Microbial processes affect the chemical composition of groundwater and the
hydraulic properties of aquifers in both contaminated and pristine groundwa
ter systems. The patterns of water-chemistry changes that occur depend upon
the relative abundance of electron donors and electron accepters. In many
pristine aquifers, where microbial metabolism is limited by the availabilit
y of electron donors (usually organic matter), dissolved inorganic carbon (
DIC) accumulates slowly along aquifer flow paths and available electron acc
epters are consumed sequentially in the order dissolved oxygen > nitrate >
Fe(III) > sulfate > CO2 (methanogenesis). In aquifers contaminated by anthr
opogenic contaminants, an excess of available organic carbon often exists,
and microbial metabolism is limited by the availability of electron accepte
rs. In addition to changes in groundwater chemistry, the solid matrix of th
e aquifer is affected by microbial processes. The production of carbon diox
ide and organic acids can lead to increased mineral solubility, which can l
ead to the development of secondary porosity and permeability. Conversely,
microbial production of carbonate, ferrous iron, and sulfide can result in
the precipitation of secondary calcite or pyrite cements that reduce primar
y porosity and permeability in groundwater systems.