Characterization of Cellulolytic and Fermentative Communities in Everglades Soils Ilker Uz Soil and Water Science Department University of Florida.
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Characterization of Cellulolytic and Fermentative Communities in Everglades Soils Ilker Uz Soil and Water Science Department University of Florida Widespread agricultural activity in the northern boundary of Florida Everglades has resulted in nutrient gradients, causing drastic physicochemical and ecological changes from the original system Lake Okeechobee WCA -1 WCA -2A WCA - 3 ~ 1500 mgP/kg Everglades National Park F1 Cattail U3 VEGETATION : Cattail ~ 500 mgP/kg Cattail/ sawgrass mix Sawgrass/slough 0 1 2 3 4 5 Km Nutrient inputs resulted in changes in vegetation Sawgrass Introduction Anaerobic Carbon Cycle Cellulose degradation Fermentation Syntrophy Methanogenesis Homoacetogenesis Sulfate Reduction Plant Detritus Monomers and Oligomers Methanotrophs ANAEROBIC Fermentative (propionate, butyrate, etc); alcohols H 2 and CO 2 Homo Bacteria acetogens Syntrophic Bacteria Acetate Acetate Sulfate Reducing Bacteria H 2 S and CO 2 H 2 and CO 2 Methanogens CH 4 Acetate Cellulose Degradation Aerobic Anaerobic Endoglucanase Glucosidase Exoglucanase Lynd et al. 2002. Microbiol.Mol. Biol. Rev. 66(3): 506-577. Fermentation An energy-yielding metabolic process in which an organic compound serves as both an electron donor and an electron acceptor. (Madigan et al. 1997. Brock Biology of Microorganisms) Lactate Propionate Ethanol Glucose H2 Butanol CO2 Butyrate Acetone Acetate Syntrophs Methanogens Methane H2 utilizing bacteria Genus Clostridium – Gram positive – Endospore forming – Obligate anaerobic – Contains the majority of anaerobic cellulolytic bacteria. – Also contains noncellulolytic fermentation bacteria. – Highly diverse in 16S rRNA gene sequence and divided into 19 clusters. Cellulose degradation and fermentation are two of the most studied microbial processes in laboratory conditions. However: • Little is known about the ecology of cellulolytic and fermentative bacteria. • Their ecology must be investigated to understand true microbial nature of the Everglades and impact of nutrient loading on carbon cycling mechanism. Hypothesis Composition and metabolism of cellulolytic and fermentative Clostridium group is function of the nutritional status of the Everglades soil. H1: Accumulation of nutrient rich organic material in impacted site correlates with relatively larger population size in cellulolytic community. H2: Nutritional status of soils correlates with the composition of cellulolytic and fermentative species. H3: Impacted soils contain a microbial community that is poised to respond more rapidly to changes in nutritional status compared to nonimpacted soils. Specific Objectives Characterization of fermentation processes and fermentation product pattern under different carbon sources. Assessment of cellulolytic and fermentative bacterial assemblages. Standardization and application of T-RFLP method for the Everglades Soils. Material and Method Soil Samples The Everglades WCA-2A Blue Cypress Marsh – Impacted (F1) zone – Impacted zone – Transition (F4) zone – Nonimpacted zone – Nonimpacted (U3) zone Samples from 0-10 cm depth will be used Most Probable Number (MPN) Counting – Anaerobic Cellulolytic Microorganisms – Fermentative Microorganisms Molecular analysis of MPN dilutions – Universal 16S rRNA gene Primers Isolation of Microorganisms From Soil Samples – Roll tube method (cellulolytic bacteria) – Glucose enrichment and glucose agar plate technique (fermentative bacteria) Objective 1: Fermentation Microcosms – Liquid media with basic nutrients and vitamins – Soil – Carbon source Glucose Cellulose Plant material (dried crushed cattail and sawgrass) Plant material (no P addition in the media) Measurement of fermentation products in microcosms Acetate, butyrate, propionate, lactate, isobutyrate Methane Objective 2: Molecular Ecology Isolate DNA Correct fragment size PCR Soil Clone Mixed rDNA fragment ATCGATCG Sequence clones Transform to E. coli PCR cloning vector Phylogenetic Analysis Analysis of rRNA gene sequences and determination of their places in the taxonomy. In-silico alignment of sequences Creation of phylogenetic tree Objective 3: T-RFLP Analysis Isolate DNA One primer labeled Soil Sp. A PCR Sp. C Sp. B Size of labeled fragment Automatic sequencer Detects labeled fragment Digest with enzymes (Mixed template) Results Results Most Probable Number (MPN): Soil Cellulose Fermentation F1 2.39x105 5.42x106 F4 3.47x105 9.17x106 U3 2.43x104 1.72x106 Soil Cellulose Fermentation Impacted 5.42x105 5.42x106 Nonimpacted 2.11x104 2.21x106 Everglades Blue Cypress Glucose Microcosms 50 1000 Everglades-Impacted Acetate Butyrate Propionate Methane 40 800 30 mM 600 20 400 10 200 0 0 0 20 50 40 60 80 Everglades-Nonimpacted 1000 40 800 30 mM mmole/g methane 600 20 400 10 200 0 0 0 20 40 Time (day) 60 80 mmole/g methane Acetate Butyrate Blue Cypress-Impacted 40 600 30 mM 400 20 Propionate Methane mmole/g methane 200 10 0 0 0 20 40 60 80 Blue Cypress-Nonimpacted 40 600 30 mM 400 mmole/g methane 20 200 10 0 0 0 20 40 Time (day) 60 80 0.1 substitutions/site 100 77 99 Clostridium cellulolyticum Clostridium josui F2 U8 U27 F1 F8 U19 72 T26 T14 99 T8 F14 F7 Bacteroides cellulosolvens U1 Acetivibrio cellulolyticus 100 100 Acetivibrio cellulolyticus Clostridium aldrichii U2 71 T3 U33 Clostridium stercorarium T25 U4 U11 92 F10 U16 Clostridium thermocellum T11 F3 Clostridium acetobutylicum 100 100 Clostridium butyricum Clostridium tetanomorphum Clostridium glycolicum 100 Clostridium bifermentans 100 Clostridium ghonii 86 Clostridium sordellii Rhodococcus opacus 100 89 100 U3 F4 100 Clostridium termitidis Clostridium cellobioparum Clostridium papyrosolvens Fig. Phylogenetic tree of Clostridium cluster III 16S rRNA gene clone sequences obtained from soil samples from F1 (F), F4 (T), U3 (U). Cluster III Cluster I Cluster XI 78 T10 T4 Fig. Phylogenetic tree of Clostridium cluster I 16S rRNA gene clone sequences obtained from soil samples from F1 (F), F4 (T), U3 (U). F1 Clostridium quinii T21 65 T6 83 T5 63 Clostridium disporicum T1 95 T30 Clostridium paraputrificum F15 Clostridium chromoreductans T29 Clostridium butyricum 62 Clostridium favososporum U28 T36 Clostridium acetobutylicum T41 T16 93 Clostridium saccharobutylicum Clostridium saccharoperbutylacetonicum Clostridium cellulovorans 68 100 Sarcina ventriculi Sarcina maxima 86 Clostridium fallax F18 86 Clostridium bowmanii 60 T2 72 Clostridium tunisiense 94 Clostridium argentinense Clostridium tetanomorphum 100 Clostridium pasteurianum Clostridium acidisoli U44 Clostridium ragsdalei Clostridium carboxidivorans 60 76 T24 79 Clostridium magnum T26 65 F1, F4 and U3 0.1 substitutions/site Only F1 and U3 95 U3-9 100 F1-19 F1-13 F1-26 F1-8 F1-2 U3-33 U3-22 100 U3-1 100 U3-20 U15 100 F1-25 99 F1-20 F3 U3-7 U3-19 100 U5 U3-30 62 92 100 T12 F17 T3 Clostridium glycolicum Clostridium mangenotii 80 Clostridium bifermentans 100 96 Clostridium ghonii Clostridium sordellii Clostridium thermocellum Clostridium cellulolyticum 100 Clostridium termitidis Clostridium papyrosolvens 100 100 100 100 Rhodococcus opacus Cluster XI Cluster III Summary Impacted soils shows higher and faster metabolic activity. – Fermentation process seems to be similar in impacted and nonimpacted soil microcosms. (Based on glucose depletion and acetate production trend data) – Difference in fatty acid accumulation and depletion pattern may be more dependent of syntrophic activity rather than type of fermentation bacteria. Summary Based on microcosm studies, type of plant material as carbon and nutrient source does not appear to be important in the Everglades soils. created significant difference in Blue Cypress Marsh. Summary Microbial community structure is affected by the nutrient loading. – It is a possibility that the composition of fermentation bacteria depend on activity of higher trophic bacterial groups. – Differences observed in phylogenetic analysis may be used as indicator to monitor bacterial changes. Summary Impacted sites contain larger celluloytic community. THANK YOU