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•• THERMODYNAMICS OF GROWTH -contTHERMODYNAMICS OF GROWTH -cont’’dd
•• APPLICATIONS of MICROBIAL APPLICATIONS of MICROBIAL CHEMOLITHOTROPHY & ANAEROBIC RESP.CHEMOLITHOTROPHY & ANAEROBIC RESP.
Systems MicrobiologyWeds Sept 20 - Ch 5 & Ch 17 (p 533-555)
Bioenergetics & Metab.Diversity•• BASIC MODES OF ENERGY GENERATIONBASIC MODES OF ENERGY GENERATION
Phototrophs (Use Light as Energy Source )
Photoautotrophs (Use CO2)
Photoheterotrophs (Use Organic Carbon)
Figure by MIT OCW.
Anoxygenic photoautotrophs utilize cyclicphotophosphorylation
Light
Excited electrons (2 e-)
Electron transport chain
Energy for productionof ATP
Electron carrier
Cyclic Photophosphorylation
Chlorophyll
ATP
Figure by MIT OCW.
LOTS OF DIVERSITY IN BACTERIAL ANOXYGENIC PHOTOTROPHS !
+0.5
+0.25
-0.25E0'(V)
-0.5
-0.75
-1.0
-1.25
0
P870
Purple Bacteria Green Sulfur Bacteria Heliobacteria
Fd
P870
NADH
Reverse electron flow
QCytbc1
Light
Cytc2
BChlBPh
Light Light
Fd
P840
Chl a
QQCyt
bc1Cytc553
Cytc553P840
P798
Chl a-OH
FeS FeS
Cytbc1
P798
Figure by MIT OCW.
+1.0
+0.75 H2O
O2 + 2H12
e-
+0.5
+0.25
0.0
-0.25
-0.5
-0.75
-1.0
-1.25
LightPhotosystem I
Photosystem II
E0(V)
'
LightP680
Cyclic electron flow(generates proton motive force)
Noncyclicelectron flow(generates protonmotive force)
FeS
Pc
QB
Q pool
Chl a0
P680*
NAD(P)HNAD(P)+
P700
Cyt bf
P700*
Fd
Fp
QA
Ph
QA
PSII PSI
The Z Scheme
Figure by MIT OCW.
HALOARCHAEAHALOARCHAEALive in Live in hypersaline hypersaline habitatshabitats
Aerial photograph of haloarchaea changing the colors of their saltwater habitats removed due to copyright restrictions.
Microbial rhodopsins fall into two main functional classes
Sensory rhodopsinsLight-driven ion pumps
Figure by MIT OCW.
Bacteriorhodpsin
BR
H+
Cl-
HR Htrl
His-kinase
Regulator
Regulator
Regulator
His-kinase
P
P
Methylation helices
SRll HtrllSRl
Flagellar motor
Rhodopsin Functional Diversity
Cytoplasm
Bacteriorhodopsin and proteorhodospinLight driven proton pumps
High H+ concentration
Outside cell
Inside cell
Electrons from NADH or chlorophyll
ADP+ Pi
Low H+ concentration
H+ H+
1
2
3
ATP
} Membrane
ATPsynthase
Electron transport chain (includes proton pumps)
Figure by MIT OCW.
Figure by MIT OCW.
Cell interior
Cell exterior
Asp-85
Arg-82
Asp-96
Glu-204
H+
H+
Glu-194
Retinal
Images and diagrams of various rhodopsins removed due to copyright restrictions.See Science 289 (September 15, 2000). www.sciencemag.org.
Venter et al., Environmental Genome ShotgunSequencing of the Sargasso Sea,
Science 394:66-74 (2004)
Many new bacterialproteorhodopsins discoveredin environmetnal shotgunsequencing
Diagram removed due to copyright restrictions.
ALL ORGANISMS
chemotrophs phototrophs
chemolithotrophs chemoorganotrophs
Where do organisms get their energy?
Oxidize inorganic compounds Oxidize organic compounds
Derive energy from light
MICROBIALMICROBIALMETABOLIC METABOLIC DIVERSITYDIVERSITY
Relative VoltageRelative VoltageREDUCTANTS (EAT) OXIDANTS (BREATHE)
-10
- 8
- 6
- 4
- 2
0
+ 2
+ 4
+ 6
+ 8
+ 10
+ 12
+ 14
-10
- 8
- 6
- 4
- 2
0
+ 2
+ 4 + 6
+ 8
+ 10 + 12
+ 14
OrganicCarbon
CO2
SO4=
AsO43-
FeOOH
SeO3NO2
-
NO3-
MnO2
NO3-/N2
O2
H2
H2SSo
Fe(II)
NH4+
Mn(II)
A
B
Photoreductants
Microbes can
eat & breathe just
about anything !
Diagrams removed due to copyright restrictions.See Figures 5-22a, 5-20, and 5-23 in Madigan, Michael, and John Martinko. Brock Biology of Microorganisms.11th ed. Upper Saddle River, NJ: Pearson Prentice Hall, 2006. ISBN: 0131443291.
Chemolithoautotroph (chemo [chemical], litho [rock], auto[self], troph [feeding])Energy source: inorganic substrates (H2, NH3, NO2-, H2S, Fe2+)Carbon source: CO2
e- acceptor: O2(aerobes), or S(some anaerobes), Fe3+, NO3, SO4
Chemolithoautotrophs can be grouped according to the inorganic compounds that they oxidize for energy:Nitrifiers - Oxidize reduced Nitrogen compounds such as NH4+
Sulfur Oxidizers- Oxidize reduced Sulfur compounds such as H2S, S0, and S2O-
Iron Oxidizers- Oxidize reduced Iron-Fe2+ (ferrous iron)
Hydrogen Oxidizers-Oxidize Hydrogen gas-H2
METABOLIC DIVERSITY - Continued ….
Table of energy yields from the oxidation of various inorganic electron donors removed due to copyright restrictions. See Table 17-1 in Madigan, Michael, and John Martinko. Brock Biology of Microorganisms. 11th ed.Upper Saddle River, NJ: Pearson Prentice Hall, 2006. ISBN: 0131443291.
CHEMOLITHOTROPHIC AMMONIA OXIDATION - AEROBIC
NH4+ + 3/2O2 --> NO2
- + H2O + 2H+
NH2OH
NH2OH+ H2O
+ H2O
+ O2+ 2H+NH3 H2O
O2 + 4H+
O
O-N + 5H+
Oxidation of hydroxylamine
2H+H+
H+
ADP + Pi
ATP
12
Oxidation of ammonia
Reduction of oxygen
HAO
AMO
4e- 2e-Cyt c
Cyt c
Q Cyt aa3
2e-2e-
2e-
Periplasm
Figure by MIT OCW.
Anammox means "anaerobic ammonium oxidation". Anammox is both a new low-cost method ofN-removal in wastewater treatment, and a spectacular microbial way of life - woo - woo !
CHEMOLITHOTROPHIC AMMONIA OXIDATION -
ANAEROBIC
Courtesy of the Department of Microbiology at Radboud University Nijmegen. Used with permission.
ΔEo= Eo (electron acceptor) - Eo (electron donor) = 1233 mV
2NH4+/N2 half reaction (6e-) Eo = -0.277 V
2NO2-/N2 half reaction (6e-) Eo = +0.956 V
ΔGo=-nF ΔEo= -(3) (96.5 kJ/Vmol)(1.233V) = - 357 kJ/mol
Broda predicted, based solely on the thermodynamics, that suchmicroorganisms should exist. (And also the fact that if abioenergetically favorable niche exists, a microbe will evolveto fill it !).
About a decade later, the ’ bugs’ were discovered in bioreactorsstarted from waste water treatment plants.
Compared to conventionalnitrification/denitrification, thismethod saves 100% of the carbonsource, & 50% of the requiredoxygen. This leads to a reduction ofoperational costs of 90%, a decreasein CO2 emissions of more than 100%(the process actually consumes CO2),and a decrease in energy demand.
Photograph removed due to copyright restrictions
Anaerobic ammonium oxidation by anammox bacteria in the Black Sea Marcel M. M. Kuypers, A. Olav Sliekers, Gaute Lavik, Markus Schmid, Bo Barker Jørgensen, J. Gijs Kuenen, Jaap S. Sinninghe Damsté, Marc Strous and Mike S. M. Jetten. Nature 422, 608-611 (10 April 2003)
Graphs removed due to copyright restrictions.
Denitrification = Use of NO3- as terminal electron acceptor, that results
in complete conversion to N2 gas.
See Figures 17-35 and 17-37 in Madigan, Michael, and John Martinko. Brock Biology of Microorganisms. 11th ed. Upper Saddle River, NJ: Pearson Prentice Hall, 2006. ISBN: 0131443291.
Diagrams removed due to copyright restrictions.
Geobacter growing on iron oxides
CH3COO- Fe3+
e-
Fe2+CO2
Anaerobic respiration
Image of geobacter growing on iron oxides removed due to copyright restrictions.
Complex Organic Matter
Hydrolysis
Fermentable Substrates
H2 Acetate
Microbial Competition for Substrates
Other low molecular weight organic acids}
NO3- reducers
Mn(IV) reducersFe(III) reducersSO4
2- reducersMethanogens
}Organic Matter Degradation In Anaerobic Environments
Fermentation
Figure by MIT OCW.
E- acceptor ΔGo’ (using glucose)
Oxygen -3190 kJ/mol
NO3- -3030
Mn (IV) -3090
Fe(III) -1410
Sulfate -380
CO2 -350
From Nealson and Saffarini 1994
Energetic explains order: not all e-acceptors are equal!
25
Complex Assemblage of Organic Matter
Hydrolysis into Constituents
Fermentable Sugars and Amino Acids
Fermentation by a Fermentative Microbial Consortium
Acetate and Minor Products Aromatic CompoundsLong-Chain Fatty Acid
Fe3+ Oxide
Fe2+
Geobacter spp.
CO2
Generalized pathway for the anaerobic oxidation of organic matter to carbon dioxide with Fe3+ oxide serving as an electron acceptor in temperate, freshwater and sedimentary environments. The process is mediated by a consortium of fermentative microorganisms and Geobacter species.
Figure by MIT OCW.
Source
Methanogenic
SO4 reduction2
Fe(III) reduction
Mn(IV) reduction
NO3 (IV) reduction Aerobic
Groundwater flow
-
High O2
Low O2
High organics
Figure by MIT OCW.
The distribution of terminal electron-accepting processes (TEAPs) observed within anaerobic portions of aquiferscontaminated with organic compounds.
Images removed due to copyright restrictions.See Lovley, D. R., E. J. P. Phillips, Y. A. Gorby, and E. R. Landa. "Microbial Reduction of Uranium." Nature 350 (1991): 413-416.
Anaerobic respiration to “clean up” of uranium pollution
Acetate + U (VI) U (IV)s + CO2
CH3C00- + 4 U(VI)U (IV)s + 2HCO3- + 9H+
Carried out by Geobacter
Example of “bioremediation”Lovley DR, Phillips EJP, Gorby YA, Landa ER. Microbial Reduction of Uranium, 1991, Nature.350(6317): 413-6.
Soluble= mobile Insoluble, immobile
Photograph removed due to copyright restrictions.
Diagram removed due to copyright restrictions. See Bond, Holmes, Tender, and Lovley. Science 295 (2002): 483-485.
Correspondence between pilus current and applied voltage demonstrating the linear, ohmic, response characteristic of a true conductor.
Schematic of the electronic connection of the AFM tip in a conducting probe atomic force microscope (CP-AFM). HOPG, highly oriented pyrolytic graphite.
Atomic force microscope stage
V=IR
Extracellular electron transfer via microbial nanowires.Nature. 2005 Jun 23;435(7045):1098-101.
DNS
SO42-
SO42- Diffusion
Sea FloorSeawater
METHANE FLUX
Sulfa
te Re
ducti
on Z
one
AB
CDNS
Figure by MIT OCW.
AANAEROBIC NAEROBIC MMETHANE ETHANE OOXIDATIONXIDATION
Geochemical Observations:Geochemical Observations:CH4 + SO4
2- HCO3- + HS- + H2O
Microbiologically ???CH4 + 2H2O CO2 + 4H2 “Reverse Methanogenesis”
HSO4- + 4H2 HS- + 4H2O Sulfate reduction ΔGo’ = -156 kJ/mol
ΔGo’ = +131 kJ/mol
CH4 + HSO42- CO2
+ HS- + 2H2O ΔGo’ = -25 kJ/mol