Historical ecology of riverine fish in Europe
Aquat Sci (2015) 77:315–324
DOI 10.1007/s00027-015-0400-0
Aquatic Sciences
EDITORIAL
Historical ecology of riverine fish in Europe
Gertrud Haidvogl • Richard Hoffmann •
Didier Pont • Mathias Jungwirth • Verena Winiwarter
Received: 19 June 2015 / Accepted: 27 June 2015 / Published online: 7 July 2015
The Author(s) 2015. This article is published with open access at Springerlink.com
Abstract The temporal dynamic of riverine ecosystems
and their fish communities and populations has been
addressed in ecological theory and management for several
decades. A growing number of case studies on the historic
development especially of European and North American
rivers have been published. Nonetheless, a theoretical
debate about the contributions and limits of historical
approaches and interdisciplinary co-operation is lacking.
This article presents a brief overview of the role of history
in river and fish ecology and suggests historical ecology as
a scientific field that can offer a framework for future
research. Based on case studies compiled in this special
issue on the ‘‘Historical ecology of riverine fish in Europe’’,
we draw conclusions on long-term changes of fish communities, on fisheries, aquatic ecosystem management and
past habitat alterations and the potential of archaeological
This article is part of the special issue ‘Historical ecology of riverine
fish in Europe’.
G. Haidvogl (&) M. Jungwirth
Institute of Hydrobiology and Aquatic Ecosystem Management,
University of Natural Resources and Life Sciences Vienna,
Max Emanuelstraße 17, 1180 Vienna, Austria
e-mail:
R. Hoffmann
Department of History, 2140 Vari Hall, York University,
4700 Keele St., Toronto, ON M3J 1P3, Canada
D. Pont
Irstea UR HBAN, 1 rue Pierre-Gilles de Gennes—CS 10030,
92761 Antony, France
V. Winiwarter
Faculty of Interdisciplinary Studies, Institute of Social Ecology,
Alpen-Adria-Universität Klagenfurt, Schottenfeldgasse 29,
1070 Vienna, Austria
remains and written sources to study them. We discuss how
modelling of historical fish data can help elucidate the
effects of climate change and human influences on rivers
and fish. Finally, we account for the necessity to consider
appropriate spatial and temporal scales. In conclusion we
call for future comparative studies on continental and
global scales and methodological development, which can
benefit especially from recent advances in marine historical
ecology. We suggest that future interdisciplinary studies of
ecologists, hydrologists, historians and archaeologists can
reveal the history of riverine ecosystems as socio-ecological systems, addressing both their natural dynamics and
human dimension. Such an endeavor can also support
developing management plans for habitat restoration and
conservation against the background of global change.
Keywords Historical ecology History of fish
European rivers Historical sources
Integrated river basin management
The temporal dimension and history in river and fish
ecology
The dynamic nature of ecosystems has been addressed for
several decades. Disturbance theory is often identified as an
important milestone of the debate. White and Pickett
(1985) defined disturbance as a ‘‘relatively discrete event in
time that disrupts ecosystem, community or population
structure and changes resources, substrate availability, or
the physical environment’’. Resh et al. (1988) applied the
idea of disturbance regimes in river ecology. In 1989, Ward
conceptualized lotic ecosystems as 4-dimensional (Ward
1989). He emphasized the role of temporal dynamics apart
from the three spatial dimensions, i.e. the longitudinal, the
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lateral and the vertical and pointed to the difficulties to
distinguish low-level anthropogenic perturbations from
normal variations resulting from long-term natural cycles
(Ward 1989; see also Hohensinner et al. 2011). Later,
concepts rooted in the idea of an ecological equilibrium
have been challenged, taking into account species dispersal
and metapopulation theory (Hanski 1999), the role of
spatial heterogeneity on ecological processes and the
importance of fluxes between ecosystems (Pickett and
Cadenasso 1995). Ecosystems are now seen as unstable,
open, hierarchical and scaled (O‘Neill 2001).
Without referring explicitly to the progress in ecological
theory, a growing number of case studies on the historical
development of riverine ecosystems have been published
since the end of the 1980s. For European river systems,
Petts et al. (1989) presented long-term changes of river
morphology and hydrology. They also accounted for biological studies with a focus on fish. Similar publications
followed for the Americas, even treating fish specifically
(see e.g. Rinne et al. 2005). On a general level, Downs and
Gregory (2004) identified six historical periods of river use
and according management practices. They distinguish
hydraulic civilizations, preindustrial societies, the period of
the industrial revolution, the late 19th to mid-20th century,
the second half of the 20th century and finally, the period
since the late 20th century, which accounts for integrated
river basin management, re-regulation of flow, mitigation,
enhancement and restoration techniques as well as hybrid
and bioengineered revetments. In terms of biodiversity
change, three periods are usually differentiated with reference in particular to the so-called ‘‘Columbian
exchange’’. Notwithstanding earlier species‘transfers on a
smaller scale, the ‘‘discovery’’ of the Americas by Europeans in 1492 is perceived as a turning point in the history
of ecosystems and their biota (see especially Crosby 1972,
1986). In the second half of the 19th century, the industrial
revolution with its improved means of transport triggered
large-scale and frequent exchange of species. Besides
deliberate introductions, for which the rainbow trout can be
cited as an example for some European freshwater systems,
this led also to the translocation of species to new habitats
where they were considered as non-native or even invasive
(di Castri 1989 as an early study).
In the 1990s, historical approaches gained importance in
ecosystem management. Restoration ecology was increasingly relying on historically based reference conditions and
‘‘historical ecology’’ has been adopted as a specific
approach to study past ecosystems and their development
(see e.g. Swetnam et al. 1999; Egan and Howell 2001).
Freshwater system management was no exception. When
the European Water Framework Directive (WFD, EC
2000) came into force, the idea of natural, i.e. anthropogenically undisturbed aquatic systems as a target of
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restoration even received legal status. Although the WFD is
not interested in historical conditions as such, it stimulated
related research, as it requires defining a high ecological
status, reflecting conditions in the absence of human
influence (e.g. Jungwirth et al. 2002). Recent studies in
European fish ecology thus often focus (...truncated)