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O k l a h o m a N S F E P S C o R B i o e n e r g y R e s e a r c h a n d E d u c a t i o n STUDENT #1 SYNCHRONIZATION AND ISOLATION OF SWITCHGRASS FOR INTERECOTYPIC HYBRID DEVELOPMENT Laxman Adhikari and Yanqi Wu Department of Plant and


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O k l a h o m a N S F E P S C o R B i o e n e r g y R e s e a r c h a n d E d u c a t i o n

Laxman Adhikari and Yanqi Wu

Department of Plant and Soil Sciences, Oklahoma State University

STUDENT #1 SYNCHRONIZATION AND ISOLATION OF SWITCHGRASS FOR INTERECOTYPIC HYBRID DEVELOPMENT

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SLIDE 2

 To know the flowering behavior of upland and lowland

switchgrass.

 To determine the effects of synchronization and isolation

in interecotypic hybrid development.

 To identify male sterile genotypes in interecotypic hybrid.

Objectives

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SLIDE 3

Materials and Methods

1.

Earlier flowering upland plants were trimmed.

2.

Crossing pairs were isolated.

3.

Hybrid seeds were collected.

4.

Hybrid seeds’ genetic origins were identified using SSR markers.

5.

Male sterile lines were identified using pollen stainability and pollen germination.

Fig 1. (a) Isolated synchronized upland and lowland plants, (b) Panicles from two ecotypes crossing each

  • ther, (c) hybrid seeds, and (d) hybrid plants.

a b c d

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SLIDE 4

Results

Fig 2. (A) F1 upland progenies and their genetic origin, and (B) lowland F1 progenies and their genetic origin.

10 20 30 40 50 60 70 80 90 100 C1 C2 C3 C4 C5 C6 C7 C8 C9 Hybrid % Cross ID (upland progenies) Hybrid % Selfed % Contaminated %

A

10 20 30 40 50 60 70 80 90 100 RC1 RC2 RC3 RC4 RC6 RC7 RC8 Hybrid % Reciprocal cross ID (lowland progenies)

Hybrid % Selfed % Contaminated %

B

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SLIDE 5

Conclusions

 Proper synchronization of reciprocal parents yielded 58 to

100 % interecotypic hybrids.

 Improper synchronization yielded relatively higher selfed

seeds of reciprocal parents.

 The F1 genotypes C-8-17 and RC-3-3 were detected as

possible male sterile line, no pollen germination.

 The information from this study will be valuable in the

development of hybrid switchgrass.

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SLIDE 6

O k l a h o m a N S F E P S C o R B i o e n e r g y R e s e a r c h a n d E d u c a t i o n

Prakash Bhoi, Research Engineer

  • Dr. Krushna Patil, Assistant Researcher
  • Dr. Ajay Kumar, Assistant Professor
  • Dr. Raymond Huhnke, Professor

Biosystems & Agricultural Engineering Department Oklahoma State University, Stillwater, OK 74078

STUDENT #2 An equilibrium based process modeling

  • f a packed bed scrubbing system for

the removal of model tar compounds

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SLIDE 7

 To develop an equilibrium based process model of a wet

packed bed scrubber for the removal of model tar compounds.

  • Equation of state (EOS) models
  • Activity coefficient models

 To study the effect of important variables on the removal

efficiency of model tar compounds

  • Packing bed height
  • Solvent temperature
  • Liquid-to-gas (L/G) ratio

Objectives

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SLIDE 8

Methods

RadFrac

Oil in Model syngas Model syngas Oil out

Thermodynamic property methods:

  • Peng-Robinson
  • RK-Soave

Solvent: Soybean oil Packing media: 6 mm Raschig ring Raschig Ring Characteristics Values Density, Kg/m3 900 Surface are, m2/m3 900 Packing factor, 1/m 2300 Void fraction, % 89

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SLIDE 9

Results

20 40 60 80 100 20 30 40 50 60 70 Tar Removal Efficiency, % Solvent Temperature, °C

Peng-Robinson

L/G = 0.52 L/G = 0.45 L/G = 0.37

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SLIDE 10

Conclusions

 Both property models (Peng-Robinson and RK-Soave)

lead to comparable results.

 Packed bed height significantly increases tar removal

efficiency.

 Solvent temperatures above 40°C significantly reduce tar

removal efficiency.

 An increase in liquid-to-gas (L/G) ratio substantially

increases tar removal efficiencies for solvent temperatures above 40°C.

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O k l a h o m a N S F E P S C o R B i o e n e r g y R e s e a r c h a n d E d u c a t i o n

MB Couger, Noha H. Youssef, Audra S. Liggenstoffer, and Mostafa Elshahed Oklahoma State University Stillwater, Oklahoma.

STUDENT #3 Genome Sequence of the Anaerobic Gut Fungi Orpinomyces sp. strain C1A

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SLIDE 12

 Establish a high quality, well annotated, genome

sequence from a member of the anaerobic fungal genera Neocallamastix

 Identify the unique salient features of the genome and

conduct comparative analysis to other microbial genomes

 Identify enzymatic components of the genome that allows

it to have the ability to thrive in the Rumen.

Objectives

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Methods

Final Gene Models

10x Coverage 100x Coverage 35GB 16,347 Models Average Gene Length 1.6KB 100MB 3.5KB n50 22,000 Models N50 1080

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SLIDE 14

Results

Genome size 100.95 MB Number of Contigs 32,574 Protein Coding 20.60% Non- coding intergenic 73.60% Non-coding introns 5.10% rRNA 0.67% 5.8S 183 (30,763 bp) 18S 272 (168,110 bp) 28S 366 (457,301 bp) tRNA 0.06% 770 (58,292 bp) Number of Genes 16,347 Number of Genes with transcripts 14,009 Average Gene Length 1623 Number of Intron 35,697 Introns/gene 2.18 Average Intronlength 163 GC content 17.00% Protein Coding 26.80% Intergenic 14.80% Intron 8.10% SSR Repeats 4.90% TE repeats 3.31%

  • 0.4
  • 0.2

0.0 0.2 0.4 PC1 PC2

  • 60
  • 40
  • 20

20

  • 20

20

GH1 GH2 GH3 GH5 GH6 GH8 GH9 GH10 GH11 GH13 GH16GH18 GH26 GH28 GH31 GH43 GH45 GH47 GH48 GH61

  • 0.8
  • 0.6
  • 0.4
  • 0.2

0.0 0.2 0.4

Orpinomyces P_anse A_oryz M_gris M_ther P_chry T_rees N_cras P_plac R_oryz S_punc B_dend A_mac C_obs A_ther C_ther R_alba F_succ M_circ C_phyt

Bacterial Homolog 247 Rumen Homolog 141 Eukaryotic Homolog 110

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SLIDE 15

Conclusions

 Analysis of the Genome of Orpinomyces C1A reveals a

distinct genome structure from other members of Mycota.

 Anaerobic fungi contain a uniquely evolved enzymatic

system for plant cell wall degradation, many members of which where obtained from horizontal gene transfer from

  • ther prokaryotic members residing in the rumen. C1A

contains the capacity to degrade all major chemical moieties found in hemicellulose.

 This unique system combined with the invasiveness of

fungi make this organism a very promising agent for consolidated bioprocessing.

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SLIDE 16

O k l a h o m a N S F E P S C o R B i o e n e r g y R e s e a r c h a n d E d u c a t i o n

Miguel A. Gonzalez Borja, Daniel E. Resasco

School of Chemical, Biological & Materials Engineering University of Oklahoma

STUDENT #4 Alkylation Reactions for the Upgrading

  • f Bio-oil in the Presence of Liquid Water

Using Hydrophobic Zeolites

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SLIDE 17

 To develop bio-oil upgrading strategies that maximize the

yield of liquid products.

 To evaluate the performance of water-resistance catalyst for

alkylation reactions in aqueous media.

 To understand the reaction pathways for the alkylation of

phenolic compounds with 2-isopropanol.

Objectives

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SLIDE 18

Methods

MULTI-STAGE PYROLYSIS

T increase FRACTION I

Light Oxygenates

FRACTION II

Sugar derived

FRACTION III

Phenolics

ALKYLATION

CHALLENGES

  • Bio-oil unstability upon heating
  • Phase separation
  • Deactivation of catalyst by water

APPROACH

  • Work in liquid phase
  • Use catalyst that remains at

liquid-liquid interphase

  • Use catalyst that is stable in the

presence of water. HYDROPHOBIC ZEOLITE IN A BIPHASIC LIQUID PHASE REACTOR

2-Propanol m-Cresol

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SLIDE 19

Results

0.0 0.1 0.2 0.3 0.4 0.5 0.6 5 10 15 20 25 m-Cresol Conversion (mol/l) Time (hours)

Regular Zeolite / Monophasic Hydrophobic Zeolite / Monophasic Regular Zeolite / Biphasic Hydrophobic Zeolite / Biphasic

HYDROPHOBIC ZEOLITE PERFORMANCE

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Conclusions

 Alkylation reactions between light oxygenates and

phenolics appear to be an effective strategy for bio-oil upgrading while maximizing the yield of liquid products.

 Hydrophobic zeolites that remain at the oil-water interphase

posses improved stability for alkylation reactions in the presence

  • f liquid water.

 2-Propanol can be incorporated into the aromatic ring of

phenolics via alkylation or via etherification. Ethers can in turn convert to the alkylated product via trans-alkylation.

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SLIDE 21

O k l a h o m a N S F E P S C o R B i o e n e r g y R e s e a r c h a n d E d u c a t i o n

F . L i n a, C . M a n i s s e r i b, A . F a g e r s t r o m d, B . W i l l i a m s c, D . M . C h i n i q u y b , c, M . L . P e c k a, P . S a h a a, M . V e g a - S a n c h e z b , c, J . U . F a n g e l d, W . T . W i l l a t s d, H . V . S c h e l l e r b, P . C . R o n a l d b , c, L . E . B a r t l e y a , b , c

a D e p a r t m e n t o f M i c r o b i o l o g y a n d P l a n t B i o l o g y , U n i v e r s i t y o f O k l a h o m a , N o r m a n , O K 7 3 0 1 9 b J o i n t B i o E n e r g y I n s t i t u t e , E m e r y v i l l e , C A 9 4 6 0 8 a n d L a w r e n c e B e r k e l e y N a t i o n a l L a b o r a t o r y ,

B e r k e l e y , C A 9 4 7 2 0

c D e p a r t m e n t o f P l a n t P a t h o l o g y a n d T h e G e n o m e C e n t e r , U n i v e r s i t y o f C a l i f o r n i a , D a v i s , C A

9 5 6 1 6

d D e p a r t m e n t o f P l a n t a n d E n v i r o n m e n t a l S c i e n c e s , U n i v e r s i t y o f C o p e n h a g e n , D e n m a r k

STUDENT #5 Identification of Grass Cell Wall Synthesis Genes by Correlation Analysis between Gene Expression and Cell Wall Composition

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SLIDE 22

 Focus on grass-specific cell wall biosynthesis.  Develop a correlation based method to identify cell wall

synthesis genes

 Improve grass cell walls as a feedstock for biofuel

production

Objectives

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SLIDE 23

0.0 0.5 1.0 1.5 2.0 2.5 3.0 0.05 0.15 0.25 0.35 Correlation between a GT77 gene and Xylose Gene expression of GT77 Xylose (ug/ug cell wall residue)

Developmental Time Course Based Correlation Analysis

Quantitative PCR results of 74 grass diverged genes

16 cell wall components and 18 cell wall epitopes

30 samples from different developmental stages

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SLIDE 24

Putative Cell Wall Synthesis Genes Identified by Correlation Analysis

The cutoff is set as FDR<0.05 and |correlation coefficient|>0.6 Gene Cell Wall Component Gini correlation coefficient Pearson correlation coefficient Reference AT4-OsPMT p-coumarate 0.776 0.669 Withers, 2012 GT8-GAUT8-1 L5-galactan 0.716 0.633 GT8-GAUT8-1 GalA 0.787 0.742 GT8-GAUT1-1 L5-galactan 0.746 0.760 GT17-C-1 coumarate 0.699 0.609 GT17-C-1 Xyl 0.709 0.660 GT17-C-1 L10-xylan 0.732 0.680 GT77-4 Xyl 0.705 0.742 GT77-4 L10-xylan 0.740 0.733

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SLIDE 25

Conclusions

 It is feasible to identify cell wall synthesis genes using the

correlations between gene expression and cell wall composition.

 This analysis reveals the putative functions in cell wall

synthesis of 18 genes, which can now be tested by experiments.

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SLIDE 26

O k l a h o m a N S F E P S C o R B i o e n e r g y R e s e a r c h a n d E d u c a t i o n

Lei Nie, Daniel E Resasco*

University of Oklahoma

STUDENT #6 Improving Carbon Retention in Bio-oil Upgrading by Hydrogenation and Alkylation

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SLIDE 27

 Fast Pyrolysis Bio-oil Upgrading :  Oxygen Removal  Improving Carbon Retention

Objectives

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SLIDE 28

Methods

Fast Pyrolysis Bio-oil

Cut 1: Light oxygenates: Acetic acid, Acetol, Acetaldehyde, Water Cut 2: Sugar derived compounds: Furfurals Cut 3: Lignin derived compounds: C6-C8 Phenolics

Acetone Iso- propanol

H2

To Alkylation* With Cut 3 Aldol Condensation

C8-C13 Oxygenates

To Alkylation* With Cut 1 : Hydro- Deoxygenation (HDO) C10-C13 Phenolics

To Gasoline

  • r Diesel

pool

  • L. Nie, D.E. Resasco / Applied Catalysis A: General 447–448 (2012) 14 – 21
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SLIDE 29

Results

O

+

0.1g Pt-Fe/SiO2

OH

0.06g H-Beta

+

OH

0.06g H-Beta

O

+

4 : 1 (molar) 2 : 2 : 1 (molar)

OH

OH OH OH

Alkylate Yield : 2.5%

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Conclusions

 An alternative bio-oil upgrading straegy is proposed: combination

  • f hydrogenation and alkylation.

 Relative low reaction temperature needed.  The dehydration product, propylene, is the true alkylating agent.  Pt-Fe/SiO2 was found to be a selective hydrogenation catalyst.

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SLIDE 31

O k l a h o m a N S F E P S C o R B i o e n e r g y R e s e a r c h a n d E d u c a t i o n

Taiwo Omotoso Steven Crossley

School of Chemical, Biological and Materials Engineering University of Oklahoma

STUDENT #7 MECHANISM OF METHOXYBENZENE CONVERSION ON RUTHENIUM TITANIA CATALYSTS

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SLIDE 32

 Investigate mechanism of methoxy group conversion  Minimize catalyst deactivation  Catalytically remove oxygen from liquid bio oil

Objectives

+ *CH3 + CH4 + H2O methoxybenzene Sequential pathway Concerted pathway

O CH3 OH

Surface OH groups Ru Interface Surface defects H

*

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SLIDE 33

Methods

Model compound, Methoxybenzene

TiO2

= Ru

PRODUCT DISTRIBUTION Primary products Secondary products CALCINATION PRETREATMENT Calcine under air at 400 °C Calcine under air at 500 °C

Ru/TiO2

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SLIDE 34

Results

Product Distribution Calcination Temperature Effects

Catalyst Ru wt% Particle size(nm) Ru/TiO2(400) 3.66 6.9 Ru/TiO2(500) 3.86 >10

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SLIDE 35

Conclusions

 Ru/TiO2 is an active catalyst for deoxygenation of model

phenolic compounds under atmospheric pressure

  • f

hydrogen.

 A

sequential mechanism for the conversion

  • f

methoxybenzene via formation of phenol as a primary product is proposed.

 Calcination temperature plays an important role in the activity

and selectivity of the Ru/TiO2 catalyst for catalytic upgrading.

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SLIDE 36

O k l a h o m a N S F E P S C o R B i o e n e r g y R e s e a r c h a n d E d u c a t i o n

A s h o k k u m a r M . S h a r m a a, A j a y K u m a r a, S u n d a r M a d i h a l l y b, R o b W h i t e l e y b, R a y m o n d L . H u h n k e a

a B i o s y s t e m s a n d A g r i c u l t u r a l E n g i n e e r i n g D e p a r t m e n t b C h e m i c a l E n g i n e e r i n g D e p a r t m e n t

O k l a h o m a S t a t e U n i v e r s i t y , S t i l l w a t e r , O K 7 4 0 7 8 U S A

STUDENT #9 Reaction kinetics-based biomass gasification model to predict syngas quality suitable for biofuel production

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SLIDE 37

 To develop a reaction kinetics-based gasification model

using a continuous stirred-tank reactor (CSTR) to predict syngas composition and yield.

Objective

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SLIDE 38

Methods

1) Gibbs Equilibrium Model: 2) Reaction-Kinetics Model:

Inputs  Biomass flowrate  Air flowrate  Gasifier temperature  Gasifier pressure Outputs  Gas composition  Gas yield Inputs  Biomass flowrate  Air flowrate  Gasifier temperature  Gasifier pressure  Gasification reactions  Reaction rates (r values)  Rate constants (k values)  Residence time (τ) Outputs  Gas composition  Gas yield

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SLIDE 39

Results

Fig.1 – Experimental and predicted CO yield with varying ER Fig.2 - Experimental and predicted H2 yield with varying ER

0.00 0.20 0.40 0.60 0.80 0.29 0.32 0.40 CO, kg/kg biomass Equivalence ratio (ER) Experiment Reaction-kinetics Gibbs Eq. 0.00 0.01 0.02 0.03 0.04 0.05 0.29 0.32 0.40 H2, kg/kg biomass Equivalence ratio (ER) Experiment Reaction-kinetics Gibbs Eq.

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Conclusions

 As compared to experimental results:

 Gibbs equilibrium-based gasification model predicted CO and H2

yields 78% and 180% higher, respectively.

 Reaction kinetics based gasification model predicted CO and H2

yields within 13% and 9%, respectively.

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SLIDE 41

O k l a h o m a N S F E P S C o R B i o e n e r g y R e s e a r c h a n d E d u c a t i o n

Shaolong Wan, Christopher Waters, Rolf Jentoft, Steven Crossley, Lance Lobban, Daniel Resasco, Richard Mallinson

University of Oklahoma

STUDENT #10

Deactivation of Zeolite Catalysts During Upgrading

  • f Pyrolysis Vapors
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SLIDE 42

 Understand zeolite performance characteristics

(specifically deactivation) over various reaction conditions with non-model biomass feedstock

 Apply known model zeolite chemistries to vapor-phase

pyrolysis oil upgrading

 Increase total carbon retention in liquid product,

decrease hydrogen consumption

 Develop more robust upgrade strategies and pathways for

thermochemical biomass conversion to hydrocarbon fuels (gasoline, diesel)

Objectives

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SLIDE 43

Methods

Glass Plug Biomass Catalyst Wool

Separate Reactor 500°C

GC/MS

Pyroprobe 500°C

~0.5 mg (typ.) ~5mg

Catalytic

Glass Beads

Non-Catalytic

Separate reactor allows us to:

 Vary reactor conditions (temperature,

residence time) independent of pyrolysis conditions

 Measure catalyst deactivation with

multiple pulses

 Autosampler: very high throughput (15

pulses/day)

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SLIDE 44

Results

Feedstock: Pyrolysis temp: Catalyst: Oak sawdust 500C HZSM5, 5mg

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Conclusions

 Increased temperature slows catalyst deactivation  Zeolite chemistry produces aromatic hydrocarbons from

biomass pyrolysis vapors

 Separating the catalysis from the pyrolysis decouples

variables and allows us to better evaluate the catalytic performance (temperature, residence time)

 Rapid screening allows for evaluation of performance of

catalyst modification (crystal size, acid density, mesoporosity, additives, etc)

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O k l a h o m a N S F E P S C o R B i o e n e r g y R e s e a r c h a n d E d u c a t i o n

Tyler Weirick 1, Babu Z. Fathepure 2, Ramamurthy Mahalingam 3, Rakesh Kaundal 1*

1National Institute for Microbial Forensics & Food and

Agricultural Biosecurity, 1,3Dept of Biochemistry & Molecular Biology; 2Dept of Microbiology & Molecular Genetics

STUDENT #11 LigPred: A Comprehensive Prediction System for the Identification and Classification of Enzymes Related to the Synthesis and Degradation of Lignin

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SLIDE 47

 Better understand processes related to lignin.  Improve machine learning techniques for protein

functional classification.

 Discover novel lignin-related enzymes.

Objectives

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SLIDE 48

Methods

 Obtain high quality datasets  Reduce datasets to 40% sequence similarity  Split datasets into independent and training datasets.  Do 5-fold testing on training datasets to find optimum kernel

and parameters.

 Generate models with training datasets and to independent

testing with independent dataset.

 Classify all Swiss-Prot proteins not in dataset to further test

specificity.

 Classify true datasets; metagenomes, NCBI unknowns, etc.

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SLIDE 49

Results

 50 classes identified, 37 suitable for SVM classification.  5-Fold testing excellent.

 Maximum Matthews Correlation Coefficient (MCC): 1.0

 Independent Training acceptable.

 Max MCC ~0.7

 Negative Set testing poor (maybe).  Sequences predicted from metagenome and NCBI unknowns.

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SLIDE 50

Conclusions

 High chance of correctly predicting lignin related

enzymes.

 False positives likely very high.  False positives can likely be reduced with modifications to

experimental procedure.

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SLIDE 51

O k l a h o m a N S F E P S C o R B i o e n e r g y R e s e a r c h a n d E d u c a t i o n

Tao Xu, Yongchao Li, Zhili He, Jizhong Zhou

The University of Oklahoma

STUDENT #12 Cellulosomal protease inhibitor protects key cellulosomal cellulases in Clostridium cellulolyticum

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SLIDE 52

 Characterize the enzymatic activity of a cellulosomal

protease inhibitor in Cl0stridium cellulolyticum

 Examine the physiological function of this inhibitor  Examine the role of this inhibitor in regulating

cellulosomal composition

Objectives

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SLIDE 53

Methods

 Enzymatic activity test

Ni affinity chromatography + In vitro inhibitor assay

 Physiological characterization

Mutagenesis+ Growth determination+ Cellulose hydrolysis test

 Analysis to cellulosomal composition

SDS-PAGE + Mass spectrometry+ Densitometry analysis

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SLIDE 54

Results

  • The cellulosomal protease inhibitor is an effective

inhibitor of cysteine protease.

  • Lack of the inhibitor reduced cell growth and decreased

cellulose utilization.

  • Lack of the inhibitor greatly reduced the protein

abundance of several cellulosomal components.

  • Two major cellulosomal components, Cel48F and Cel9E,

are pivotal cellulases for cellulose hydrolysis.

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SLIDE 55

Conclusions

 This is the first study to uncover the physiological

importance of a cellulosomal protease inhibitor in protecting key cellulosomal cellulases in cellulose- degrading Clostridia.

 The presence of this protease inhibitor allows C.

cellulolyticum to maintain a higher efficiency in metabolizing lignocellulosic biomass.