This document discusses several types of anaerobic microbes that are important in the global methane and nitrogen cycles. It describes the discovery of anaerobic ammonium oxidizing (anammox) bacteria, which were long considered "impossible" microbes. It also discusses the recent discovery of complete ammonium-oxidizing (comammox) bacteria in the genus Nitrospira. Finally, it covers anaerobic oxidation of methane (AOM) coupled to the reduction of nitrate or nitrite, and the microbes involved in these processes, including Methylomirabilis and Methanoperedens species.
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“Impossible” anaerobic microbes
important in the global
Methane and Nitrogen Cycles
BSM December 11th 2015
MIKE JETTEN
GRAVITATION CENTER OF EXCELLENCE
SOEHNGEN INSTITUTE OF ANAEROBIC MICROBIOLOGY
(SIAM)
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TABLE of CONTENT
Introduction (anaerobic) microbiology
1. Anaerobic oxidation of ammonium (anammox)
2. Complete ammonium oxidation (comammox)
3. Anaerobic oxidation of methane (AOM)
4. Latest sampling campaigns
5. Take home message
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Many very useful (anaerobic) microbes
–Wastewater treatment
–Oxygen production
–Nitrogen fixation
–Food and fermentation
–Drugs and Antibiotics
–Degradation of xenobiotics
Very few pathogens
Earth = Microbial planet
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Many very useful (anaerobic) microbes
–Wastewater treatment
–Oxygen production
–Nitrogen fixation
–Food and fermentation
–Drugs and Antibiotics
–Degradation of xenobiotics
Very few pathogens
Earth = Microbial planet
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Under explored microbial diversity
40,000 trains in DMSZ, LMGBC & ATCC
3,224,600 16S rRNA genes in RDP
10,000,000,000,000,000,000,000,000,000,000 Nonillion microbial cells on Earth
Terra incognita
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Microbial Metabolic Diversity
CH4
NH4
+ & CH4
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The Quest for the “Impossible” Microbes
H2 CH4 H2S NH4
+ Fe2+
O2
NO3
-
??? ???
Fe3+
SO4
2-
CO2
After 40 years of searching in vain
They were being called
“impossible” microbes
ELECTRON DONORS
ELECTRONACCEPTORS
OXIC
ANOXIC
??? ???
???
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H2 CH4 H2S NH4
+ Fe2+
O2
NO3
-
??? ???
Fe3+
SO4
2-
CO2
After 40 years of searching in vain
They were being called
“impossible” microbes
ELECTRON DONORS
ELECTRONACCEPTORS
OXIC
ANOXIC
CS2
???
The Quest for the “Impossible” Microbes
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HOW TO DISCOVER THESE “IMPOSSIBLE” MICROBES?
• Survey of selected ecosystems
• Bring Best Samples to Lab
• Design optimal bioreactors
• Enrichment under optimal conditions
• Grow enough cells
• Use of the molecular toolbox to
unravel their secrets
• Back to the ecosystem
• Application of the new microbes
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Absolute prerequisite
Excellently Educated & Enthusiastic Team Members
www.ru.nl/microbiology/vacancies
www.ru.nl/masters/microbiology
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Prerequisite 2 State-of-the-Art Methods
Bioreactors Bioreactors Bioreactors
Bioreactors Bioreactors Bioreactors
Metagenomics, bioinformatics, new experiments
illumina, minion
pacbio
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TABLE OF CONTENT
Introduction anaerobic microbiology
1. Anaerobic oxidation of ammonium (anammox)
2. Complete ammonium oxidation (comammox)
3. Anaerobic oxidation of methane (AOM)
4. Latest sampling campaigns
5. Take home messages
Ammonium & Nitrate: toxicity & eutrophication
Nitrite & Nitric oxide : toxicity
Nitrous oxide : strong green house gas
ERC AG 2008
anammox
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Calculations in the N cycle
NH4
+ + NO2
- N2 + 2H2O ΔG’0 = -358 kJ/mol
Engelbert Broda 1910-1983
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Anaerobic pilot plant, TU Delft, the Netherlands
Influent
Effluent
Mulder , van de Graaf et al FEMS Ecology 1995
Mulder et al FEMS 1995; van de Graaf et al AEM 1995
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ANAMMOX MILESTONES
ANAEROBIC PILOT PLANT
Mulder et al FEMS 1995
SBR ENRICHMENT CULTURES
Strous et al AMB 1998
PHYLOGENETIC IDENTITY
Strous et al Nature 1999
LADDERANE LIPIDS
Damste et al Nature 2002
BLACK SEA Kuypers et al Nature 2003
Namibia OMZ Kuypers et al PNAS 2005
Peru OMZ Lam et al Nature 2007
Jettenia asiatica
Jettenia caeni
Jettenia moscovienisis
OMZs: 50% N loss
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ANAMMOX MILESTONES
GENOME ASSEMBLY
Strous et al Nature 2006
CELL BIOLOGY
Van Niftrik & Jetten MMBR 2012
METABOLISM
Kartal et al Nature 2013
CHINESE WETLANDS
Zhu et al Nature Geoscience 2013
Zhu et al Sci report 2015
PEPTIDOGLYCAN DETECTED
van Teeseling et al Nature comm 2015
PROTEIN STRUCTURES
Dietl et al Nature 2015
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How does ANAMMOX make the rocket fuel hydrazine?
Protein
purification
15N14N
Protein activity
Hydrazine and N2 production
Protein crystalisationImmunogold labelling hzsABC
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Microbial interactions of ANAMMOX bacteria
High NH4
+
Low O2 AOB
Sliekers et al 2002
NO2
-
Low NH4
+
Low O2 AOA
Yan et al 2012
Low NO3
-
Low O2 Nitrospira
Van Kessel et al
Nature 2015
High S2- NO3
-
No O2 DNRA
Lam et al 2008
Russ et al 2014
Low NO3
-
No O2 Denitrifiers
Russ et al 2015
High CH4
No O2
AAA/Moxyfera
Luesken et al 2012
Haroon et al 2013
Anammox
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Microbial interactions of ANAMMOX bacteria
High NH4
+
Low O2 AOB
Sliekers et al 2002
NO2
-
Low NH4
+
Low O2 AOA
Yan et al 2012
Low NO3
-
Low O2 Nitrospira
Van Kessel et al
Nature 2015
High S2- NO3
-
No O2 DNRA
Lam et al 2008
Russ et al 2014
Low NO3
-
No O2 Denitrifiers
Russ et al 2015
High CH4
No O2
AAA/Moxyfera
Luesken et al 2012
Haroon et al 2013
Anammox
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NH4
+ + 1.5 O2 NO2
- AOB/AOA
NO2
- + 0.5 O2 NO3
- NOB
NH4
+ + 2 O2 NO3
- ?
Complete ammonium oxidiser (comammox)
ERC AG 2008
anammox
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• Inoculum: Biofilm from aquaculture biofilter
• Medium: Aquaculture water, plus low [NH4
+, NO2
-,
NO3
-] ; No extra carbon source; No O2 supply
Conditions for anaerobic ammonia oxidizers
(Anammox)
After1 year good NH4
+ plus NO2
- consumption
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15N activity assays; N balance does NOT add up
• Labelled substrates: 15NH4
+
• Anammox activity is higher than possible based on NO2
- conversion
• Where is this additional NO2
- coming from?
Increase in ratio 29N2
=
conversion of NH4
+ in gas
Maartje van Kessel
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Fluorescence in situ hybridization
• Nitrospira is always present in flocs with anammox
• Stable coculture; cross feeding?
pink = anammox; green = Nitrospira; blue= all bacteria
Januari 2012 November 2012
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Metagenome sequencing, assembly and coverage binning
• Recovery of two high quality Nitrospira genomes
• Nitrospira nitrificans & Nitrospira nitrosa
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Metagenomic analyses: complete ammonium oxidiser
Only in ammonium oxidizers
Only in nitrite oxidizers
• Both Nitrospira spp. genomes contain genes for
- Ammonia monooxygenase
- Hydroxylamine dehydrogenase
- Nitrite oxidoreductase
Experimental validation
Test with ATU = amo inhibitor
Test with FISH MAR
Test with specific AMO labeling
Sebastian Luecker
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Comammox : Aerobic batch incubation assays
NH4
+ oxidation w/o ATU
NH4
+ oxidation with ATU
Shows full inhibition
NO2
- oxidation
Maartje van Kessel
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Specific AMO activity staining by fluorescent dye FTCP
red = Nitrospira
green = FTCP
blue= all bacteria
White = overlay
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• Comammox does exist!
• Nitrospira species
• unusual/novel amoA gene
• Implications;
- N-cycle research
- Wastewater treatment plants
NO3
-
NO2
-
NH4
+
N2
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TABLE OF CONTENT
Introduction anaerobic microbiology
1. Anaerobic oxidation of ammonium (anammox)
2. Complete ammonium oxidation (comammox)
3. Anaerobic oxidation of methane (AOM)
3. Latest sampling campaigns
4. Take home messages
ERC AG 2013
EcoMoM
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Theoretical considerations
Also with nitrate
3 CH4 + 8 NO2
- + 8 H+ 3 CO2 + 4 N2 + 10 H2O
∆G0’ = -928 kJ mol-1 CH4
Energetically feasible, should exist in nature
• important greenhouse gas, global warming potential
about 25x that of CO2
• atmospheric concentrations have doubled since
industrialization
• one of the main products of anaerobic
decomposition of organic material
• energy-rich, but high activation energy (for a long
time only aerobic degradation was known)
Significance of methane
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Schulze et al. (2010), Global Change Biology
Natural methane sources
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Wetlands are important sources for methane
Methane Sinks:
aerobic and anaerobic methane munching microbes
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Aerobic methane oxidation
Nitrite dependent anaerobic methane oxidation
Nitrate dependent anaerobic methane oxidation
Quest for Nitrate/Nitrite AOM
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HIGH NO3
- due to agricultural run-off /ground water
HIGH CH4 production in the sediment
sampling sites
Twente
kanaalBrunsummerheide
Ooij
polder
Where do we find nitrate/nitrite-AOM?
Vercelli Paddy fields
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Suitable counter gradient profiles of nitrate & methane
-250
-200
-150
-100
-50
0
-100 0 100 200 300 400 500
NO3-
NH4+
CH4
depth[cm]
concentration[µmol/L]
Nutrient profile
Activity tests
qPCR
Enrichment
FISH
Metagenome
Stable isotopes
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Activity assays of soil samples
0,0
0,2
0,4
0,6
0,8
1,0
1,2
1,4
1,6
1,8
2,0
0 20 40 60
umol/gdryweight
Time (days)
NO3
NO3
Control
CH4
Control
CH4
Annika
Vaksmaa
Vaksmaa et al FEMS Microbiology Ecology submitted
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Incubation set up
Sediment slurry in mineral medium
Fe(OH)3 or MnO2 nanoparticles
13CH4 (~50%)
12CO2 (~5%)
Headspace gas analysis: GC-MS Ion measurements: ICP-OES
Anaerobic set-up
Egger, Rasigraf et al EST 2014
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13CH4 oxidation to 13CO2 coupled to Fe3+ reduction
0
1
2
3
4
5
0 20 40 60 80 100 120
13CO2[µmol]
control
days
Egger, Rasigraf et al EST 2014
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0
1
2
3
4
5
0 20 40 60 80 100 120
13CO2[µmol]
only 13CH4
control
days
13CH4 oxidation to 13CO2 coupled to Fe3+ reduction
Egger, Rasigraf et al EST 2014
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0
1
2
3
4
5
6
0 20 40 60 80 100 120
13CO2[µmol]
only 13CH4
13CH4 & Fe3+
control
days
13CH4 oxidation to 13CO2 coupled to Fe3+ reduction
Egger, Rasigraf et al EST 2014
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0
1
2
3
4
5
6
0 20 40 60 80 100 120
13CO2[µmol]
only 13CH4
13CH4 & Fe3+
control
Fe3+ injection
days
13CH4 oxidation to 13CO2 coupled to Fe3+ reduction
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Anammox, Comammox, Moxyfera, AAA and other new
(an)aerobic microbes could save the world
Unique bacteria hiding out in a witches’ brew of anoxic
water not only thrive in cold wetlands and oceans but
also chow down its ammonium and methane