals are around 100 to 1000 years. Concentrations of these metals are highest around bottom sediments, hydrothermal vents, and rivers. For aluminum, atmospheric dust provides the largest source of external inputs to the ocean.[39].
Iron and copper show hybrid distributions in the ocean. They are influenced by recycling and intense cleaning. Iron is a limiting nutrient in vast areas of the oceans, and is found in great abundance along with manganese near hydrothermal vents. Here, many iron precipitates are found, mainly in the form of iron sulfides and oxidized iron oxyhydroxide compounds. Iron concentrations near hydrothermal vents can be up to a million times the concentrations found in the open ocean.[39].
Using electrochemical techniques, it is possible to show that bioactive trace metals (zinc, cobalt, cadmium, iron and copper) are bound by organic ligands on the surface of seawater. These ligand complexes serve to decrease the bioavailability of trace metals in the ocean. For example, copper, which can be toxic to phytoplankton and bacteria in the open ocean, can form organic complexes. The formation of these complexes reduces concentrations of bioavailable inorganic copper complexes that could be toxic to marine life at high concentrations. Unlike copper, the toxicity of zinc in marine phytoplankton is low and there is no advantage to increasing organic binding of Zn. In high-chlorophyll, low-nutrient regions, iron is the limiting nutrient, and the dominant species are strong organic Fe(III) complexes.[39].