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Biological Considerations for Successful Vadose Zone Remediation Fred Brockman Pacific Northwest Natl. Lab. Introduction to Microbes Vadose Zone microbiology Bioremediation Research Opportunities
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What Microbes Can Do Degrade organic compounds Mobilize or immobilize inorganic compounds Affect water & gas geochemistry & quality Increase and reduce porosity Alter unsaturated & saturated flow Cause/enhance corrosion Move to more favorable conditions fortuitous physical transport directed biological (behavioral) “ Microbes are the things that screw up our chemistry and physics” - PNNL non-biologist
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Morphology Gram-negative - Membrane weaker but protected w/coatings - Does not form spores - “Hibernates” during lean times - Dominant in disturbed environments Gram-positive - Tougher membrane - Many form spores - “Suspended animation” - Dominant in very low nutrient flux environments Generally 0.5 – 2.0 micrometers in width/length Generally spherical or rod-shaped.
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Physiology A.Source of carbon 1.Organic compounds (heterotroph) 2.CO 2 (autotroph) B.Source of energy (electron donor) 1.Oxidize organic compounds (chemotroph) 2.Oxidize inorganics (lithotroph) 3.Oxidize H 2 (hydrogenstroph) 4.Oxidize CH 4 (methanotroph) 5.Oxidize NH 4 6.Sunlight (phototroph)
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Physiology C.Fate of electrons (electron acceptor) 1.O 2 (aerobe) 2.NO 3, NO 2 (denitrifier) 3.Split organic (fermentor) 4.Mn (IV) (Mn reducer) 5.Fe (III) (Fe reducer) 6.SO 4 (SO 4 reducer) 7.CO 2 (Methanogen) 8.Contaminants Cr Ur, Tc, Pu TCE, PCE, CT Chlorinated biphenyls, phenols, benzoates } facultative anaerobes } strict anaerobes *Specific physiologies, and specific organisms, degrade specific contaminants.
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Vadose Zone Microbiology ≈ 10 6 cells/g below the B horizon Live cells Physiological status Spatial distribution All 0.1g samples active No activity in 0.1 and 1g samples Live organisms cluster in isolated pockets Some 0.1 and 1g samples active * Colonization critical to remediation in arid climate V.Z.
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Bioremediation requires: Order of magnitude increases in contaminant – degrading activity of individual cells Order of magnitude increases in populations of contaminant – degrading organism(s) same fraction of total population increased fraction of total population
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Bioremediation Natural attenuation – degradation via natural processes Microbes often play a large role in physical/chemical remediation processes soil vapor extraction air sparging b-phase heating chemical oxidation Engineered or accelerated bioremediation – enhance rate of natural remediation or supplement other treatments by optimizing biology. bioventing (air) biosparging (air) nutrient injection – e - donor, donor + acceptor, other nutrients
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Research Opportunities in Multidisciplinary V.Z. Science Unsaturated zone conditions/experimental systems Fracture flow hydrology-microbiology studies Colloidal transport of inorganic contaminants (microbes as colloids) What physiologies can be amplified in which V.Z. geohydrologic/geochemical environments Functional and genetic stability of communities in the face of natural and engineered perturbations Colonization of locations containing contaminants.
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Where/How Can Bioremediation Fail? 1.Absence of contaminant – degrader population 2.Microbes, contaminants, nutrients not co-located 3.Other organisms out compete the contaminant-degraders Activity or numbers can not be adequately increased to achieve desired removal rate. 4.Sick contaminant – degrader population substrate: alternative substrate ratio too high or too low mutation & selection favor poorly performing strains crossed signals (microbes communicate w/chemical signals) byproducts toxic/inhibitory (transfer Rates too high) non-target organisms inhibitory * Functional stability is not guaranteed even if contaminant-degrader population is large
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