experimental transcriptomics: marine microbial...

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C . M O R E C o n n e c t i o n s Partnerships and Leveraged Funding CMORE-EdVentures European Community 7th Framework Programme Presenters Laure-Anne Ventouras Grad Student MIT Mar Nieto Cid Post Doc WHOI / IIM Kathleen Munson Grad Student MIT/WHOI Additional Authors Erin Bertrand Mak Saito Cruises and Time Series: CMORE Photoperiod Cruise, Costa Rica Upwelling Dome Cruise. Dan Repeta Senior Scientist WHOI Ed DeLong Professor MIT Experimental Transcriptomics: Marine Microbial Community Response to Additions of Iron-Bound Organic Ligands Iron is a limiting nutrient in various open-ocean habitats, including the Equatorial Pacific [1], Subarctic Pacific [2], and the Southern Ocean [3], as well as in coastal sys Iron is a limiting nutrient in various open-ocean habitats, including the Equatorial Pacific [1], Subarctic Pacific [2], and the Southern Ocean [3], as well as in coastal sys- tems of California [4] and Peru [5]. As a co-factor of key enzymes, for example those controlling nitrogen fixation and photosynthesis, iron availability regulates key bio tems of California [4] and Peru [5]. As a co-factor of key enzymes, for example those controlling nitrogen fixation and photosynthesis, iron availability regulates key bio- chemical reactions that drive the carbon, nitrogen, and phosphorous biogeochemical cycles. Over 99% of total iron in seawater is complexed with organic ligands of chemical reactions that drive the carbon, nitrogen, and phosphorous biogeochemical cycles. Over 99% of total iron in seawater is complexed with organic ligands of unknown origin [6,7] Previous studies have suggested that these organic ligands are of biological origin and may be marine siderophores similar to those identified in unknown origin [6,7] Previous studies have suggested that these organic ligands are of biological origin and may be marine siderophores similar to those identified in terrestrial ecosystems [ terrestrial ecosystems [6,7] 6,7]. . To test the hypothesis that complexation with organic ligands may increase iron’s accessibility to the marine microbial community, an incubation experiment was per To test the hypothesis that complexation with organic ligands may increase iron’s accessibility to the marine microbial community, an incubation experiment was per- formed aboard the formed aboard the R/V Kilo Moana R/V Kilo Moana at Hawai’i Ocean Time Series Station ALOHA in September 2009. Organic ligands complexed to iron previously collected from the at Hawai’i Ocean Time Series Station ALOHA in September 2009. Organic ligands complexed to iron previously collected from the Equatorial Pacific were used in the following incubations, set up under trace metal clean conditions: 1). surface-seawater, 2). surface-seawater + Fe(III), 3). surface Equatorial Pacific were used in the following incubations, set up under trace metal clean conditions: 1). surface-seawater, 2). surface-seawater + Fe(III), 3). surface- seawater + XAD-extracted organic ligands, 4). surface-seawater + Fe(III) + XAD-extracted organic ligands. Samples were taken at various time points until the experi seawater + XAD-extracted organic ligands, 4). surface-seawater + Fe(III) + XAD-extracted organic ligands. Samples were taken at various time points until the experi- ment was ended after 36 hours of incubation. Preliminary results show that treatments 3 and 4 have an effect on the microbial community composition. Experimental ment was ended after 36 hours of incubation. Preliminary results show that treatments 3 and 4 have an effect on the microbial community composition. Experimental transcriptomics will be used to further analyze the response at the gene expression level of the whole microbial community. transcriptomics will be used to further analyze the response at the gene expression level of the whole microbial community. This experiment conceived largely independently by grad students and postdocs, partly funded by a CMORE EdVentures grant shows the extraordinary opportunities This experiment conceived largely independently by grad students and postdocs, partly funded by a CMORE EdVentures grant shows the extraordinary opportunities afforded by CMORE to promote collaboration across institutions, between laboratories focused on different research fields as well as to offer specialized education afforded by CMORE to promote collaboration across institutions, between laboratories focused on different research fields as well as to offer specialized education and training to postdocs and students, for example in trace-metal clean techniques. and training to postdocs and students, for example in trace-metal clean techniques. Abstract Preliminary Results Conclusions and Future Directions Travel and supplies were funded by a CMORE EdVentures grant and a European Community's Seventh Framework Programme grant. Additional funding by the Gordon and Betty Moore Foundation. We also would like to thank Dave Karl for providing us with the opportunity to join the Photoperiod Cruise in September 2009, as well as scientists, techni- cians and crew on the R/V Kilo Moana, for assistance to complete the experiment on board. Special Thanks to: Approach - Surface seawater in the Costa Rica Upwelling Dome in July 2005. - ~1,000L pumped through XAD-16 hy- drophobic column - Organic com- pounds, including those bound to iron. 1. Ligand Collection - Ligands extracted from XAD-16 in methanol - Concentration by roto- vaporization - Final concentration: Fe : 2nM Ligand: 93nM 2. Amendments 3. Trace Metal Clean Bubble - Positive-pressure trace-metal clean bubble - Site of sampling and amendments 4. On-deck incubation - On-deck flow- through incubator with 8L bottles - 40% incident light, 25ºC - 36 hours incu- bation Surface Seawater Surface Seawater + Fe Surface Seawater + XAD ligands Surface Seawater + Fe + XAD ligands Summary of Experimental Design 2. T36h T36h T12h T12h T3h T3h T0h T0h Tsw Tsw DNA DNA RNA RNA Total Fe Total Fe DFe + PFe DFe + PFe FCM FCM Ligand Ligand X X X X X X X X X X X X X X X X X Time points: Time points: Sample type: Sample type: DNA and RNA of the microbial community fraction (0.2um-1.6um) DNA and RNA of the microbial community fraction (0.2um-1.6um) DFe: dissolved iron (< 0.2um) DFe: dissolved iron (< 0.2um) PFe: particulate iron (>0.2um) PFe: particulate iron (>0.2um) FCM: Flow cytometry FCM: Flow cytometry 3. Treatments 4. 1. • Treatments 3 (+ ligand) and 4 (+ ligand + Fe) stimulate microbial cell division (Figure 1 b) Prochlorococcus cell numbers do not increase under any treatment (Figure 1 a) • Treatments 3 (+ ligand) and 4 ( + ligand +Fe) enhance Prochlorococcus cell size and chlorophylly fluorescence (Figure 2). • Treatments 3 and 4 differentially affect the Prochlorococcus population (Figure 2). • Organic ligand amendments have an effect on the bulk microbial community composition and more specifically on Prochlorococcus physiology. • Increase in Sybr stained cell-counts under treatments 3 and 4 (Figure 1) may be due to greater accessibility to iron or to the added organic matter. This will be further investigated in the transcriptomics analysis (Figure 3). • Gene expression patterns may reveal specific genes and pathways associ- ated with iron transport and utilization. • PFe, DFe, and Total Fe samples have been acidified and will be analyzed on an Inductively-Coupled Plasma Mass Spectrometer. • The CMORE 2010 cruise across the Equatorial Pacific will present a unique opportunity to use the skills learned and repeat this experiment in a truly iron- limited environment, using further characterized fractions of the organic li- gands. 1. Sampling from incubation experiment 2. Collection of microbial cell fraction (0.2um - 1.6 um) 3. Extraction of community DNA and RNA 4. Subtraction of rRNA from community RNA, amplification of community RNA, synthesis of cDNA 5. Pyroseqencing 6. Meta-transcriptomics analysis Surface Seawater Surface Seawater + Fe Surface Seawater + XAD ligands Surface Seawater + Fe + XAD ligands community RNA community DNA FLX Reads FLX Reads gene expression profile community composition Figure 3: Sample preparation pipeline for transcriptomic analysis. References: Gordon and Betty Moore Foundation 35 40 Prochlorococcus Time (hours) Counts/mL 0 5.0E+04 1.0E+05 1.5E+05 2.0E+05 2.5E+05 3.0E+05 3.5E+05 4.0E+05 4.5E+05 0 5 10 15 20 25 30 Control w/ Fe w/ Ligand w/ Ligand + Fe Diel Control Time (hours) 0 2.0E+05 4.0E+05 6.0E+05 8.0E+05 1.0E+06 1.2E+06 0 5 10 15 20 25 30 35 40 Sybr Stained Cells Figure 1: Changes in cell numbers of a. Prochloroccocus and b. Sybr stained cells (DNA- containing cells) across treatments and time points. Sybr stained cells were subtracted for Pro- chlorococcus counts. Diel control is an additional non-amended bottle for which only RNA and flow-cytometry samples were collected. a. b. Prochlorococcus Fluorescence 0 0.2 0.4 0.6 0.8 1 1.2 0 5 10 15 20 25 30 35 40 Time (hours) Prochlorococcus Fluorescence Prochlorococcus FSC 0 0.2 0.4 0.6 0.8 1 1.2 0 5 10 15 20 25 30 35 40 Time (hours) Prochlorococcus FSC a. b. [1] Martin, J.H., Coale, K.H., Johnson, K.S., Fitzwater, S.E., Gordon, R.M., Tanner, S.J., Hunter, C.N., Elrod, V.A., et al. 1994, "Testing the iron hypothesis in ecosystems of the equa- torial Pacific Ocean", Nature, vol. 371, pp. 123-129. [2] Tsuda, A., Takeda, S., Saito, H., Nishioka, J., Nojiri, Y., et al. 2003, "A mesoscale iron enrichment in the western Subarctic Pacific induces a large centric diatom bloom", Sci- ence, vol. 300, pp. 958-961. [3] Behrenfeld, M.J. & Kolber, Z.S. 1999, "Widespread iron limitation of phytoplankton in the South Pacific Ocean ", Science, vol. 283, no. 5403, pp. 840-843. [4] Hutchins, D.A., DiTullio, G.R., Zhang, Y. & Bruland, K.W. 1998, "An iron limitation mosaic in the California upwelling regime", Limnology and Oceanography, vol. 43, pp. 1037-1054. [5] Hutchins, D.A., Hare, C.E., Weaver, R.S., Zhang, Y., Firme, G.F., DiTullio, G.R., Alm, M.B., et al. 2002, "Phytoplankton iron limitation in the Humboldt Current and Peru upwell- ing", Limnology and Oceanography, vol. 47, no. 4, pp. 997-1011. [6] Rue, E.L. & Bruland, K.W. 1997, "The role of organic complexation on ambient iron chemistry in the equatorial Pacific Ocean and the response of a mesoscale iron addi- tion experiment", Limnology and Oceanography, vol. 42, pp. 901-910. [7] Rue, E.L. & Bruland, K.W. 1995, "Complexation of iron(III) by natural organic ligands in the Central North Pacific as determined by a new competitive ligand equilibration/adsorptive cathodic stripping voltammetric method", Marine Chemistry, vol. 50, pp. 117-138. Figure 2: Physiological changes of Prochlorococcus cells across treatments and time points. Fluorescence is a proxy for chlorophyll-intensity. FSC (forward scatter) is a proxy for size. Both fluorescence and FSC represent average values for the Prochlorococcus population, which were normalized to fluorescence and FSC of standard beads. Control w/ Fe w/ Ligand w/ Ligand + Fe Diel Control

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Page 1: Experimental Transcriptomics: Marine Microbial …cmore.soest.hawaii.edu/downloads/ED13_ventouras_poster.pdfing", Limnology and Oceanography, vol. 47, no. 4, pp. 997-1011. [6] Rue,

C. MORE Connections

Partnerships andLeveragedFunding

CMORE-EdVentures

European Community 7thFramework Programme

Presenters

Laure-Anne VentourasGrad Student

MIT

Mar Nieto CidPost Doc

WHOI / IIM

Kathleen MunsonGrad Student

MIT/WHOI

AdditionalAuthors

Erin BertrandMak Saito

Cruises and Time Series: CMORE Photoperiod Cruise, Costa Rica Upwelling Dome Cruise.

Dan RepetaSenior Scientist

WHOI

Ed DeLongProfessor

MIT

Experimental Transcriptomics: Marine Microbial Community Response to Additions of Iron-Bound Organic Ligands

Iron is a limiting nutrient in various open-ocean habitats, including the Equatorial Pacific [1], Subarctic Pacific [2], and the Southern Ocean [3], as well as in coastal sysIron is a limiting nutrient in various open-ocean habitats, including the Equatorial Pacific [1], Subarctic Pacific [2], and the Southern Ocean [3], as well as in coastal sys--tems of California [4] and Peru [5]. As a co-factor of key enzymes, for example those controlling nitrogen fixation and photosynthesis, iron availability regulates key biotems of California [4] and Peru [5]. As a co-factor of key enzymes, for example those controlling nitrogen fixation and photosynthesis, iron availability regulates key bio--chemical reactions that drive the carbon, nitrogen, and phosphorous biogeochemical cycles. Over 99% of total iron in seawater is complexed with organic ligands of chemical reactions that drive the carbon, nitrogen, and phosphorous biogeochemical cycles. Over 99% of total iron in seawater is complexed with organic ligands of unknown origin [6,7] Previous studies have suggested that these organic ligands are of biological origin and may be marine siderophores similar to those identified in unknown origin [6,7] Previous studies have suggested that these organic ligands are of biological origin and may be marine siderophores similar to those identified in terrestrial ecosystems [terrestrial ecosystems [6,7]6,7]. .

To test the hypothesis that complexation with organic ligands may increase iron’s accessibility to the marine microbial community, an incubation experiment was perTo test the hypothesis that complexation with organic ligands may increase iron’s accessibility to the marine microbial community, an incubation experiment was per--formed aboard the formed aboard the R/V Kilo MoanaR/V Kilo Moana at Hawai’i Ocean Time Series Station ALOHA in September 2009. Organic ligands complexed to iron previously collected from the at Hawai’i Ocean Time Series Station ALOHA in September 2009. Organic ligands complexed to iron previously collected from the Equatorial Pacific were used in the following incubations, set up under trace metal clean conditions: 1). surface-seawater, 2). surface-seawater + Fe(III), 3). surfaceEquatorial Pacific were used in the following incubations, set up under trace metal clean conditions: 1). surface-seawater, 2). surface-seawater + Fe(III), 3). surface--seawater + XAD-extracted organic ligands, 4). surface-seawater + Fe(III) + XAD-extracted organic ligands. Samples were taken at various time points until the experiseawater + XAD-extracted organic ligands, 4). surface-seawater + Fe(III) + XAD-extracted organic ligands. Samples were taken at various time points until the experi--ment was ended after 36 hours of incubation. Preliminary results show that treatments 3 and 4 have an effect on the microbial community composition. Experimental ment was ended after 36 hours of incubation. Preliminary results show that treatments 3 and 4 have an effect on the microbial community composition. Experimental transcriptomics will be used to further analyze the response at the gene expression level of the whole microbial community. transcriptomics will be used to further analyze the response at the gene expression level of the whole microbial community.

This experiment conceived largely independently by grad students and postdocs, partly funded by a CMORE EdVentures grant shows the extraordinary opportunities This experiment conceived largely independently by grad students and postdocs, partly funded by a CMORE EdVentures grant shows the extraordinary opportunities afforded by CMORE to promote collaboration across institutions, between laboratories focused on different research fields as well as to offer specialized education afforded by CMORE to promote collaboration across institutions, between laboratories focused on different research fields as well as to offer specialized education and training to postdocs and students, for example in trace-metal clean techniques. and training to postdocs and students, for example in trace-metal clean techniques.

Abstract

Preliminary Results Conclusions and Future Directions

Travel and supplies were funded by a CMORE EdVentures grant and a European Community's Seventh Framework Programme grant. Additional funding by the Gordon and Betty Moore Foundation. We also would like to thank Dave Karl for providing us with the opportunity to join the Photoperiod Cruise in September 2009, as well as scientists, techni-cians and crew on the R/V Kilo Moana, for assistance to complete the experiment on board.

Special Thanks to:

Approach

- Surface seawater in the Costa Rica Upwelling Dome in July 2005. - ~1,000L pumped through XAD-16 hy-drophobic column- Organic com-pounds, including those bound to iron.

1. Ligand Collection

- Ligands extracted from XAD-16 in methanol- Concentration by roto-vaporization- Final concentration: Fe : 2nM Ligand: 93nM

2. Amendments

3. Trace Metal Clean Bubble

- Positive-pressure trace-metal clean bubble - Site of sampling and amendments

4. On-deck incubation

- On-deck flow-through incubator with 8L bottles- 40% incident light, 25ºC- 36 hours incu-bation

SurfaceSeawater

SurfaceSeawater + Fe

SurfaceSeawater + XAD ligands

SurfaceSeawater + Fe + XAD ligands

Summary of Experimental Design

2.

T36hT36hT12hT12hT3hT3hT0hT0hTswTsw

DNADNARNARNATotal FeTotal FeDFe + PFeDFe + PFeFCMFCMLigandLigand

XX

XX XX XX XX XX

XX XX XXXXXX

XX XX XXXX

XXXX

Time points:Time points:

Sample type:Sample type:

DNA and RNA of the microbial community fraction (0.2um-1.6um) DNA and RNA of the microbial community fraction (0.2um-1.6um) DFe: dissolved iron (< 0.2um)DFe: dissolved iron (< 0.2um)PFe: particulate iron (>0.2um)PFe: particulate iron (>0.2um)FCM: Flow cytometryFCM: Flow cytometry

3. Treatments

4.

1.

• Treatments 3 (+ ligand) and 4 (+ ligand + Fe) stimulate microbial cell division (Figure 1 b)

• Prochlorococcus cell numbers do not increase under any treatment (Figure 1 a)

• Treatments 3 (+ ligand) and 4 ( + ligand +Fe) enhance Prochlorococcus cell size and chlorophylly fluorescence (Figure 2).

• Treatments 3 and 4 differentially affect the Prochlorococcus population (Figure 2).

• Organic ligand amendments have an effect on the bulk microbial community composition and more specifically on Prochlorococcus physiology.

• Increase in Sybr stained cell-counts under treatments 3 and 4 (Figure 1) may be due to greater accessibility to iron or to the added organic matter. This will be further investigated in the transcriptomics analysis (Figure 3).

• Gene expression patterns may reveal specific genes and pathways associ-ated with iron transport and utilization.

• PFe, DFe, and Total Fe samples have been acidified and will be analyzed on an Inductively-Coupled Plasma Mass Spectrometer.

• The CMORE 2010 cruise across the Equatorial Pacific will present a unique opportunity to use the skills learned and repeat this experiment in a truly iron-limited environment, using further characterized fractions of the organic li-gands.

1. Sampling from incubation experiment

2. Collection of microbial cell fraction (0.2um - 1.6 um)

3. Extraction of community DNA and RNA

4. Subtraction of rRNA from community RNA, amplification of community RNA, synthesis of cDNA

5. Pyroseqencing

6. Meta-transcriptomics analysis

SurfaceSeawater

SurfaceSeawater + Fe

SurfaceSeawater + XAD ligands

SurfaceSeawater + Fe + XAD ligands

community RNA community DNA

FLX Reads FLX Reads

gene expression profile

community composition

Figure 3: Sample preparation pipeline for transcriptomic analysis.

References:

Gordon and Betty Moore Foundation

35 40

Prochlorococcus

Time (hours)

Co

un

ts/m

L

0

5.0E+04

1.0E+05

1.5E+05

2.0E+05

2.5E+05

3.0E+05

3.5E+05

4.0E+05

4.5E+05

0 5 10 15 20 25 30

Counts/mL

Controlw/ Few/ Ligandw/ Ligand + FeDiel Control

Time (hours)

counts/mL

0

2.0E+05

4.0E+05

6.0E+05

8.0E+05

1.0E+06

1.2E+06

0 5 10 15 20 25 30 35 40

Sybr Stained Cells

Figure 1: Changes in cell numbers of a. Prochloroccocus and b. Sybr stained cells (DNA-containing cells) across treatments and time points. Sybr stained cells were subtracted for Pro-chlorococcus counts. Diel control is an additional non-amended bottle for which only RNA and flow-cytometry samples were collected.

a. b.

Prochlorococcus Fluorescence

0

0.2

0.4

0.6

0.8

1

1.2

0 5 10 15 20 25 30 35 40

Time (hours)

Prochlorococcus Fluorescence Relative to

Beads Fluorescence

Pro

chlo

roco

ccu

s F

luo

resc

ence

Prochlorococcus FSC

0

0.2

0.4

0.6

0.8

1

1.2

0 5 10 15 20 25 30 35 40

Time (hours)

FSC Beads

Pro

chlo

roco

ccu

s F

SC

a. b.

[1] Martin, J.H., Coale, K.H., Johnson, K.S., Fitzwater, S.E., Gordon, R.M., Tanner, S.J., Hunter, C.N., Elrod, V.A., et al. 1994, "Testing the iron hypothesis in ecosystems of the equa-torial Pacific Ocean", Nature, vol. 371, pp. 123-129. [2] Tsuda, A., Takeda, S., Saito, H., Nishioka, J., Nojiri, Y., et al. 2003, "A mesoscale iron enrichment in the western Subarctic Pacific induces a large centric diatom bloom", Sci-ence, vol. 300, pp. 958-961. [3] Behrenfeld, M.J. & Kolber, Z.S. 1999, "Widespread iron limitation of phytoplankton in the South Pacific Ocean ", Science, vol. 283, no. 5403, pp. 840-843.[4] Hutchins, D.A., DiTullio, G.R., Zhang, Y. & Bruland, K.W. 1998, "An iron limitation mosaic in the California upwelling regime", Limnology and Oceanography, vol. 43, pp. 1037-1054.[5] Hutchins, D.A., Hare, C.E., Weaver, R.S., Zhang, Y., Firme, G.F., DiTullio, G.R., Alm, M.B., et al. 2002, "Phytoplankton iron limitation in the Humboldt Current and Peru upwell-ing", Limnology and Oceanography, vol. 47, no. 4, pp. 997-1011. [6] Rue, E.L. & Bruland, K.W. 1997, "The role of organic complexation on ambient iron chemistry in the equatorial Pacific Ocean and the response of a mesoscale iron addi-tion experiment", Limnology and Oceanography, vol. 42, pp. 901-910.[7] Rue, E.L. & Bruland, K.W. 1995, "Complexation of iron(III) by natural organic ligands in the Central North Pacific as determined by a new competitive ligand equilibration/adsorptive cathodic stripping voltammetric method", Marine Chemistry, vol. 50, pp. 117-138.

Figure 2: Physiological changes of Prochlorococcus cells across treatments and time points. Fluorescence is a proxy for chlorophyll-intensity. FSC (forward scatter) is a proxy for size. Both fluorescence and FSC represent average values for the Prochlorococcus population, which were normalized to fluorescence and FSC of standard beads.

Controlw/ Few/ Ligandw/ Ligand + FeDiel Control