Integrative conservation of riparian zones

https://doi.org/10.1016/j.biocon.2016.10.035Get rights and content

Highlights

  • Current management is failing at effectively conserving riparian zones.

  • Conservation requires integration of technical, socio-economic and legal approaches.

  • Environmental education, long term monitoring and specific legislation are needed.

  • Economic activities in riparian zones should convey sustainable management.

  • Restoration needs clear, realistic, multiple-scaled and evaluable goals.

Abstract

Riparian zones are the interface between aquatic and terrestrial systems along inland watercourses. They have a disproportionate ecological role in the landscape considering their narrow extent, which makes them a good example of small natural features (sensu Hunter, 2017-inthisissue). Characteristically, riparian zones increase species richness in the landscape and provide key services to society, such as soil fertility, water purification, and recreation. Despite the recognized importance of riparian zones for ecological, economic and social reasons, and the vast amount of scientific literature exploring measures for their conservation, current management is still failing at enabling a proper ecological functioning of these areas. The best practices for conservation of riparian zones have mostly focused on manipulating biotic and physical components (e.g. renaturalizing flow regimes, improving channel mobility, and controlling invasions of exotic ecosystem engineer species). However, these strategies face important technical, socio-economic, and legal constraints that require a more integrative approach for effective conservation. In this paper we summarize the main problems affecting riparian zones and their current management challenges. Following Hunter et al. (2017-inthisissue), we review novel approaches to conservation of riparian zones, complementary to manipulating processes that reflect contemporary management and policy. These include (1) investing in environmental education for both local people and technical staff, (2) guaranteeing qualitative and long term inventories and monitoring, (3) establishing legislation and solutions to protect riparian zones, (4) framing economic activities in riparian zones under sustainable management, and (5) planning restoration of riparian zones at multiple and hierarchical spatio-temporal scales.

Introduction

Riparian zones are ecosystems created at the interface between terrestrial and freshwater habitats along flowing waters. They represent only a narrow portion of the landscape while contributing disproportionately to the biodiversity of the region as a whole (Sabo et al., 2005) and providing many ecosystem services (“Frodo effect”, Primack and Sher, 2016), mainly due to the dynamic “edge effect” of the aquatic/terrestrial transition zone following flooding pulses (Junk et al., 1989). Therefore, riparian zones are small natural features (SNFs) with an ecological role extending beyond their area (Hunter, 2017--inthisissue). The conservation of riparian zones, as for many other SNFs, is acutely threatened by human activities. Flow regulation by dams, diversions and other infrastructures to reduce flood risk, and the conversion of riparian zones by agriculture, forestry, industrial and urban development are responsible for the deterioration and loss of riparian ecosystems worldwide (Hughes and Rood, 2003, Nilsson and Berggren, 2000). Up to 90% of North American and European floodplains, for example, are considered ecologically dysfunctional following human occupation (Schillinga et al., 2015, Tockner and Stanford, 2002). In Europe, the combined effect of conversion to agriculture and regulation has resulted in the disappearance of up to 88% of floodplain forests (Hughes and Rood, 2003).

Unlike other SNFs such as temporary streams (Acuña et al., 2017--inthisissue) or large old trees (Lindenmayer, 2017--inthisissue), conservation of riparian ecosystems has been the object of much research. Many studies have focused on how to manipulate riparian ecosystems to enable their conservation or restoration (e.g. renaturalization of flow regimes (Poff et al., 1997, Rood et al., 2003); restitution of channel migration (Rohde et al., 2005, Jähnig et al., 2009); and control of species invasions (Richardson et al., 2007, Stromberg, 2001). However, conservation strategies purely based on manipulating ecological processes face important technical–ecological, socio-economic, and legal constraints. First, after decades of impact, some rivers may have lost their capacity to positively respond to conservation actions (Cooper and Andersen, 2012, Johnson et al., 2015). Secondly, society may prioritize extractive uses and particular ecosystem services such as flood prevention or recreation over key ecological functions like wildlife habitat or nutrient filtering (Gumiero et al., 2013, Rohde et al., 2005). Thirdly, legislation may subordinate environmental goals to other interests. In Europe, for example, there are a number of socio-economic reasons (such as “overriding public interest” or “no other significantly better option”) to be exempted from meeting the environmental objectives of the Water Framework Directive (European Commission, 2009). The conflict between different interests and directives usually leads to the adoption of uncoordinated measures in the management of riparian zones. For instance, in Italy, in order to save public money in flood risk prevention, private companies are allowed to remove vegetation from riparian zones for biomass production (WWF, 2016). However, this increases flood risk downstream and may generate dramatic effects on riparian wildlife (Anderson et al., 2006). Thus, conservation of riparian zones will not be possible if technical–ecological, socio-economic, and legal issues are not addressed holistically. Hunter et al. (2017--inthisissue) have proposed a matrix of key conservation activities (educate, inventory, protect, sustainably manage, restore, and create) that may include incidental, voluntary, incentive, or restrictive approaches relevant to the conservation of SNFs, which we can apply to riparian zones.

The main goal of this paper is to identify and discuss conservation measures for riparian zones complementary to manipulation of biotic and physical processes that reflect management and policy directions. To achieve this goal, we (i) briefly introduce riparian zones (Section 2) and their ecological, economic, and social importance (Section 3), (ii) describe the main human impacts on riparian zones (Section 4) and current management challenges (Section 5), and, following Hunter et al. (2017--inthisissue) (iii) review key measures for conserving riparian zones that will facilitate SNF conservation (Section 6).

Section snippets

What are riparian zones?

Riparian zones are the interface between terrestrial and aquatic ecosystems along inland watercourses (Naiman and Décamps, 1997). They encompass the space between the flowing water at low levels and the highest water mark where vegetation is influenced by floods, elevated water tables, and soil type. In the landscape, they function as a dendritic network of narrow-shaped corridors with flowing energy, matter and biodiversity (Gregory et al., 1991, Naiman and Décamps, 1997). Riparian zones are

Ecological, economic, and social importance of riparian zones

Riparian zones perform multiple ecological functions, including refuge for regional biodiversity, climate regulation, flood buffering, water and nutrient filtering, shading stream channels and high primary productivity (Naiman and Décamps, 1997, Palmer and Bennett, 2006). These ecological functions are directly related to key ecosystem services provided to society (Felipe-Lucia et al., 2014, Vidal-Abarca Gutiérrez and Suárez Alonso, 2013). Many of these functions have direct economic relevance,

Impacts on riparian zones

Riparian zones have faced profound anthropogenic modifications since the rise of civilization (Feld et al., 2011), which have been shown to affect trophic networks at every level (Mensing et al., 1998). Human activities have been centered along rivers and riparian zones because of their position in the landscape. Agriculture exploits the nutrient-rich substrates of wide floodplains, while rivers in canyons or open valleys are dammed to store water for agricultural, domestic, and/or industrial

Establishing reasonable goals for the effective conservation of riparian zones

Returning degraded riparian zones to pre-disturbance or low human impact conditions is rarely possible. Riparian zones are especially dynamic and evolving systems subjected to non-linear, often unpredictable trajectories and are in permanent change. Conservation of riparian zones must aim at establishing a state able to adapt to changing conditions (Dufour and Piégay, 2009, Hughes et al., 2005).

In order to define such a state representing desirable yet reasonable conservation goals, an accurate

Key measures to conserve riparian zones

In this section, we expand on some important aspects of conservation that have received less attention in the literature. These solutions are grouped in five key activities (education, inventory, protection, sustainable management, and restoration) that respond to one or more approaches: incidental (as a result of conserving the landscapes in which riparian zones are embedded), voluntary (often due to ethical concerns), incentive (due to financial inducements or other benefits), or restrictive

Conclusions

Riparian zones are threatened by continuous and increasing anthropogenic impacts since the rise of civilization. Among the main management challenges facing riparian zones we stress: (i) difficulties to establish reasonable conservation goals, (ii) a vast but non-specific and sometimes contradictory legislation, (iii) uncertainty about the response of riparian zones to climate change, biological invasions, and the long time-lags between the application of conservation measures and eventual

Acknowledgements

We are grateful for the invitation of Dr. Malcolm Hunter to participate in the symposium and write this paper. Drs. Vicenç Acuña, Aram Calhoun, Monique Poulin and two anonymous reviewers provided helpful comments to improve the manuscript. EG and MFL wrote the paper with contributions from the remaining authors, who are listed in alphabetical order. EG participation in the symposium was supported by a Marie Curie International Outgoing Fellowship within the 7th European Community Framework

References (133)

  • V. Acuña et al.

    Managing temporary waterways as unique rather than second-class ecosystems

    Biol. Conserv.

    (2017)
  • B.G. Anderson et al.

    An analysis of the influence of riparian vegetation on the propagation of flood waves

    Environ. Model. Softw.

    (2006)
  • A. Apan et al.

    Mapping and analysis of changes in the riparian landscape structure of the Lockyer Valley catchment, Queensland, Australia

    Landsc. Urban Plan.

    (2002)
  • L.A. Arroyo et al.

    Integration of LiDAR and QuickBird imagery for mapping riparian biophysical parameters and land cover types in Australian tropical savannas

    For. Ecol. Manag.

    (2010)
  • C. Baker et al.

    Mapping wetlands and riparian areas using Landsat ETM + imagery and decision-tree-based models

    Wetlands

    (2006)
  • M.J. Baptist et al.

    Assessment of the effects of cyclic floodplain rejuvenation on flood levels and biodiversity along the Rhine River

    River Res. Appl.

    (2004)
  • R.F. Bay et al.

    Success of active revegetation after Tamarix removal in riparian ecosystems of the Southwestern United States: a quantitative assessment of past restoration projects

    Restor. Ecol.

    (2008)
  • S. Bell et al.

    What counts? Volunteers and their organisations in the recording and monitoring of biodiversity

    Biodivers. Conserv.

    (2008)
  • T. Buffin-Bélanger et al.

    Freedom space for rivers: an economically viable river management concept in a changing climate

    Geomorphology

    (2015)
  • D.P. Bunting et al.

    Using existing agricultural infrastructure for restoration practices

    J. Arid Environ.

    (2011)
  • S.R. Carpenter et al.

    Plausible futures of a social–ecological system: Yahara watershed, Wisconsin, USA

    Ecol. Soc.

    (2015)
  • P. Cavaillé et al.

    Functional and taxonomic plant diversity for riverbank protection works: bioengineering techniques close to natural banks and beyond hard engineering

    J. Environ. Manag.

    (2015)
  • N. Clerici et al.

    Ranking European regions as providers of structural riparian corridors for conservation and management purposes

    Int. J. Appl. Earth Obs. Geoinf.

    (2013)
  • Y. Chen et al.

    Effects of ecological water conveyance on groundwater dynamics and riparian vegetation in the lower reaches of Tarim River, China

    Hydrol. Process.

    (2010)
  • A. Chin et al.

    The significance of perceptions and feedbacks for effectively managing wood in rivers

    River Res. Appl.

    (2014)
  • D.J. Cooper et al.

    Novel plant communities limit the effects of a managed flood to restore riparian forests along a large regulated river

    River Res. Appl.

    (2012)
  • N. Dalkey et al.

    An experimental application of the DELPHI method to the use of experts

    Manag. Sci.

    (1963)
  • H. da Silva Melo

    Educação Ambiental em uma Comunidade Rural: uma abordagem sobre a preservação de nascentes e matas ciliares/Environmental Education in a rural community: an approach to the preservation of springs and riparian forests

    Rev. Educom. Ambient.

    (2011)
  • D. De Steven et al.

    Understory vegetation as an indicator for floodplain forest restoration in the Mississippi River Alluvial Valley, U.S.A.

    Restor. Ecol.

    (2015)
  • J. Diez et al.

    Will extreme climatic events facilitate biological invasions?

    Front. Ecol. Environ.

    (2012)
  • M.D. Dixon et al.

    Dynamics of plains cottonwood (Populus deltoides) forests and historical landscape change along unchannelized segments of the Missouri River, USA

    Environ. Manag.

    (2012)
  • M.D. Dixon et al.

    Effects of a “natural” flood event on the riparian ecosystem of a regulated large-river system: the 2011 flood on the Missouri River, USA

    Ecohydrology

    (2015)
  • S. Dufour et al.

    From the myth of a lost paradise to targeted river restoration: forget natural references and focus on human benefits

    River Res. Appl.

    (2009)
  • K. Džubáková et al.

    Monitoring of riparian vegetation response to flood disturbances using terrestrial photography

    Hydrol. Earth Syst. Sci.

    (2015)
  • EAFRD

    European Agricultural Fund for Rural Development. Council Regulation (EC) № 1290/2005 of 21 June 2005 on the Financing of the Common Agricultural Policy

    (2005)
  • EC (European Commission)

    Communication from the Commission to the European Parliament, the Council, the European Economic and Social Committee and the Committee of the Regions. Green Infrastructure (GI) — Enhancing Europe's Natural Capital

  • European Commission

    Common Implementation Strategy for the Water Framework Directive (2000/60/Ec)

  • P.H. Evangelista et al.

    Mapping invasive tamarisk (Tamarix): a comparison of single-scene and time-series analyses of remotely sensed data

    Remote Sens.

    (2009)
  • C.K. Feld et al.

    From natural to degraded rivers and back again

  • M.R. Felipe-Lucia et al.

    Interactions among ecosystem services across land uses in a floodplain agroecosystem

    Ecol. Soc.

    (2014)
  • M.R. Felipe-Lucia et al.

    Ecosystem services flows: why stakeholders' power relationships matter

    PLoS One

    (2015)
  • M.R. Fernandes et al.

    Riparian responses to extreme climate and land-use change scenarios

    Sci. Total Environ.

    (2016)
  • W. Fleming

    Volunteer watershed health monitoring by local stakeholders: New Mexico watershed watch

    J. Environ. Educ.

    (2003)
  • A.G. Garssen et al.

    Effects of climate-induced increases in summer drought on riparian plant species: a meta-analysis

    Freshw. Biol.

    (2014)
  • G.W. Geerling et al.

    Nature rehabilitation by floodplain excavation: the hydraulic effect of 16 years of sedimentation and vegetation succession along the Waal River, NL

    Geomorphology

    (2008)
  • G.H. Golet et al.

    Assessing societal impacts when planning restoration of large alluvial rivers: a case study of the Sacramento River project, California

    Environ. Manag.

    (2006)
  • E. González et al.

    Strategies to restore floodplain vegetation after abandonment of human activities

    Restor. Ecol.

    (2016)
  • E. González et al.

    Restoration of riparian vegetation: a global review of implementation and evaluation approaches in the international, peer-reviewed literature

    J. Environ. Manag.

    (2015)
  • M. González del Tánago et al.

    River restoration in Spain: theoretical and practical approach in the context of the European Water Framework Directive

    Environ. Manag.

    (2012)
  • W.L. Graf

    Downstream hydrologic and geomorphic effects of large dams on American rivers

    Geomorphology

    (2006)
  • W.L. Graf

    Dam nation: a geographic census of American dams and their large-scale hydrologic impacts

    Water Resour. Res.

    (1999)
  • S.V. Gregory et al.

    An ecosystem perspective of riparian zones

    BioScience

    (1991)
  • C.R. Groves et al.

    Planning for biodiversity conservation: putting conservation science into practice

    Bioscience

    (2002)
  • B. Gumiero et al.

    Effectiveness of the cross-compliance standard 5.2 “buffer strips” on protecting freshwater against diffuse nitrogen pollution

    Ital. J. Agron.

    (2016)
  • B. Gumiero et al.

    Linking the restoration of rivers and riparian zones/wetlands in Europe: sharing knowledge through case studies

    Ecol. Eng.

    (2013)
  • B. Gumiero et al.

    Riparian vegetation as indicator of channel adjustments and environmental conditions: the case of the Panaro River (Northern Italy)

    Aquat. Sci.

    (2015)
  • A.M. Gurnell et al.

    A multi-scale hierarchical framework for developing understanding of river behaviour to support river management

    Aquat. Sci.

    (2016)
  • F.M. Hughes et al.

    Restoring riparian ecosystems: the challenge of accommodating variability and designing restoration trajectories

    Ecol. Soc.

    (2005)
  • F.M.R. Hughes et al.

    Allocation of river flows for restoration of floodplain forest ecosystems: a review of approaches and their applicability in Europe

    Environ. Manag.

    (2003)
  • K.R. Hultine et al.

    Tamarisk biocontrol in the western United States: ecological and societal implications

    Front. Ecol. Environ.

    (2010)
  • Cited by (117)

    View all citing articles on Scopus
    1

    equal contribution.

    View full text