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VOL. 77, 2011 BALTIC SEA BACTERIONEUSTON COMMUNITY STRUCTURE 3731<br />

radiation. In contrast, <strong>the</strong> total communities (as determ<strong>in</strong>ed by<br />

16S rRNA gene analysis) were not <strong>in</strong>fluenced by any of <strong>the</strong><br />

meteorological conditions <strong>in</strong>vestigated. Phylogenetically, active<br />

members of <strong>the</strong> bacterioneuston belonged to Cyanobacteria,<br />

Bacteroidetes, and <strong>the</strong> alpha, beta, and gamma subgroups of<br />

Proteobacteria. Their 16S rRNA sequences were related ma<strong>in</strong>ly<br />

to environmental clones from soils and different water columns,<br />

and thus, <strong>the</strong>y most likely did not form dist<strong>in</strong>ct bacterioneuston<br />

assemblages.<br />

Comparison of bacterioneuston and bacterioplankton community<br />

compositions. Oppos<strong>in</strong>g results have been reported<br />

regard<strong>in</strong>g <strong>the</strong> differences between SML and ULW bacterial<br />

communities. For <strong>in</strong>stance, 16S rRNA gene-based analyses<br />

showed bacterioneuston diversity patterns strongly dist<strong>in</strong>guishable<br />

from those of bacterioplankton when <strong>the</strong> SML was sampled<br />

with membrane filters (12, 16) but not when a screen<br />

sampler was used (1, 36). This discrepancy was caused partly by<br />

<strong>the</strong> different SML sampl<strong>in</strong>g techniques (2, 10), demonstrat<strong>in</strong>g<br />

<strong>the</strong> importance of sample collection. The most important considerations<br />

for obta<strong>in</strong><strong>in</strong>g high-quality SML samples are m<strong>in</strong>imal<br />

dilution with bulk water, a lack of bias due to sampler<br />

selectivity, collection of a large sample volume with<strong>in</strong> a reasonable<br />

sampl<strong>in</strong>g time, and easy handl<strong>in</strong>g of <strong>the</strong> samplers (17,<br />

24). The glass-plate sampl<strong>in</strong>g device used <strong>in</strong> our study was<br />

chosen because (i) its layer thickness is <strong>in</strong> <strong>the</strong> range of 50 m,<br />

as recommended <strong>in</strong> previous reports (10, 55), (ii) larger<br />

amounts of water could be sampled for fur<strong>the</strong>r analyses, and<br />

(iii) previous studies demonstrated that this method shows no<br />

selectivity <strong>in</strong> <strong>the</strong> analysis of bacterial community composition<br />

(48).<br />

Pairwise comparisons of bacterial community structures of<br />

<strong>the</strong> SML and ULW, as carried out <strong>in</strong> this and o<strong>the</strong>r studies,<br />

allow assessment of <strong>the</strong> extent of bacterioneuston and bacterioplankton<br />

differentiation. Whereas previous studies generally<br />

compared total bacterial communities, we sought to<br />

achieve a higher-resolution comparison by dist<strong>in</strong>guish<strong>in</strong>g between<br />

nonattached and particle-attached communities as well<br />

as between active and total communities. In our study it became<br />

obvious that <strong>the</strong> differences between <strong>the</strong> SML and ULW<br />

exhibited by particle-attached assemblages were much more<br />

pronounced than those for <strong>the</strong> nonattached assemblages, <strong>in</strong><br />

which <strong>the</strong> two compartments were highly similar. This is <strong>in</strong><br />

accordance with <strong>the</strong> notion that particulate material is generally<br />

<strong>in</strong>habited by specific bacterial assemblages that are dist<strong>in</strong>guishable<br />

from those of <strong>the</strong> surround<strong>in</strong>g bulk water and that<br />

differ depend<strong>in</strong>g on <strong>the</strong> particle type (47). These observations<br />

underl<strong>in</strong>e <strong>the</strong> importance of dist<strong>in</strong>guish<strong>in</strong>g different size fractions<br />

as well as active and total communities <strong>in</strong> order to obta<strong>in</strong><br />

more-profound comparisons of bacterioneuston and bacterioplankton<br />

diversity analyses.<br />

Influence of meteorological conditions. In general, differences<br />

between active bacterioneuston and bacterioplankton<br />

community compositions <strong>in</strong> both size fractions were highest<br />

dur<strong>in</strong>g low w<strong>in</strong>d speeds (Fig. 2), suggest<strong>in</strong>g a shift <strong>in</strong> <strong>the</strong> composition<br />

of active bacteria <strong>in</strong> <strong>the</strong> SML under calm conditions.<br />

In a previous study, a correlation between w<strong>in</strong>d speed history<br />

and chang<strong>in</strong>g SML properties was demonstrated (36). Also <strong>in</strong><br />

<strong>the</strong> present study, only w<strong>in</strong>d speed history, expressed as <strong>the</strong><br />

mean w<strong>in</strong>d speed 6 h prior to sampl<strong>in</strong>g and not <strong>the</strong> actual w<strong>in</strong>d<br />

speed dur<strong>in</strong>g sampl<strong>in</strong>g, was related to <strong>the</strong> differences between<br />

<strong>the</strong> bacterioneuston and bacterioplankton f<strong>in</strong>gerpr<strong>in</strong>ts. This<br />

probably reflected <strong>the</strong> fact that <strong>the</strong> reduction of turbulent<br />

surface mix<strong>in</strong>g <strong>in</strong>duced by low w<strong>in</strong>d speeds is time delayed. In<br />

<strong>the</strong> presence of less w<strong>in</strong>d-<strong>in</strong>duced surface mix<strong>in</strong>g, <strong>the</strong> sea surface<br />

calms. This may <strong>in</strong> turn promote <strong>the</strong> development of a<br />

dist<strong>in</strong>ct, active bacterioneuston community. The development<br />

of a dist<strong>in</strong>ct total-bacterioneuston community most likely requires<br />

more than 6hoflowturbulence <strong>in</strong> <strong>the</strong> SML. Similar<br />

suggestions have been made regard<strong>in</strong>g estuar<strong>in</strong>e bacterioneuston<br />

assemblages, s<strong>in</strong>ce <strong>the</strong>y are exposed to strong hydrodynamics<br />

(45), and might expla<strong>in</strong> previous observations of highly<br />

dist<strong>in</strong>ctive bacterioneuston assemblages after a few days <strong>in</strong><br />

mesocosm experiments and dur<strong>in</strong>g slick formation (13, 49). In<br />

addition, alp<strong>in</strong>e lakes, which are exposed to less w<strong>in</strong>d stress<br />

than mar<strong>in</strong>e systems, conta<strong>in</strong> unique archaeal assemblages <strong>in</strong><br />

<strong>the</strong> air-water <strong>in</strong>terface and ULW (6), and even specific neustonic<br />

bacteria, such as Nevskia ramosa, may live <strong>in</strong> limnic<br />

habitats (39).<br />

Compared to w<strong>in</strong>d speed history, global solar radiation and<br />

UV-A radiation had only m<strong>in</strong>or impacts on <strong>the</strong> differences<br />

between <strong>the</strong> active bacterioneuston and bacterioplankton communities,<br />

imply<strong>in</strong>g low structur<strong>in</strong>g effects on bacterioneuston<br />

assemblages <strong>in</strong> <strong>the</strong> present study. This has also been shown for<br />

<strong>the</strong> near-surface bacterioplankton composition of <strong>the</strong> North<br />

<strong>Sea</strong>, which was only slightly <strong>in</strong>fluenced by chang<strong>in</strong>g levels of<br />

UV radiation (52). However, <strong>in</strong> <strong>the</strong> active communities of <strong>the</strong><br />

nonattached size fraction exam<strong>in</strong>ed <strong>in</strong> <strong>the</strong> present study, <strong>the</strong><br />

strongest differences occurred <strong>in</strong> response to <strong>the</strong> highest radiation<br />

levels. This suggests that <strong>in</strong>creas<strong>in</strong>g exposure to UV<strong>in</strong>duced<br />

stress alters <strong>the</strong> community composition of nonattached,<br />

active bacterioneuston members, which aga<strong>in</strong> is<br />

favored dur<strong>in</strong>g low w<strong>in</strong>d conditions. In contrast, variability <strong>in</strong><br />

<strong>the</strong> particle-attached f<strong>in</strong>gerpr<strong>in</strong>ts was not related to chang<strong>in</strong>g<br />

levels of radiation, probably due to <strong>the</strong> shelter<strong>in</strong>g from UV<br />

exposure conferred by particle association (22, 53).<br />

Interest<strong>in</strong>gly, none of <strong>the</strong> meteorological conditions correlated<br />

with changes <strong>in</strong> <strong>the</strong> total bacterioneuston and bacterioplankton<br />

assemblages, at least based on our methodological<br />

approach. A previous study likewise detected no association<br />

between w<strong>in</strong>d speed and differences between total bacterioneuston<br />

and bacterioplankton communities <strong>in</strong> coastal Mediterranean<br />

waters (1), <strong>in</strong>dicat<strong>in</strong>g that <strong>the</strong> high spatial and temporal<br />

variability <strong>in</strong> <strong>the</strong> SML is also caused by o<strong>the</strong>r factors. The<br />

dynamic patterns of <strong>the</strong> similarities between <strong>the</strong> SML and<br />

ULW <strong>in</strong> <strong>the</strong> total, particle-attached communities were found<br />

to be related to TOC and TN accumulation <strong>in</strong> <strong>the</strong> SML (see<br />

Table S2 <strong>in</strong> <strong>the</strong> supplemental material). The SML is generally<br />

characterized by strong enrichment of organic and <strong>in</strong>organic<br />

substances, especially of <strong>the</strong> particulate fraction (25). Under<br />

very calm conditions, e.g., <strong>in</strong> visible surface films, <strong>the</strong> particulate<br />

fraction <strong>in</strong>creas<strong>in</strong>gly contributes to <strong>the</strong> total-organic-matter<br />

pool (49). Thus, <strong>the</strong> chang<strong>in</strong>g enrichment of particulate<br />

organic matter may account even better for <strong>the</strong> differences <strong>in</strong><br />

community composition that were already shown for bacterial<br />

abundances and productivity (49). Fur<strong>the</strong>r evidence of large<br />

differences between <strong>the</strong> community compositions of <strong>the</strong> SML<br />

and <strong>the</strong> ULW follow<strong>in</strong>g <strong>in</strong>creases <strong>in</strong> <strong>the</strong> amount of organic<br />

matter comes from mesocosm experiments, <strong>in</strong> which autotrophic<br />

production resulted <strong>in</strong> high concentrations of transparent<br />

exopolymeric particles <strong>in</strong> <strong>the</strong> SML (10, 11).

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