Headwaters are critical reservoirs of microbial diversity for fluvial networks
Katharina Besemer
Gabriel Singer
Christopher Quince
Enrico Bertuzzo
William Sloan
Tom J. Battin
0
School of Engineering, University of Glasgow
,
Glasgow G12 8QQ
,
UK
1
WasserCluster Lunz GmbH
,
Dr Carl Kupelwieser Promenade 5, 3293 Lunz am See
,
Austria
2
Department of Limnology and Oceanography, University of Vienna
,
Althanstrasse 14, 1090 Vienna
,
Austria
3
Laboratory of Ecohydrology, School of Architecture, Civil and Environmental Engineering, Ecole Polytechnique Fe de rale Lausanne
,
1015 Lausanne
,
Switzerland
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Cite this article: Besemer K, Singer G, Quince
C, Bertuzzo E, Sloan W, Battin TJ. 2013
Headwaters are critical reservoirs of microbial
diversity for fluvial networks. Proc R Soc B 280:
20131760.
http://dx.doi.org/10.1098/rspb.2013.1760
Subject Areas:
ecology, microbiology, environmental science
Authors for correspondence:
Katharina Besemer
e-mail:
Tom J. Battin
e-mail:
Electronic supplementary material is available
at http://dx.doi.org/10.1098/rspb.2013.1760 or
via http://rspb.royalsocietypublishing.org.
Katharina Besemer1,2, Gabriel Singer1,2, Christopher Quince3, Enrico Bertuzzo4,
William Sloan3 and Tom J. Battin1,2
1. Introduction
& 2013 The Authors. Published by the Royal Society under the terms of the Creative Commons Attribution
License http://creativecommons.org/licenses/by/3.0/, which permits unrestricted use, provided the original
author and source are credited.
high beta diversity compared with mid-sized steams [8], an
observation that is supported by experimental work with
protozoan metacommunities [11]. These patterns may be
attributable to large environmental variation among
headwaters [12], their spatial isolation limiting dispersal [11] and
their high abundance within fluvial networks [13,14].
Furthermore, stream confluences, as conspicuous nodes in
the fluvial network, have been postulated to augment
biodiversity of a network by way of accumulating species from multiple
catchments and, thus, increasing the size of the metacommunity
from which local communities assemble [5,11,12]. As posited by
the network dynamics hypothesis, strong gradients of channel
geomorphology across confluences may also increase habitat
heterogeneity and community variation, which would have a
knock-on effect on network scale biodiversity [15]. However,
empirical observations supporting these conjectures are
sparse. Field studies have revealed elevated fish diversity
around confluences [16,17] and, similarly, laboratory work on
protozoan metacommunities evoked that dispersal increases
diversity in experimental confluences characterized by higher
connectivity [11].
In streams and rivers, microbial life is dominated by
benthic biofilms, which control key ecosystem processes [10].
The biodiversity of these biofilms results from the interplay
of local environmental conditions and the dispersal dynamics
of microorganisms from the source community suspended in
the streamwater [18]. Microorganisms are primarily passive
dispersers [19]; the directionality of the water flow generating
asymmetrical dispersal, together with the dendritic network
structure, are therefore likely to influence microbial diversity
patterns [20]. Understanding microbial biodiversity patterns
at the scale of entire fluvial networks is of paramount
importance, especially since headwaters are increasingly under
threat by burial, mountain-top mining and inter-basin water
transfer [21,22].
In this study, we investigated patterns of microbial alpha
and beta diversity in benthic biofilms throughout a fluvial
network. We leaned on the concept of metacommunity (i.e. a set
of local communities linked by dispersal) ecology [2] to guide
our understanding of microbial diversity. Specifically, we
predicted higher alpha diversity downstream than upstream of
confluences because of increasing metacommunity size [23].
Furthermore, based on the converging structure of fluvial
networks [7], we hypothesized that microbial alpha diversity
increases from headwaters downstream, a pattern that may be
amplified by significant downstream dispersal of small
organisms with water flow [11]. We also predicted that microbial
beta diversity decreases from headwaters downstream because
of dispersal limitations [11] and pronounced habitat variation
among headwaters [12].
2. Material and methods
(a) Study area and field survey
We sampled benthic biofilms from 114 streams within a pre-alpine
catchment (River Ybbs, Austria; 254 km2; 1893532 metres above
sea level (m.a.s.l.); figure 1). Catchment geology is dominated by
dolomite (82%) and karst; forests (82%) and alpine meadows
(11%), characterized land use, bare rock, agricultural areas and
settlements constitute minor parts of the catchment (7% in total).
Streams were sampled during a one-week period in winter after
prolonged baseflow. This was to ensure rather stable and
homogeneous hydrological conditions throughout the fluvial
network and to sample mature biofilms with reduced successional
dynamics [24]. Discharge ranged from less than 1 l s21 in the
smallest headwaters to 2282 l s21 in the fifth-order stream during the
survey. To assess the relevance of confluences for biodiversity
patterns, we primarily sampled tributary pairs upstream of their
confluence and the recipient streams downstream of their
confluence (figure 1). Recipient streams were sampled 1020 times the
channel width or at least three riffle-pool sequences downstream
of the confluence [25] to ensure complete mixing of the streamwater,
while retaining the characteristics of the confluence environment
[15]. Mixing of streamwater was confirmed by measuring electrical
conductivity. Sampling was primarily designed to cover important
confluences, while equally representing all orders and sizes of
streams. A number of additional samples were taken at the inflow
and outflow of lakes to complete the picture of the network.
Stream channel depth, width, slope, velocity and discharge
were measured in the field following standard procedures. The
dimensionless Froude number was calculated as an integrative
descriptor of streambed hydraulics [14]. A digital elevation model,
rigorously ground-truthed, served to compute network metrics,
hydrologic distances between sampling sites, the size of
subcatchments and land use (see the electronic supplementary material,
methods). Streamwater was analysed for NO3, NH4 and PO4
concentrations and dissolved organic matter (DOM) was
characterized using fluorescence and spectrophotometric techniques
(electronic supplementary material, methods). From each site,
612 stones (14 cm in diameter) (...truncated)