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Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David C. White, Cory Lytle, Sarah J. Macnaughton, John R. Stephen, Aaron Peacock, Carol A. Smith, Ying Dong Gan, Yun- Juan Chang, Yevette M. Piceno Center for Environmental Biotechnology, University of Tennessee, Knoxville, TN, Environmental Sciences Division, Oak Ridge National Laboratory, Oak Ridge, TN, Microbial Insights, Inc., Rockford, TN, -CEB Microbial Insights, Inc.

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Page 1: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring

Effectiveness, and as Rational End-Points

David C. White, Cory Lytle, Sarah J. Macnaughton, John R. Stephen, Aaron Peacock, Carol A. Smith, Ying Dong Gan, Yun-Juan Chang, Yevette M. Piceno

Center for Environmental Biotechnology, University of Tennessee, Knoxville, TN, Environmental Sciences Division, Oak Ridge National Laboratory, Oak Ridge, TN,

Microbial Insights, Inc., Rockford, TN,

-CEBMicrobial Insights, Inc.

Page 2: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

In-situ Microbial Community Assessment

Classical Plate Count < 1.0 to 0.1% of community, takes days, lose community interactions & Physiology

Two Biomarker Methods: DNA: Recover from surface, Amplify with PCR

using rDNA primers , Separate with denaturing gradient gel electrophoresis (DGGE), sequence for identification and phylogenetic relationship. Great specificity

Lipids: Extract, concentrate, structural analysisQuantitative, Insight into: viable biomass, community composition,Nutritional-physiological status, evidence for metabolic activity

Page 3: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Vadose/Capillaryfringe12.2-12.8’

Bridgingcapillary13.5-14.3’

Saturated15-16’

Saturated17-18’

12.4-13.1’Vadose/Capillaryfringe

13.7-14.6’Bridgingcapillary

16-17’Saturated

Mig

ra

tio

n S

tan

da

rd

sM

igra

tio

n S

tan

da

rd

sIncreasing sample depth

Background samples,single bore-hole,triplicate sub-samples

Whey-barrier samples,single bore-hole, triplicatesub-samples.(45 days after amendment)

DGGE3 White et al

Page 4: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Burkholderia and relatives

Bacteroides-Flexibacter-Cytophaga phylum

Arthrobacter and relatives

Background(No treatment)

Whey-Barrier

Key: Prominent bandsderived from:

Neighbor-joining analysis of sequences recoveredfrom DGGE gels and reference sequences

Vadose

Saturated

No box = capillary

Page 5: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

LIPID Biomarker Analysis

1. Intact Membranes essential for Earth-based life

2. Membranes contain Phospholipids

3. Phospholipids have a rapid turnover from endogenous phospholipases .

4. Sufficiently complex to provide biomarkers for viable biomass, community composition, nutritional/physiological status

5. Analysis with extraction provides concentration & purification

6. Structure identifiable by Electrospray Ionization Mass Spectrometry at attomoles/uL (near single bacterial cell)7. Surface localization, high concentration ideal for organic

SIMS mapping localization

Page 6: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Cathedral from a Brick Predict impact of Cr contamination (from 50-200,000 ppm) on soil microbial community by artificial neural network (ANN) analysis

PLFA (phospholipid fatty acid) excellent ~x 102-103 ppm Cr with (PLFA).

DNA is “non compressible” ~ perfect code not so influencedBy microniche conditions as cell membranes PLFA is compressible as contains physiological status input Contains “holistic’ information & responds to perturbations Predict it is a Cathedral or a Prison : DNA a perfect brick PLFA a non-linear mixture of bricks and a window

Signature Lipid Biomarker Analysis

Page 7: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Phospholipid Fatty Acid [PLFA] Biomarker Analysis = Single most quantitative, comprehensive insight into in-situ microbial community

Why not Universally utilized?

1. Requires 8 hr extraction with ultrapure solvents [emulsions]. 2. Ultra clean glassware [incinerated 450oC]. 3. Fractionation of Polar Lipids4. Derivatization [transesterification] 5. GC/MS analysis ~ picomole detection ~ 104 cells LOD 6. Arcane Interpretation [Scattered Literature] 7. 3-4 Days and ~ $250

Signature Lipid Biomarker Analysis

Page 8: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

NEW Expanded Lipid Analysis

1. Utilizes HPLC not GC [Greatly expanded Molecular Sizes]2. Semi-automated, ~ “Flash” Extraction ~ 1 hr with

fractionation & > recovery from spores 3. Direct analysis of intact lipids [no derivatization]4. Sensitivity ~ Electrospray Ionization [sub femtomolar near

single cell as 100% of analyte ionize not 1%] 5. Specificity ~ Tandem Mass Spectrometry

Neutral loss or gain Select parent ions Analysis of specific product ions

Structural analysis of components in MS/MS [<< Chemical Noise]

Signature Lipid Biomarker Analysis

Page 9: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Lyophilized Soil Fractions, Pipe Biofilm

SFECO2 1. Neutral Lipids

UQ isoprenologues

Derivatize –N-methyl pyridyl Diglycerides Sterols Ergostrerol Cholesterol

ESE Chloroform.methanol

2. Polar Lipids

Transesterify

PLFA

CG/MS

Intact Lipids

HPLC/ESI/MS/MS

Phospholipids PG, PE, PC, Cl, & sn1 sn2 FAAmino Acid PGOrnithine lipidArchea ether lipidsPlamalogens

PHAThansesterify & Derivatize N-methyl pyridyl

3. In-situ Derivatize in SFECO2

2,6 DPA (Spores)

LPS-Amide OH FA

Page 10: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Sequential Extraction & HPLC/ESI/MS analysis ~ 1-2 hrs

Concentration/Recovery

Extraction SFE/ESE

SeparationHPLC/in-line

Fractionation

DetectionHPLC/ESI/MS(CAD)MS

or HPLC/ESI/IT(MS)n

CEBMicrobial Insights, Inc.

Page 11: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Lipid Biomarker Analysis

Sequential High Pressure/Temperature Extraction (~ 1 Hour)

Supercritical CO2 + Methanol enhancer Neutral Lipids, (Sterols, Diglycerides, Ubiquinones)

Lyses Cells Facilitates DNA Recovery (for off-line analysis

2. Polar solvent Extraction Phospholipids CID detect negative ions

Plasmalogens

Archeal Ethers 3). In-situ Derivatize & Extract Supercritical CO2 + Methanol

enhancer 2,6 Dipicolinic acid Bacterial Spores

Amide-Linked Hydroxy Fatty acids [Gram-negative LPS]

Three Fractions for HPLC/ESI/MS/MS Analysis

Page 12: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

*Macnaughton, S. J., T. L. Jenkins, M. H. Wimpee, M. R. Cormier, and D. C. White. 1997. Rapid extraction of lipid biomarkers from pure culture and environmental samples using pressurized accelerated hot solvent extraction. J. Microbial Methods 31: 19-27(1997)

Feasibility of “Flash” Extraction

ASE vs B&D solvent extraction*

Bacteria = B&D, no distortionFungal Spores = 2 x B&D Bacterial Spores = 3 x B&D Eukaryotic = 3 x polyenoic FA

[2 cycles 80oC, 1200 psi, 20 min] vs B&D = 8 -14 Hours

CEBMicrobial Insights, Inc.

Page 13: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Q6

Q7Q10

O

O

H3OC

H3OC

CH3

]H

n

197 m/z

Respiratory Ubiquinone (UQ)

Gram-negative Bacteria with Oxygen as terminal acceptor LOQ = 225 femtomole/uL, LOD = 75 femtomole/uL ~ 100 E. coli

Isocratic 95.5/4.5 % methanol/aqueous 1 mM ammonium acetate

Page 14: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

CH2O C

O

CH2(CH2)13CH3

CH2OH

CHO C

O

CH2(CH2)13CH3N

CH3

F+

CH3

SO3

N

CH3

O

N

CH3

CH2O C

O

CH2(CH2)13CH3

CHO C

O

CH2(CH2)13CH3

OCH

CH2O C

O

CH2(CH2)13CH3

CH2

CHO C

O

CH2(CH2)13CH3

Pyridinium Derivative of 1, 2 Dipalmitin

C41H73NO5+

Exact Mass: 659.55

Mol. Wt.: 660.02

C6H7NOExact Mass: 109.05

Mol. Wt.: 109.13

neutral loss

C35H67O4+

Exact Mass: 551.50

Mol. Wt.: 551.90

[M+92]+

[M+92-109]+

M = mass of original Diglyceride

LOD ~100 attomoles/ uL

Page 15: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

VIABLE NON-VIABLE

O O || ||

H2COC H2COC

| |C O CH C O CH

| |

H2 C O P O CH2CN+ H3

||

|

O

O-

||O

H2 C O H

||O

Polar lipid, ~ PLFA

Neutral lipid, ~DGFA

phospholipase

cell death

Membrane Liability (turnover)

Page 16: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

(A) Chromatogram of purified brain and egg yolk derived authentic PG, PE, and PC; (B) Extracted ion chromatogram (EIC) of PG from soil containing 15:0, 16:0, 16:1, 17:0, 17:1, 18:1, 19:1 (see Fig 5); (C) EIC for ions diagnostic of PE from the soil used in B.

A

B

C

PGPE PE

PC

PG

PESeparation on HAISIL reverse phase HL C-18 column, 30 mm x 1mm x 3 μ,95/5 methanol + 0.002% piperidine/water50 μL/min,

post-column modifier 0.02% piperidine in methanol, 10 μL/min.

Page 17: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

HPLC/ESI/MS

CEB

• Enhanced Sensitivity• Less Sample

Preparation• Increased Structural

Information• Fragmentation highly

specific i.e. no proton donor/acceptor fragmentation processes occurring

CH2

HC O C

O

R1

CH2OC

O

R2

OP

O

O

OX

Page 18: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

ESI (cone voltage) Q-1 CAD Q-3

ESI/MS/MS

Page 19: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Parent product ion MS/MS of synthetic PG Q-1 1ppm PG scan m/z 110-990 (M –H) -

Sn1 16:0, Sn2 18:2

Q-3 product ion scan of m/z 747 scanned m/z 110-990 Note 50X > sensitivity

SIM additional 5x > sensitivity ~ 250X

Page 20: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

OHO CH2OH

HO OH

O

CH O

CH2 O

O

O CH2

CH2

CH2 O P

O

O

O-

CH2

CH2

CH2

H2C OH

Archaebacterial Tetraether Lipid

5 ppm

1600 1620 1640 1660 1680 1700 1720 1740m/z0

100

%

1704

1701

1698

16411638

16431695

1664 1680

1706

1707

1713

FW 1640.4

ES+

[M+H]+

[M-2H+Na+K]+

In sim LOQ ~ 50 ppb

Page 21: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Expanded Lipid Analysis Greatly Increase Specificity ~Electrospray Ionization ( Cone voltage between skimmer and inlet ) In-Source Collision-induced dissociation (CID)

Tandem Mass Spectrometry Scan Q-1 CID* Q-3 DifferenceDaughter ion Fix Vary VaryParent ion Vary Fix VaryNeutral loss Vary Vary FixNeutral gain Vary Vary Fix

Select-ion monitoring Fix Fix Fix

*Collision-induced dissociation (CID) is a reaction region between quadrupoles

Lipid Biomarker Analysis

Page 22: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Problem: Rapid Detection of Bacterial Spores & LPS Amide-Linked OH Fatty Acids in Complex Matrices

From the lipid-extracted residue - - - - derivatize (acid methanolysis) & Supercritical Carbon Dioxide + methanol Extract

1. Detect 2,6 dipicolinate with HPLC/ESI/MS/MS 1 hour and 100% not 3 days and ~ 20% viable

2. Detect 3-OH Fatty Acids Amide-linked to KDO in LPS of Gram-negative Bacteria with HPLC/ESI/MS/MS

Enterics & Pathogens 3OH 14:0Pseudomonad's 3OH 10:0 & 3OH 12:0 (Should Dog Drink from Toilet Bowl?)

Page 23: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

[M+H]+

[M+Na]+NOCH3

O

H3OC

O

C9H9NO4Exact Mass: 195.05

Mobile phase: MeOH + 1mM ammonium acetateCone: 40V

ES+

ESI Spectrum of 2, 6-Dimethyl Dipicolinate

LOD ~ 103 spores ~ 0.5 femtomoles/ul

Page 24: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Signal Optimization for 2,6 Dimethyl Dipicolinate

0.0E+00

2.0E+07

4.0E+07

6.0E+07

8.0E+07

1.0E+08

1.2E+08

0 20 40 60 80 100 120

Cone Voltage, V

Re

sp

on

se

196 m/z

218 m/z

168 m/z

Page 25: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Microniche Properties from Lipids

1. Aerobic microniche/high redox potential.~ high respiratory benzoquinone/PLFA ratio, high proportions of Actinomycetes, and low levels of i15:0/a15:0 (< 0.1) characteristic of Gram-positive Micrococci type bacteria, Sphinganine from Sphingomonas 2. Anaerobic microniches ~high plasmalogen/PLFA ratios (plasmalogens are characteristic Clostridia), the isoprenoid ether lipids of the methanogenic Archae.

3. Microeukaryote predation ~ high proportions of phospholipid polyenoic fatty acids in phosphatidylcholine (PC) and cardiolipin (CL). Decrease Viable biomass (total PLFA) 4. Cell lysis ~ high diglyceride/PLFA ratio.

Signature Lipid Biomarker Analysis

Page 26: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Microniche Properties from Lipids

5. Microniches with carbon & terminal electron acceptors with limiting N or Trace growth factors ~ high ( > 0.2) poly β-hydroxyalkonate (PHA)/PLFA ratios

6. Microniches with suboptimal growth conditions (low water activity, nutrients or trace components) ~ high ( > 1) cyclopropane to monoenoic fatty acid ratios in the PG and PE, as well as greater ratios of cardiolipin (CL) to PG ratios.

7. Inadequate bioavailable phosphate ~ high lipid ornithine levels

8. Low pH ~ high lysyl esters of phosphatidyl glycerol (PG) in Gram-positive Micrococci.

9. Toxic exposure ~ high Trans/Cis monoenoic PLFA

Signature Lipid Biomarker Analysis

Page 27: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

ANN Analysis of CR impacted Soil Microbial Communities

1. Cannelton Tannery Superfund Site, 75 Acres on the Saint Marie River near Sault St. Marie, Upper Peninsula, MI

2. Contaminated with Cr+3 and other heavy metals between1900-1958 by the Northwestern Leather Co.

3. Cr+3 background ~10-50 mg/Kg to 200,000 mg/Kg.

4. Contained between ~107-109/g dry wt. viable biomass by PLFA; no correlation with [Cr] (P>0.05)

5. PLFA biomass correlated (P<001) with TOM &TOC but not with viable counts (P=0.5)

-CEB

Page 28: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

C181W

9C

CI1

70

C181W

7C

C10M

E180

CA

170

CI1

51W

11C

I151A

C161W

5C

CI1

50

C201W

9C

C161W

11C

C10M

E160

CB

R181

CA

150

CI1

60

%TO

MC

160

CC

Y170B

C170

C150

C203W

6C

AC

210

PH

C12M

E160

C161W

7T

C183W

3%

TO

CC

I171W

8C

BR

150B

CB

R170B

C181W

7T

C182A

CB

R170A

BIO

MA

SS

C151 P

CI1

51B

WE

TLA

ND

CB

R150A

CC

Y190

MG

CI1

40

C180

C161W

7C

C230

CB

R160 K

C11

ME

160

C205W

3C

12M

E180

C200

CC

Y170A

CI1

51C

C182W

6C

140

C220

CI1

61

C162

C240

CB

R150C

C204W

6V

IAB

LE

_C

C181W

5C

0.0%

1.0%

2.0%

3.0%

4.0%

5.0%

6.0%

7.0%

Rel

ativ

e se

nsiti

vity

0%

10%

20%

30%

40%

50%

60%

70%

80%

90%

100%

110%

Cum

mulative sensitivity

Sensitivity analysis ranks the inputs by importance in predicting [Cr+3]PLFA have a significant larger predictive value than environment parameters (marked with arrows).

PLFA profiles are a can be used as a general purpose biosensorgeneral purpose biosensor

Page 29: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

ANN Analysis of CR impacted Soil Microbial Communities

SENSITIVITY (from ANN) 20% of the variables accounted for 50% of the predictive of Cr+3

concentrationOf these 20 %:

18:1w9c (6.6%) Eukaryote (Fungal) correlated with 18:26 (P<0.02)

10Me 16:0 (2.5%) correlated with i17:0 (4.8), 16:1 11c (2.9), i15:0 (3.1) (P<0.001). Thus all are most likely indicative of SRBs or MRBs.

18:17c (4.6%) = Gram negative bacteria

10Me 18:0 (4.3%) (Actinomycetes)

-CEBNABIR

Page 30: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

ANN Analysis of CR impacted Soil Microbial Communities

CONCLUSIONS:1. Non-Linear ANN >> predictor than Linear PCA (principal Components Analysis)

2. No Direct Correlation (P>0.05) Cr+3 with Biomass (PLFA), Positive correlation between biomass (PLFA) and TOC,TOM

3. ANN: Sensitivity to Cr+3 Correlates with Microeukaryotes (Fungi)18:19c, and SRB/Metal reducers (i15:0, i 17:0, 16:1w11, and 10Me 16:0)

4. SRB & Metal reducers peaked 10,000 mg/Kg Cr+3

5. PLFA of stress > trans/cis monoenoic, > aliphatic saturated with > Cr+3

-CEBNABIR

Page 31: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Expand the Lipid Biomarker Analysis

1. Increase speed and recovery of extraction “Flash”

2. Include new lipids responsive to physiological status HPLC (not need derivatization)

Respiratory quinone ~ redox & terminal electron acceptorDiglyceride ~ cell lysisArchea ~ methanogensLipid ornithine ~ bioavailable phosphateLysyl-phosphatidyl glycerol ~ low pHPoly beta-hydroxy alkanoate ~ unbalanced growth

3. Increased Sensitivity and Specificity ESI/MS/MS

Signature Lipid Biomarker Analysis

Page 32: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Extract lipids, HPLC/ESI/MS/MS analysis of phospholipids detect specific PLFA as negative ions PLFA 12C Per 13C 16:1 253 269 same as 12C 17:0

16:0 255 271 Unusual 12C 17:0 (269) + 2 13C cy17:0 267 284 12C 18:0 (283) + 13C

18:1 281 299 12C 20:6 , 12C 19:0 with 2 13C 19:1 295 314 12C 21:5 (315), 12C 21:6 (313)

Detection of specific per 13C-labeled bacteria added to soils

13C bacteria added

No 13C bacteria added

Page 33: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

0 400ft

N

C4

B5 B7 B9

C8 C10

D9 D11

C16

D17E16 E18

G14

H15 H17 H19 H21I20 I22

J19J21

K22K20

L21M20

J23

N21O22

P23

Q24

N23

O24

P25

U26T27

K28

TANNERY

G18

Q26

RemovedBeach

Grass Pond

Woodland

Swampy/Cattails

Wooded Wetland

Grassy Wetland

Running Water

A

Cannelton Tannery Superfund Site

Page 34: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

100,001-300,000

75,001-100,000

50,001-75,000

25,001-50,000

10,001-25,000

7,001-10,000

5,001-7,000

3,001-5,000

2,001-3,000

1,001-2,000

501-1,000

101-500

51-100

1-50

ND

Cr+3 Concentrations Site map

Page 35: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

regression

training

testing

Pred

ictiv

e er

ror

cross-validated error

Stop !

classificationvector

Inputprofile hidden layer

Schematic architecture of a three layer

feedforward network used to associate

microbial community typing profiles

(MCT) with classification vectors.

Symbols correspond to neuronal nodes

Generalization is assured

by cross-validation

ANN are universal predictors

Capable oflearning from examples

Page 36: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

1 10 100 1000 10000 100000 1E+006

Observed Cr3+ concentration (mg Kg-1)

1

10

100

1000

10000

100000

1E+006

Predicted Cr3+ concentration (mg Kg-1)

training setvalidation setregressionidentity

slope = 1.09

R2 = 0.98

Good Predictive Accuracy at > 100 mg Cr+3 /Kg

Page 37: Assessment of Subsurface in-situ Microbial Communities by Biomarkers for Remediation Potential, Monitoring Effectiveness, and as Rational End-Points David

Tandem Mass Spectrometers

CEBJPL

Ion trap MSn (Tandem in Time)Smaller, Least Expensive, >Sensitive (full scan)

Quadrupole/TOF> Mass Range, > Resolution

MS/CAD/MS (Tandem in Space)1. True Parent Ion Scan to Derivative Ion Scan2. True Neutral Loss Scan 3. Generate Neutral Gain Scan4. More Quantitative 5. > Sensitivity for SIM6. > Dynamic Range