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Manipulating Deinococcus radiodurans for treatment of mixed wastes

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Presentation on theme: "Manipulating Deinococcus radiodurans for treatment of mixed wastes"— Presentation transcript:

1 Manipulating Deinococcus radiodurans for treatment of mixed wastes

2 The Mixed Waste Problem
Poorly characterized, complex mixtures Difficult to treat: chemically complicated dangerous

3 Hanford Wastes 149 tanks built between 1944 and 1964
66 leak 37 Million gallons of waste Low level radiation + solvents Often just buried in pits Contaminated soils later isolated Conditions inside the tanks pH often near 10 to avoid corroding tank liners Radiation dose from a few to 5,000 rad/hour (50 Gy/hour) Organics often in the ppm concentration, or mM depending on the organic Millions of gallons of wash water will be generated after the tanks are emptied

4 The Mixed Waste Problem
Poorly characterized, complex mixtures Difficult to treat: chemically complicated dangerous Simplification is necessary: Remove toxic organic component radioactive + inorganics can be isolated using conventional methods.

5 Bioremediation and Cometabolism
Bacteria have evolved to degrade naturally occurring organics for growth or protection. Oxygenases are able to catalyze oxidation of organics at specific carbons

6 Toluene degradation TCE degradation
T2MO T3MO TOD toluene-cis- dihydrodiol dehydrogenase catechol-2,3 3-methylcatechol sMMO T2MO TOD TCE epoxide glyoxylate formate chloral hydrate (not in whole cells) sMMO T2MO (only with sMMO) dichloroacetate glyoxylate formate The University of Minnesota Biocatalysis/Biodegradation Database, Organisms isolated that contain these oxygenases would mutate or die in radioactive waste

7 Deinococcus radiodurans
High resistance to UV, ionic radiation Survive complete desiccation Fast, efficient DNA repair Complete genome sequence available No toxic organics are known to be degraded by R1

8 Proposal Engineer D. radiodurans to
solvents non-toxic products metals Engineer D. radiodurans to Degrade solvents Adsorb heavy metals Develop an onsite, low-cost treatment process using the altered strain Remove solvents Remove heavy metals waste treated effluent engineered D. radiodurans

9 Steps Develop genetic tools
Clone and express broad spectrum oxygenases Manipulate polyphosphate metabolism to achieve metal binding

10 Genetic Tools Insertion vector to create stable constructs
Expression vector and promoters to express foreign genes Mutation system Minimal medium Rob Meima, Lindy Gewin, Heather Rothfuss, Amy Schmid, Alex Holland

11 Clone and express broad spectrum oxygenases
Broad spectrum oxygenases degrade many toxic solvents (toluene, TCE) Candidates: Toluene dioxygenase Toluene monooxygenases Methane monooxygenase Target: TCE: 1-5 nmol/min/mg protein Toluene: nmol/min/mg protein Heather Rothfuss

12 High Toluene Degradation with Toluene Dioxygenase
80 80 80 mg protein) 70 70 70 - - - 60 60 60 /min /min 50 50 50 40 40 40 30 30 30 degradation rate ( 20 20 20 10 10 10 500 500 500 1000 1000 1000 1500 1500 1500 2000 2000 2000 nmol toluene added TCE degradation: 2 nmol/min/mg protein Heather Rothfuss

13 Solvent Resistance of P. putida DOT-T1E
Characteristics of Extremely Solvent Resistant Bacteria: Model, P. putida DOT-T1E Growth in 1% toluene (just past saturation) Survival of 0.3% (28mM) solvent shock when pre-grown with toluene supplied in headspace

14 Solvent Resistance in D. radiodurans
Toluene survival 1.00E+10 1.00E+09 1.00E+08 0%- 1.00E+07 0.5%- CFU/ml 1%- 1.00E+06 1.5%- 1.00E+05 2%- 3%- 1.00E+04 0%+ 0.5%+ 1.00E+03 1%+ 1.5%+ 1.00E+02 2%+ 1.00E+01 3%+ 10 20 30 40 50 60 minutes

15 Future Work Expression of alternate oxygenases, to expand the degradative repertoire Optimization of degradation under treatment conditions

16 Manipulate polyphosphate metabolism to achieve metal binding
Phosphate release at cell surface can result in metal precipitation (uranyl phosphate) Production then degradation of polyphosphate can supply the phosphate PO4 + metal --> metal-Pi ppt polyPO4 Jay Keasling, UC-Berkeley

17 Current hypothesis for the precipitation mechanism
High local Pi concentration Pit transporter bidirectional UO 2 2+ soluble HUO PO 4 Insoluble, membrane bound Periplasm Periplasm Inner Inner Inner membrane membrane membrane PolyP ATP ADP PPK Step 1 : required step Polyphosphate accumulation in cytosol Phosphate rich environment, no metal Cytoplasm PolyP Pi PPX Step 2 Inorganic phosphate excretion Phosphate free environment, metal laden : proposed steps Goal: Manipulate polyphosphate synthesis and degradation

18 Polyphosphate Manipulation
Hypothesis: overexpress PPX gene, get more polyP Identified the PPK and PPX genes Generated mutants, which are viable Studied promoter activity: PPK promoter is active under phosphate-limitation Cloned and overexpressed the genes singly and together: no change in polyP Heather Rothfuss, Alex Holland

19 Polyphosphate Manipulation
Developed a protocol to fill cell with polyP: Starve for phosphate for several hours, then add high phosphate Developed a protocol to release phosphate: Starve cells for phosphate Add metals: get almost complete removal in 2 hours! Pi Pi + metal --> metal-Pi ppt Alex Holland

20 Summary D. radiodurans strains have been constructed that can degrade a variety of toxic solvents A protocol has been developed to precipitate heavy metals Combining the two should allow the development of a process to remove toxic solvents and heavy metals in the presence of radioactivity

21 Assess Stress Response
Treatment conditions will involve many stresses Heat shock --solvent pH --starvation Ionic Goal is to minimize waste alteration for treatment Understanding stress response and regulatory mechanisms important for creation of an efficient bioremediation strain. Many known stress regulators are not recognizable in the annotated genome.

22 D. radiodurans R1 is extremely resistant to environmental stress
B. subtilis 168* 9%--100X loss in 4h 0.2M—550X loss in 3h pH4.3—1000X loss in 2h D.radiodurans R1 EtOH % --10X loss in 8h Salt M—10X loss in 4h Acid pH4.2—10X loss in 8h Amy Schmid * Völker et al J. Bact. 181(13):

23 Heat Shock Regulators Identified: sig1 and sig2 mutants survive poorly under heat shock
1 2 3 4 5 6 7 8 9 time (h) CFU/mL WT sig1 sig2 Amy Schmid

24 Heat shock induction of a PgroESL::lacZ fusion is decreased in sig1 and sig2 mutants
200 400 600 800 1000 1200 1400 1600 20 40 60 80 100 120 140 Time post-shift (min) Miller Units WT 30 sig1 30 sig2 30 WT 40 sig1 40 sig2 40 Amy Schmid

25 2D Gel Proteomics Comparison of 30C to 48C shows over 60 proteins induced by heat shock Comparison of WT to mutants shows 20 of these are not induced in the mutants Analysis of these spots by MS to determine identity ongoing (with R. Smith group, PNNL)

26 2D Protein Gels Reveal Over 60 Heat-shock Inducible Proteins: 20 are not induced in the mutants
30 sig1 WT sig2 48 Amy Schmid

27 Future Work Assess global changes in response to stress using microarrays (with J. Battista and TIGR) and whole cell proteomics (with R. Smith lab, PNNL) Assess response of D. radiodurans to simultaneous stresses, similar to those to be encountered in mixed wastes

28 Summary Solvent degradation at the target rate has been achieved
Polyphosphate manipulation is ongoing High stress resistance is advantageous Stress response systems being characterized Suggests simple process design with minimal manipulation of the waste

29 Potential Batch Process
Grow cells offsite in fermentation facility, dry Inoculate treatment system with dried cells and waste (possibly diluted) Run system (resting cells) until solvents are removed Remove effluent, filter cells, dry Dispose of cells/metals


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