Natural attenuation offers large benefits to owners and managers of contaminated sites, but often raises strong objections from those who live and work near a site and are asked to assume most of the long-term risks. Part of the controversy comes about because published definitions of natural attenuation do not identify a realistic end-point objective, and they also are ambiguous about the naturally occurring processes that can achieve the objective. According to guidance from the U.S. National Research Council (NRC 2000), destruction and strong immobilization are the naturally occurring processes that achieve a realistic objective: containing the contaminant relatively nears its source, thereby minimizing exposure risks. The strategy for obtaining solid evidence that the objective is being achieved requires measurements that establish a cause-and-effect relationship between contaminant loss and a destruction or strong-immobilization reaction. The cause-and-effect relationship is best documented with reaction footprints, which typically are concentration changes in reactants or products of the destruction or immobilization reaction. MTBE presents a contemporary example in which footprint evidence for biodegradation is especially crucial, since aerobic biodegradation of MTBE requires special conditions not present at all sites: a high availability of dissolved oxygen and bacteria expressing particular oxygenase enzymes.
[1]
B. Rittmann.
Applying NRC Guidelines for Natural Attenuation of MTBE
,
2002
.
[2]
P. Mccarty,et al.
Environmental Biotechnology: Principles and Applications
,
2000
.
[3]
Jacqueline A. MacDonald,et al.
Peer reviewed: evaluating natural attenuation for groundwater cleanup.
,
2000,
Environmental science & technology.
[4]
B. Rittmann.
Monitored Natural Attenuation of MTBE
,
2003
.
[5]
W. Verstraete,et al.
Natural attenuation: extant microbial activity forever and ever?
,
2002,
Environmental microbiology.
[6]
Todd H. Wiedemeier,et al.
Technical Protocol for Implementing Intrinsic Remediation with Long-Term Monitoring for Natural Attenuation of Fuel Contamination Dissolved in Groundwater. Volume II.
,
1995
.
[7]
P. F. Hudak,et al.
Alternatives for Ground Water Cleanup
,
1995
.
[8]
B. Rittmann,et al.
Subsurface interactions of actinide species and microorganisms: Implications for the bioremediation of actinide-organic mixtures
,
1999
.
[9]
Multiple Methods for Determining Stability of Attenuating MTBE Groundwater Plume
,
2002
.