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K. Hardge, S. Neuhaus, S. Frickenhaus, E.S. Kilias, C. Wolf and K. Metfies

Assessment of eukaryotic communities in environmental samples:

A workflow comparison for next-generation sequencing data

References :

Kristin Hardge

.

Am Handelshafen 12 27570 Bremerhaven Telefon 0471 4831-2261 www.awi.de

kristin.hardge@awi.de

ECC 2014

5th Early Career Scientists Conference for Marine and Climate Research 2014

Protists are the base of food web and important primary producers in aquatic systems, such as the Arctic Ocean

1

. The composition of protist communities helps us to understand function and stability of aquatic ecosystems.

For analyzing the protist diversity, next-generation sequencing (e.g. 454 pyrosequencing) has replaced conventional methods (e.g. light microscopy). So far, there is no consensus about how to process the huge amount of sequencing data .

Sequence processing parameters have to be chosen individually according to the scope of project and taxonomic level.

A combination of molecular and conventional methods provides valuable insights into the real conditions in the field and allows a better comparability between diversity studies.

Water samples (T1, T3, T9) were collected during RV Polarstern cruise to the Fram Strait with a CTD-Rosette (conductivity, temperature and depth) from the respective chlorophyll maximum layer depth (15 – 35 m) in July 2010.

Greenland

Sea Norwegian Sea

Fram Strait T1 T3 T9

In order to estimate the protist composition in environmental samples as precisely as possible, this study:

(i) compares different sequence processing workflows and

(ii) combines conventional microscopy and next-generation sequencing.

DNA of protists was extracted from fractionated water samples and sequenced with 454 pyrosequencing.

DNA extraction from filter

Sequencing

Roche GS FLX-Sequencer Membrane filter

Cell size fractionation

A part of the clearly recognizable protist community (i.e.

diatoms, belong to kingdom Stramenopila) was identified and counted using an inverted light microscope (LM).

50 µm

Work- flow

Quality- check

De- noising

Cluster- ing

Sequence assignment

Q1 x - x

Similarity based with complete

reference database*

Q2 x x x

M1 x - x

M2 x x x

P1 x - x Tree based

with subset of

reference database*

P2 x - -

P3 - - -

Position of samples.

Base of map: http://www.ngdc.noaa.gov/mgg/bathymetry/arctic/

CTD-Rosette

Quality-check: Deletion of ambiguous bases, hybrid sequences and repeats of single bases, sequences were trimmed

Denoising: Sequencing-error correction

Clustering: Similar sequences are combined into operational taxonomic units (similarity threshold of 97%)

*Silva SSU Ref NR 111

How does sequence processing effect the composition of protists?

Are the results of microscopy and sequencing comparable?

A comparison of conventional and molecular methods

• Results of PhyloAssigner were comparable with microscopic observations.

• Some counted diatom genera were not detected via sequencing due to degraded cell content (e.g. Chaetoceros).

• Possible misidentification occurred due to similar morphological features.

• Rare species could not be detected with microscopy (only 50 ml analyzed).

P Microscopy gave useful information about the diversity and ecology of dominant diatoms in the water samples.

The effect of sequence processing

• No strong effect on kingdoms but on closer related organisms (genera).

• Default workflows of Qiime and Mothur reduced the diatom diversity (may be not appropriate for eukaryotic sequences).

• A phylogenetic placement of sequences is more reliable than a similarity based assignment (esp. for unknown species as found in the Arctic Ocean).

• Genetic similarity of > 97% is too low for determining real diatom diversity.

P Sequencing allowed a reproducible overview of protist kingdoms.

Next-generation sequencing of eukaryotic kingdoms and diatom genera

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Other Eukarya Stramenopila Rhizaria

Metazoa Haptophyta Fungi

Cryptophyta Chlorophyta Alveolata

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T1

Q1 Q2 M1 M2 P1 P2 P3 T3

T9

T1

Unidentified diatoms Other pennate diatoms Pleusorigma

Nitzschia Navicula

Fragilariopsis

Other centric diatoms Porosira

Thalassiosira Lauderia

Chaetoceros

Q1 Q2 M1 M2 P1 P2 P3 T3

T9

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T1 T3 T9

Relative sequence abundance of eukaryotic kingdoms (left) and diatom genera (right).

Workflows created with PhyloAssigner (P) resulted in a higher diatom diversity. Total number of raw protist sequences (P3): T1: 41750 seqs., T3: 25407 seqs., T9: 34466 seqs.

Relative abundance of diatom genera (same color code as used for sequen- cing of diatoms) and diatom cells per litre observed with microscope.

T1: 184080 Ind/L T3: 110380 Ind/L T9: 17040 Ind/L

Light microscopy of diatom genera

T1

Thalassiosira spp. Chaetoceros spp. Navicula sp. Fragilariopsis sp.

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T3

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T3

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T9

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T9

Observed were single large and healthy cells (e.g. Thalassiosira) but also chains of small, less healthy and broken cells (e.g. Chaetoceros). These cell conditions give information about succession of diatom bloom (i.e. Chaetoceros bloom prior Thalassiosira).

20 µm 20 µm

T1 T1

The compared workflows were created with open-source software Qiime2 (Q), Mothur3 (M) and PhyloAssigner4 (P) by using default parameters

Sequence processing Sample collection and preparation

1 Gosselin, M. et al. New measurements of phytoplankton and ice algal production in the Arctic Ocean. Deep Sea Res. Part II 44, 1623–1644 (1997).

2 Caporaso, G.J. et al. QIIME allows analysis of high-throughput community sequencing data. Nat. Methods 7, 335–336 (2010).

3 Schloss, P.D. et al. Introducing mothur: Open-source, platform-independent, community-supported software for describing and comparing microbial communities. Appl. Environ. Microbiol. 75, 7537–7541 (2009).

4 Vergin, K.L. et. al. High-resolution SAR11 ecotype dynamics at the Bermuda Atlantic Time-series Study site by phylogenetic placement of pyrosequences. ISME J. 7, 1322–1332 (2013).

This study was accomplished within the Young Investigator Group PLANKTOSENS, funded by the Initiative and Networking Fund of the Helmholtz Association. We thank the captain and crew of the RV Polarstern for their support during the cruise. We are grateful to A. Nicolaus and K. Oetjen for technical support in the laboratory.

Acknowledgements:

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