SlideShare a Scribd company logo
1 of 1
Download to read offline
3.	Methods
Preparation:
The upper 3 cm of sediment from three sediment cores collected during October 2015 were used to
enrich for Beggiatoa spp. The presence of Beggiatoa spp. filaments in the sediments was confirmed
by microscopy. Homogenized sediment slurry and shredded paper were added to Hungate tubes.
Enrichment conditions:
• MIS groundwater was added to two different heights.
• 8 tubes were loosely covered with a thin piece of aluminum foil, simulating aerobic conditions;
4 were induced to anaerobic conditions by being tightly capped; the remaining 4 had a hypodermic
needle inserted in the middle of the rubber cap, permitting microaerobic growth (Fig. 2).
• As an alternative potential terminal electron acceptor to O2 for SOB, 0.5 mL of 20 µM nitrate
solution was added to 8 tubes from each treatment, to a final concentration of 1 - 5µM.
• Half of the tubes were incubated in the dark without agitation at 8.6oC (in the following referred to
as “cold”) which resembles the temperature of the sinkhole environment. The other half was
incubated in the dark on an orbital shaker (100 RPM) at 20.0˚C (“room temperature”), to gently
move the water column and simulate the groundwater flow environment.
Observation:
The tubes were checked weekly for a month and any growth of sulfide oxidizing bacterial filaments,
namely Beggiatoa spp., was documented.
1.	Introduction
• The underwater Middle Island Sinkhole (MIS) is a photic,
sulfidic, and low-oxygen modern system to understand
microbial life on early Earth.
• Members of Beggiatoa, a genus of filamentous sulfide-
oxidizing bacteria (SOB), live in cyanobacterial-dominated
microbial mats in MIS. Beggiatoa spp. can be found in
either freshwater or marine environments, and are key
autotrophs in light-limited environments such as deep-sea
hydrothermal vents and seeps (Preisler et al., 2007).
• The characteristics and activity of MIS Beggiatoa are of
particular interest due to their unique interaction with the
cyanobacteria. The white filaments cover the purple
cyanobacterial layer during the night but migrate
underneath the purple layer during the day (Biddanda et
al., 2012).
2.	Research	goal	
To	optimize	growth	conditions	for	Middle	Island	Sinkhole	(MIS)	sulfide	oxidizing	bacteria	in	order	to	
isolate	a	pure	culture	of	Beggiatoaspp.	for	future	physiological	and	ecological	studies.	
7.	Acknowledgements	and	References	
We	thanks	Matthew	Medina	and	the	NOAA	Thunder	Bay	National	Marine	Sanctuary,	including	
captains	and	scuba	divers	and	especially	Russ	Green,	John	Bright,	Wayne	Lusardi,	and	Phil	
Hartmeyer.	 This	work	was	supported	by	NSF	grant	EAR-1637066	to	GJD.
Biddanda,	Bopaiah A.,	Stephen	C.	Nold,	Gregory	J.	Dick,	S.	T.	Kendall,	J.	H.	Vail,	S.	A.	Ruberg,	and	C.	M.	Green.	2012.	"Rock,	water,	microbes:	underwater	
sinkholes	in	Lake	Huron	are	habitats	for	ancient	microbial	life."	Nature	Education	Knowledge	3:	13.	
Kinsman-Costello,	L.	E.,	Sheik,	C.	S.,	Sheldon,	N.	D.,	Allen	Burton,	G.,	Costello,	D.	M.,	Marcus,	D.,	...	&	Dick,	G.	J.	.2016.	“Groundwater	shapes	sediment	
biogeochemistry	and	microbial	diversity	in	a	submerged	Great	Lake	sinkhole.” Geobiology
Preisler,	André,	Dirk	De	Beer,	Anna	Lichtschlag,	Gaute Lavik,	Antje	Boetius,	and	Bo	Barker	Jørgensen.	2007.	"Biological	and	chemical	sulfide oxidation	in	
a	Beggiatoa inhabited	marine	sediment."	The	ISME	journal	1,	no.	4:	341-353.
4.	Results	and	Analysis	
Understanding	growth	and	activity	of	Beggiatoa spp.	from	a	low-oxygen	environment
Hui	Chien	Tan1,	Judith	Klatt2,	Sharon	Grim3 and	Gregory	J.	Dick1
1,2,3,4Earth	and	Environmental	Sciences,	University	of	Michigan,	Ann	Arbor,	USA
After	a	month	of	weekly	observations,	white	filaments	were	absent	in	the	anaerobic	conditions	but	present	in	both	microaerobic and	aerobic	conditions.	Close	inspection	
revealed	disparity	in	the	growth	of	white	filaments	between	those	in	the	cold	environment	and	those	in	the	room-temperature	environment	(Table	1).
A B C D
Figure 3: A. An absence of growth was noted in the anaerobic tubes. B. Muddy yellow mesh growing
near the water level whereas white filament strands were found on the sediments (shown in red rings).
C. Muddy yellow clump potentially representing elemental sulfur. D. White filaments growing around red
tufts along with white ring formation near water surface.
Figure 4: SOB under 40x magnification
5.	Discussion	and	Conclusion
We observed the best growth of SOB, likely Beggiatoa spp., in dark
and microaerobic/aerobic conditions. Though some members of
Beggiatoa are known to use nitrate in sulfide oxidation, we conclude
that nitrate cannot be used efficiently as an alternative terminal
electron acceptor for MIS Beggiatoa. We have four lines of support
for MIS Beggiatoa using oxygen, not nitrate, for sulfide oxidation:
1. We observed migration of SOB filaments in aerobic and
microaerobic treatments, towards the water surface where
atmospheric exchange introduced oxygen.
2. There were insubstantial differences in SOB growth between +/-
nitrate in the aerobic conditions.
3. We did not observe Beggiatoa growth in nitrate-amended,
anaerobic tubes.
4. Low nitrate concentrations in the ambient groundwater (Kinsman-
Costello et al., 2016) support our observation that MIS Beggiatoa
are not cued to use nitrate in their metabolism.
The formation of white rings near the water level provided insight on
the migration pattern of the white mat at MIS. Previous field
observations and laboratory experiments suggest that MIS Beggiatoa
motility is linked to oxygen demand: the oxygenic photosynthetic
cyanobacterial layer likely satisfies their oxygen requirements during
the day, so the SOB reside within and below the cyanobacterial mat;
whereas at night they are the top layer of the microbial mat,
putatively to acquire oxygen from the low-oxygen water column.
• Unlike the tufts of filaments in the tubes found in the cold environment, after two weeks
the color of the tufts at room temperature changed into muddy yellow, putatively
elemental sulfur, a chemical product of sulfide oxidation (Fig. 3 B). The formation of
elemental sulfur was likely derived from competing non-filamentous SOB instead of
Beggiatoa spp. because they do not store elemental sulfur extracellularly.
• The cold growth tubes did not develop muddy yellow tufts; instead, two different colored
filaments (dark red and white) grew together (Fig. 3 C and D). The absence of muddy
yellow tufts in cold-incubated tubes might be related to the presence of the dark red
filaments (likely cyanobacteria) and/or the incubation temperature.
• The white rings were situated about 0.4 cm from the water level surface regardless of the
height of the water column. Microscopy confirmed the presence of filamentous SOB with
intracellular refractive elemental sulfur inclusions, likely Beggiatoa spp., within the white
rings (Fig 4).
We are attempting to isolate Beggiatoa spp. from our enrichments using gradient media that
simulates the natural sediment biogeochemistry. For our first attempt, instead of the targeted
SOB, another species of unknown white rod-shaped bacteria were growing in the gradient
media (Fig. 5). The rod-shaped bacteria likely belong to the genus Thiobacillus. This lead us to
our second attempt where the gradient media consists of autoclaved MIS sediments on a
sulfidic agar plug (Fig. 6). Similar to the presented multivariate experiment, the tubes simulate
aerobic, anaerobic, and microaerobic environments.
Figure	5:	
Unknown	white	
bacteria	under	
40x	magnification
Figure	6: 2nd
attempt	gradient	
media	setup	for	
culturing	
Beggiatoa spp.	
Figure 1: The observed migration pattern
of Beggiatoa spp. (Adapted from Biddanda
et al., 2012)
Table	1:	Observations	of	microbial	growth	in	a	
multivariate	environment	
WF	=	White	Filaments	(growing	on	sediments)
WR	=	White	ring	(near	water	level)
YR	=	Yellow	ring	(near	water	level)	
DRF	=	Dark	Red	Filaments	
A B C
Figure	2:	The	pictures	of	tubes	in	different	environmental	simulations	(in	order):	
A.	anaerobic,	B.	microaerobic,	C.	aerobic	conditions.
Condition Shaken Temp.
Water	
column
+	Nitrate 1st Week 2nd Week 3rd Week 4th Week
Aerobic
Yes 20.0oC
2mL
Yes
Faint	WR	and	WF
Tuft	in	the	water	column	and	WF
Muddy	yellow	clump	in	the	water	column	and	WF
No YR	and	WF
10mL
Yes No	growth	of	WF Minimal	WF White	thin	layer	of	WF White	mesh	with	muddy	yellow	clump	and	WF
No Growth	of	WF Muddy	YR, white	mesh	layer	and	WF
No 8.6oC
2mL
Yes
WF	patches	with	DRF	growing	on	top WR	and	WF	patches	with	DRF	growing	on	top
No
10mL
Yes
No	growth	of	WF Growth	of	DRF Thin	WR	and	DRF
No
Anaerobic
Yes 20.0oC
10mL
Yes
No	growth	of	WF
No
No 8.6oC
Yes
No	growth	of	WF	but	dark	red	filaments	were	observed
No
Micro-
aerobic
Yes 20.0oC
2mL
Yes
Faint	WR	and	WF YR	with	white	mesh	and	WF
No
No 8.6oC
Yes
WF	patches	with	DRF	on	top Faint	WR	and	WF	tufts	with	DRF	on	topNo
6.	Future	Direction

More Related Content

What's hot

Microfossils and their Applications in petroleum Industry
Microfossils and their Applications in petroleum Industry Microfossils and their Applications in petroleum Industry
Microfossils and their Applications in petroleum Industry Sachin Yadav
 
Paleoceanography
PaleoceanographyPaleoceanography
PaleoceanographyDedy Aslam
 
Applications of micro-fossil in bio statigraphy
Applications of micro-fossil in bio statigraphy Applications of micro-fossil in bio statigraphy
Applications of micro-fossil in bio statigraphy Pramoda Raj
 
Silicon compounds in biological systems
Silicon compounds in biological systemsSilicon compounds in biological systems
Silicon compounds in biological systemsPolice
 
Tech seminar
Tech seminarTech seminar
Tech seminarri1236
 
Micropaleontology and foraminifera
Micropaleontology and foraminifera Micropaleontology and foraminifera
Micropaleontology and foraminifera Amna Q.
 
Applications of microfossils
Applications of microfossilsApplications of microfossils
Applications of microfossilsPramoda Raj
 
Foraminifera and its Applications
Foraminifera and its ApplicationsForaminifera and its Applications
Foraminifera and its ApplicationsAditya Bhattacharya
 
Conodont
ConodontConodont
ConodontKomiSC
 
Morphology of ostracods
Morphology  of ostracodsMorphology  of ostracods
Morphology of ostracodsPramoda Raj
 
Nano minerals & their formation
Nano minerals & their formationNano minerals & their formation
Nano minerals & their formationPramoda Raj
 
Bryophyte as bioindicators of pollution
Bryophyte as bioindicators of pollutionBryophyte as bioindicators of pollution
Bryophyte as bioindicators of pollutionANAMIKA RAJ
 
Morphology of foramnifera
Morphology of foramniferaMorphology of foramnifera
Morphology of foramniferaPramoda Raj
 
A comparative study on adsorption behavior of heavy metal elements onto soil ...
A comparative study on adsorption behavior of heavy metal elements onto soil ...A comparative study on adsorption behavior of heavy metal elements onto soil ...
A comparative study on adsorption behavior of heavy metal elements onto soil ...Andre Zeitoun
 
Preventing Clay Swelling
Preventing Clay Swelling Preventing Clay Swelling
Preventing Clay Swelling Omar Radwan
 

What's hot (20)

Calcareous microfossils by Rathinavel
Calcareous microfossils by RathinavelCalcareous microfossils by Rathinavel
Calcareous microfossils by Rathinavel
 
Agu poster 1
Agu poster 1Agu poster 1
Agu poster 1
 
Biofilm Formation asignment
Biofilm Formation asignmentBiofilm Formation asignment
Biofilm Formation asignment
 
Microfossils and their Applications in petroleum Industry
Microfossils and their Applications in petroleum Industry Microfossils and their Applications in petroleum Industry
Microfossils and their Applications in petroleum Industry
 
Paleoceanography
PaleoceanographyPaleoceanography
Paleoceanography
 
Paleoecology
Paleoecology Paleoecology
Paleoecology
 
Applications of micro-fossil in bio statigraphy
Applications of micro-fossil in bio statigraphy Applications of micro-fossil in bio statigraphy
Applications of micro-fossil in bio statigraphy
 
Silicon compounds in biological systems
Silicon compounds in biological systemsSilicon compounds in biological systems
Silicon compounds in biological systems
 
Chitinozoa
ChitinozoaChitinozoa
Chitinozoa
 
Tech seminar
Tech seminarTech seminar
Tech seminar
 
Micropaleontology and foraminifera
Micropaleontology and foraminifera Micropaleontology and foraminifera
Micropaleontology and foraminifera
 
Applications of microfossils
Applications of microfossilsApplications of microfossils
Applications of microfossils
 
Foraminifera and its Applications
Foraminifera and its ApplicationsForaminifera and its Applications
Foraminifera and its Applications
 
Conodont
ConodontConodont
Conodont
 
Morphology of ostracods
Morphology  of ostracodsMorphology  of ostracods
Morphology of ostracods
 
Nano minerals & their formation
Nano minerals & their formationNano minerals & their formation
Nano minerals & their formation
 
Bryophyte as bioindicators of pollution
Bryophyte as bioindicators of pollutionBryophyte as bioindicators of pollution
Bryophyte as bioindicators of pollution
 
Morphology of foramnifera
Morphology of foramniferaMorphology of foramnifera
Morphology of foramnifera
 
A comparative study on adsorption behavior of heavy metal elements onto soil ...
A comparative study on adsorption behavior of heavy metal elements onto soil ...A comparative study on adsorption behavior of heavy metal elements onto soil ...
A comparative study on adsorption behavior of heavy metal elements onto soil ...
 
Preventing Clay Swelling
Preventing Clay Swelling Preventing Clay Swelling
Preventing Clay Swelling
 

Similar to poster_chien_final+jmk

Dan Bower's Phosphate Thesis
Dan Bower's Phosphate ThesisDan Bower's Phosphate Thesis
Dan Bower's Phosphate ThesisDaniel Bower
 
PPT microteaching.pptx
PPT microteaching.pptxPPT microteaching.pptx
PPT microteaching.pptxrizalka
 
SRK-Blue green algae and their mass multiplication
SRK-Blue green algae and their mass multiplicationSRK-Blue green algae and their mass multiplication
SRK-Blue green algae and their mass multiplicationsivaram Krishna
 
Bio mining methods
Bio mining methodsBio mining methods
Bio mining methodsSafdar Ali
 
Application of Foraminiferal Ecology- Rahul.pptx
Application of Foraminiferal Ecology- Rahul.pptxApplication of Foraminiferal Ecology- Rahul.pptx
Application of Foraminiferal Ecology- Rahul.pptxRahulVishwakarma71547
 
Aerobic Granular Sludge A Case Report
Aerobic Granular Sludge A Case ReportAerobic Granular Sludge A Case Report
Aerobic Granular Sludge A Case ReportRichard Hogue
 
green synthesis by silver nano particles
green synthesis by silver nano particlesgreen synthesis by silver nano particles
green synthesis by silver nano particlesPratikGhorpadepatil
 
Ca - Carbonate Production By Heterotrophic Bacteria
Ca - Carbonate Production  By Heterotrophic Bacteria Ca - Carbonate Production  By Heterotrophic Bacteria
Ca - Carbonate Production By Heterotrophic Bacteria Omar Radwan
 
Cyanobacteria as a Biofertilizer (BY- Ayushi).pptx
Cyanobacteria as a Biofertilizer (BY- Ayushi).pptxCyanobacteria as a Biofertilizer (BY- Ayushi).pptx
Cyanobacteria as a Biofertilizer (BY- Ayushi).pptxAyushiKardam
 
Study on Toxic Impact of Sugar Factory Effluent on the Gill of the Fresh Wate...
Study on Toxic Impact of Sugar Factory Effluent on the Gill of the Fresh Wate...Study on Toxic Impact of Sugar Factory Effluent on the Gill of the Fresh Wate...
Study on Toxic Impact of Sugar Factory Effluent on the Gill of the Fresh Wate...IJEAB
 
High Rate of Water Biodenitrification Using Anthracite as Hyphomicrobium Deni...
High Rate of Water Biodenitrification Using Anthracite as Hyphomicrobium Deni...High Rate of Water Biodenitrification Using Anthracite as Hyphomicrobium Deni...
High Rate of Water Biodenitrification Using Anthracite as Hyphomicrobium Deni...theijes
 
Thermus aquaticus gen. n. and sp. n., a nonsporulating extreme thermophile
Thermus aquaticus gen. n. and sp. n., a nonsporulating extreme thermophileThermus aquaticus gen. n. and sp. n., a nonsporulating extreme thermophile
Thermus aquaticus gen. n. and sp. n., a nonsporulating extreme thermophileJosé Luis Moreno Garvayo
 
Azotobacter in microbiology field of study
Azotobacter in microbiology field of studyAzotobacter in microbiology field of study
Azotobacter in microbiology field of studyOENDRILDAS
 

Similar to poster_chien_final+jmk (20)

N Cycle Poster
N Cycle PosterN Cycle Poster
N Cycle Poster
 
Dan Bower's Phosphate Thesis
Dan Bower's Phosphate ThesisDan Bower's Phosphate Thesis
Dan Bower's Phosphate Thesis
 
PPT microteaching.pptx
PPT microteaching.pptxPPT microteaching.pptx
PPT microteaching.pptx
 
Cx32617623
Cx32617623Cx32617623
Cx32617623
 
SRK-Blue green algae and their mass multiplication
SRK-Blue green algae and their mass multiplicationSRK-Blue green algae and their mass multiplication
SRK-Blue green algae and their mass multiplication
 
Cx32617623
Cx32617623Cx32617623
Cx32617623
 
Bio mining methods
Bio mining methodsBio mining methods
Bio mining methods
 
Biodiversity and Microbial Biodiversity
Biodiversity and Microbial BiodiversityBiodiversity and Microbial Biodiversity
Biodiversity and Microbial Biodiversity
 
Application of Foraminiferal Ecology- Rahul.pptx
Application of Foraminiferal Ecology- Rahul.pptxApplication of Foraminiferal Ecology- Rahul.pptx
Application of Foraminiferal Ecology- Rahul.pptx
 
Aerobic Granular Sludge A Case Report
Aerobic Granular Sludge A Case ReportAerobic Granular Sludge A Case Report
Aerobic Granular Sludge A Case Report
 
green synthesis by silver nano particles
green synthesis by silver nano particlesgreen synthesis by silver nano particles
green synthesis by silver nano particles
 
Stomatal Physiology.pptx
Stomatal Physiology.pptxStomatal Physiology.pptx
Stomatal Physiology.pptx
 
Ca - Carbonate Production By Heterotrophic Bacteria
Ca - Carbonate Production  By Heterotrophic Bacteria Ca - Carbonate Production  By Heterotrophic Bacteria
Ca - Carbonate Production By Heterotrophic Bacteria
 
Cyanobacteria as a Biofertilizer (BY- Ayushi).pptx
Cyanobacteria as a Biofertilizer (BY- Ayushi).pptxCyanobacteria as a Biofertilizer (BY- Ayushi).pptx
Cyanobacteria as a Biofertilizer (BY- Ayushi).pptx
 
Study on Toxic Impact of Sugar Factory Effluent on the Gill of the Fresh Wate...
Study on Toxic Impact of Sugar Factory Effluent on the Gill of the Fresh Wate...Study on Toxic Impact of Sugar Factory Effluent on the Gill of the Fresh Wate...
Study on Toxic Impact of Sugar Factory Effluent on the Gill of the Fresh Wate...
 
PhD-thesis_Matthias.Kellermann
PhD-thesis_Matthias.KellermannPhD-thesis_Matthias.Kellermann
PhD-thesis_Matthias.Kellermann
 
Mesocosms
MesocosmsMesocosms
Mesocosms
 
High Rate of Water Biodenitrification Using Anthracite as Hyphomicrobium Deni...
High Rate of Water Biodenitrification Using Anthracite as Hyphomicrobium Deni...High Rate of Water Biodenitrification Using Anthracite as Hyphomicrobium Deni...
High Rate of Water Biodenitrification Using Anthracite as Hyphomicrobium Deni...
 
Thermus aquaticus gen. n. and sp. n., a nonsporulating extreme thermophile
Thermus aquaticus gen. n. and sp. n., a nonsporulating extreme thermophileThermus aquaticus gen. n. and sp. n., a nonsporulating extreme thermophile
Thermus aquaticus gen. n. and sp. n., a nonsporulating extreme thermophile
 
Azotobacter in microbiology field of study
Azotobacter in microbiology field of studyAzotobacter in microbiology field of study
Azotobacter in microbiology field of study
 

poster_chien_final+jmk

  • 1. 3. Methods Preparation: The upper 3 cm of sediment from three sediment cores collected during October 2015 were used to enrich for Beggiatoa spp. The presence of Beggiatoa spp. filaments in the sediments was confirmed by microscopy. Homogenized sediment slurry and shredded paper were added to Hungate tubes. Enrichment conditions: • MIS groundwater was added to two different heights. • 8 tubes were loosely covered with a thin piece of aluminum foil, simulating aerobic conditions; 4 were induced to anaerobic conditions by being tightly capped; the remaining 4 had a hypodermic needle inserted in the middle of the rubber cap, permitting microaerobic growth (Fig. 2). • As an alternative potential terminal electron acceptor to O2 for SOB, 0.5 mL of 20 µM nitrate solution was added to 8 tubes from each treatment, to a final concentration of 1 - 5µM. • Half of the tubes were incubated in the dark without agitation at 8.6oC (in the following referred to as “cold”) which resembles the temperature of the sinkhole environment. The other half was incubated in the dark on an orbital shaker (100 RPM) at 20.0˚C (“room temperature”), to gently move the water column and simulate the groundwater flow environment. Observation: The tubes were checked weekly for a month and any growth of sulfide oxidizing bacterial filaments, namely Beggiatoa spp., was documented. 1. Introduction • The underwater Middle Island Sinkhole (MIS) is a photic, sulfidic, and low-oxygen modern system to understand microbial life on early Earth. • Members of Beggiatoa, a genus of filamentous sulfide- oxidizing bacteria (SOB), live in cyanobacterial-dominated microbial mats in MIS. Beggiatoa spp. can be found in either freshwater or marine environments, and are key autotrophs in light-limited environments such as deep-sea hydrothermal vents and seeps (Preisler et al., 2007). • The characteristics and activity of MIS Beggiatoa are of particular interest due to their unique interaction with the cyanobacteria. The white filaments cover the purple cyanobacterial layer during the night but migrate underneath the purple layer during the day (Biddanda et al., 2012). 2. Research goal To optimize growth conditions for Middle Island Sinkhole (MIS) sulfide oxidizing bacteria in order to isolate a pure culture of Beggiatoaspp. for future physiological and ecological studies. 7. Acknowledgements and References We thanks Matthew Medina and the NOAA Thunder Bay National Marine Sanctuary, including captains and scuba divers and especially Russ Green, John Bright, Wayne Lusardi, and Phil Hartmeyer. This work was supported by NSF grant EAR-1637066 to GJD. Biddanda, Bopaiah A., Stephen C. Nold, Gregory J. Dick, S. T. Kendall, J. H. Vail, S. A. Ruberg, and C. M. Green. 2012. "Rock, water, microbes: underwater sinkholes in Lake Huron are habitats for ancient microbial life." Nature Education Knowledge 3: 13. Kinsman-Costello, L. E., Sheik, C. S., Sheldon, N. D., Allen Burton, G., Costello, D. M., Marcus, D., ... & Dick, G. J. .2016. “Groundwater shapes sediment biogeochemistry and microbial diversity in a submerged Great Lake sinkhole.” Geobiology Preisler, André, Dirk De Beer, Anna Lichtschlag, Gaute Lavik, Antje Boetius, and Bo Barker Jørgensen. 2007. "Biological and chemical sulfide oxidation in a Beggiatoa inhabited marine sediment." The ISME journal 1, no. 4: 341-353. 4. Results and Analysis Understanding growth and activity of Beggiatoa spp. from a low-oxygen environment Hui Chien Tan1, Judith Klatt2, Sharon Grim3 and Gregory J. Dick1 1,2,3,4Earth and Environmental Sciences, University of Michigan, Ann Arbor, USA After a month of weekly observations, white filaments were absent in the anaerobic conditions but present in both microaerobic and aerobic conditions. Close inspection revealed disparity in the growth of white filaments between those in the cold environment and those in the room-temperature environment (Table 1). A B C D Figure 3: A. An absence of growth was noted in the anaerobic tubes. B. Muddy yellow mesh growing near the water level whereas white filament strands were found on the sediments (shown in red rings). C. Muddy yellow clump potentially representing elemental sulfur. D. White filaments growing around red tufts along with white ring formation near water surface. Figure 4: SOB under 40x magnification 5. Discussion and Conclusion We observed the best growth of SOB, likely Beggiatoa spp., in dark and microaerobic/aerobic conditions. Though some members of Beggiatoa are known to use nitrate in sulfide oxidation, we conclude that nitrate cannot be used efficiently as an alternative terminal electron acceptor for MIS Beggiatoa. We have four lines of support for MIS Beggiatoa using oxygen, not nitrate, for sulfide oxidation: 1. We observed migration of SOB filaments in aerobic and microaerobic treatments, towards the water surface where atmospheric exchange introduced oxygen. 2. There were insubstantial differences in SOB growth between +/- nitrate in the aerobic conditions. 3. We did not observe Beggiatoa growth in nitrate-amended, anaerobic tubes. 4. Low nitrate concentrations in the ambient groundwater (Kinsman- Costello et al., 2016) support our observation that MIS Beggiatoa are not cued to use nitrate in their metabolism. The formation of white rings near the water level provided insight on the migration pattern of the white mat at MIS. Previous field observations and laboratory experiments suggest that MIS Beggiatoa motility is linked to oxygen demand: the oxygenic photosynthetic cyanobacterial layer likely satisfies their oxygen requirements during the day, so the SOB reside within and below the cyanobacterial mat; whereas at night they are the top layer of the microbial mat, putatively to acquire oxygen from the low-oxygen water column. • Unlike the tufts of filaments in the tubes found in the cold environment, after two weeks the color of the tufts at room temperature changed into muddy yellow, putatively elemental sulfur, a chemical product of sulfide oxidation (Fig. 3 B). The formation of elemental sulfur was likely derived from competing non-filamentous SOB instead of Beggiatoa spp. because they do not store elemental sulfur extracellularly. • The cold growth tubes did not develop muddy yellow tufts; instead, two different colored filaments (dark red and white) grew together (Fig. 3 C and D). The absence of muddy yellow tufts in cold-incubated tubes might be related to the presence of the dark red filaments (likely cyanobacteria) and/or the incubation temperature. • The white rings were situated about 0.4 cm from the water level surface regardless of the height of the water column. Microscopy confirmed the presence of filamentous SOB with intracellular refractive elemental sulfur inclusions, likely Beggiatoa spp., within the white rings (Fig 4). We are attempting to isolate Beggiatoa spp. from our enrichments using gradient media that simulates the natural sediment biogeochemistry. For our first attempt, instead of the targeted SOB, another species of unknown white rod-shaped bacteria were growing in the gradient media (Fig. 5). The rod-shaped bacteria likely belong to the genus Thiobacillus. This lead us to our second attempt where the gradient media consists of autoclaved MIS sediments on a sulfidic agar plug (Fig. 6). Similar to the presented multivariate experiment, the tubes simulate aerobic, anaerobic, and microaerobic environments. Figure 5: Unknown white bacteria under 40x magnification Figure 6: 2nd attempt gradient media setup for culturing Beggiatoa spp. Figure 1: The observed migration pattern of Beggiatoa spp. (Adapted from Biddanda et al., 2012) Table 1: Observations of microbial growth in a multivariate environment WF = White Filaments (growing on sediments) WR = White ring (near water level) YR = Yellow ring (near water level) DRF = Dark Red Filaments A B C Figure 2: The pictures of tubes in different environmental simulations (in order): A. anaerobic, B. microaerobic, C. aerobic conditions. Condition Shaken Temp. Water column + Nitrate 1st Week 2nd Week 3rd Week 4th Week Aerobic Yes 20.0oC 2mL Yes Faint WR and WF Tuft in the water column and WF Muddy yellow clump in the water column and WF No YR and WF 10mL Yes No growth of WF Minimal WF White thin layer of WF White mesh with muddy yellow clump and WF No Growth of WF Muddy YR, white mesh layer and WF No 8.6oC 2mL Yes WF patches with DRF growing on top WR and WF patches with DRF growing on top No 10mL Yes No growth of WF Growth of DRF Thin WR and DRF No Anaerobic Yes 20.0oC 10mL Yes No growth of WF No No 8.6oC Yes No growth of WF but dark red filaments were observed No Micro- aerobic Yes 20.0oC 2mL Yes Faint WR and WF YR with white mesh and WF No No 8.6oC Yes WF patches with DRF on top Faint WR and WF tufts with DRF on topNo 6. Future Direction