TY - JOUR
T1 - Microbial influence on metal mobility and application for bioremediation
AU - Gadd, Geoffrey M.
N1 - Funding Information:
The author gratefully acknowledges financial support for his own work from the Biotechnology and Biological Sciences Research Council, Natural Environment Research Council and the Royal Societies of London and Edinburgh.
Copyright © 2004 Elsevier B.V. All rights reserved.
PY - 2004/10
Y1 - 2004/10
N2 - Microorganisms are intimately involved in metal biogeochemistry with a variety of processes determining mobility, and therefore, bioavailability. The balance between mobilization and immobilization varies depending on the organisms involved, their environment and physicochemical conditions. Metal mobilization can arise from a variety of leaching mechanisms, complexation by metabolites and siderophores, and methylation, where this results in volatilization. Immobilization can result from sorption to biomass or exopolymers, transport and intracellular sequestration or precipitation as organic and inorganic compounds, e.g., oxalates (fungi) and sulfides. In addition, reduction of higher valency species may effect mobilization, e.g., Mn(IV) to Mn(II), or immobilization, e.g., Cr(VI) to Cr(III). In the context of bioremediation, solubilization of metal contaminants provides a means of removal from solid matrices, such as soils, sediments, dumps and other solid industrial wastes. Alternatively, immobilization processes may enable metals to be transformed in situ and are particularly applicable to removing metals from aqueous solution. This contribution will outline selected microbiological processes which are of significance in determining metal mobility and which have actual and potential application in bioremediation of metal pollution. These include autotrophic and heterotrophic leaching mechanisms, reductive precipitation, sulfate reduction and metal sulfide precipitation.
AB - Microorganisms are intimately involved in metal biogeochemistry with a variety of processes determining mobility, and therefore, bioavailability. The balance between mobilization and immobilization varies depending on the organisms involved, their environment and physicochemical conditions. Metal mobilization can arise from a variety of leaching mechanisms, complexation by metabolites and siderophores, and methylation, where this results in volatilization. Immobilization can result from sorption to biomass or exopolymers, transport and intracellular sequestration or precipitation as organic and inorganic compounds, e.g., oxalates (fungi) and sulfides. In addition, reduction of higher valency species may effect mobilization, e.g., Mn(IV) to Mn(II), or immobilization, e.g., Cr(VI) to Cr(III). In the context of bioremediation, solubilization of metal contaminants provides a means of removal from solid matrices, such as soils, sediments, dumps and other solid industrial wastes. Alternatively, immobilization processes may enable metals to be transformed in situ and are particularly applicable to removing metals from aqueous solution. This contribution will outline selected microbiological processes which are of significance in determining metal mobility and which have actual and potential application in bioremediation of metal pollution. These include autotrophic and heterotrophic leaching mechanisms, reductive precipitation, sulfate reduction and metal sulfide precipitation.
KW - Biogeochemical cycles
KW - Bioremediation
KW - Metal immobilization
KW - Metal mobility
KW - Metal transformations
KW - Microorganisms
KW - Radionuclides
KW - Toxic metals
UR - http://www.scopus.com/inward/record.url?scp=4444248283&partnerID=8YFLogxK
U2 - 10.1016/j.geoderma.2004.01.002
DO - 10.1016/j.geoderma.2004.01.002
M3 - Article
AN - SCOPUS:4444248283
SN - 0016-7061
VL - 122
SP - 109
EP - 119
JO - Geoderma
JF - Geoderma
IS - 2-4
ER -