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  • 1
    Online Resource
    Online Resource
    San Diego :Elsevier Science & Technology,
    Keywords: Stream ecology. ; Electronic books.
    Type of Medium: Online Resource
    Pages: 1 online resource (624 pages)
    Edition: 1st ed.
    ISBN: 9780128039045
    DDC: 577.6/4
    Language: English
    Note: Front Cover -- Intermittent Rivers and Ephemeral Streams: Ecology and Management -- Copyright -- Contents -- Contributors -- Preface -- Chapter 1: General Introduction -- 1.1 What Are Intermittent Rivers and Ephemeral Streams (IRES)? -- 1.2 Causes of Flow Intermittence -- 1.3 Global Distribution and Areal Importance of IRES -- 1.4 Trends in a Context of Water Scarcity and Climate Change -- 1.5 Ecological Features of IRES -- 1.6 Legislation, Protection, Restoration, and Management of IRES -- 1.7 The Structure of This Book -- Acknowledgments -- References -- Chapter 2.1: Geomorphology and Sediment Regimes of Intermittent Rivers and Ephemeral Streams -- 2.1.1 Introduction -- Determinants of IRES Catchment Conditions -- Geomorphological Zones in IRES -- 2.1.2 Upland Zone -- 2.1.3 Piedmont Zone -- 2.1.4 Lowland Zone -- 2.1.5 Floodout Zone -- 2.1.6 Distinctions in IRES Longitudinal Trends -- 2.1.7 Influence of Human Activities on IRES Morphology and Sediment Regimes -- 2.1.8 Diversity of IRES at a Global Scale -- 2.1.9 Synthesis and New Research Directions -- Acknowledgments -- References -- Chapter 2.2: Flow Regimes in Intermittent Rivers and Ephemeral Streams -- 2.2.1 Introduction -- 2.2.2 Controls on the Natural Flow Regime of IRES -- 2.2.3 Methods to Characterize Flow Regimes of IRES -- Wet/Dry Mapping -- Imagery: From Satellites to Site Cameras -- Field Loggers and Flow Surrogates -- Hydrological Metrics -- Modeling -- 2.2.4 Describing and Classifying Flow Regimes of IRES: Case Studies -- 2.2.5 Conclusions: Research Needs and Future Perspectives -- Acknowledgments -- References -- Further Reading -- Chapter 2.3: Hydrological Connectivity in Intermittent Rivers and Ephemeral Streams -- 2.3.1 Introduction -- 2.3.2 What Governs Hydrological Connectivity in IRES?. , 2.3.3 Hydrological Connectivity, Intermittence, and Surface Water Drying and Rewetting in IRES -- 2.3.4 Longitudinal Hydrological Connectivity in IRES -- 2.3.5 Lateral Hydrological Connectivity in IRES -- 2.3.6 Vertical Hydrological Connectivity in IRES -- 2.3.7 A Preliminary Conceptual Framework for Exploring Intermittence, Connectivity, and Interacting Hydrological Dimensio ... -- 2.3.8 Conclusions -- Acknowledgments -- References -- Further Reading -- Chapter 3.1: Water Physicochemistry in Intermittent Rivers and Ephemeral Streams -- 3.1.1 Introduction -- 3.1.2 Spatial Variability of Physicochemistry in IRES -- The Longitudinal Dimension -- The Vertical Dimension -- The Lateral Dimension -- 3.1.3 Temporal Variability of Water Physicochemistry in IRES -- Daily Variability -- Seasonal Variability -- Seasonal variability along the longitudinal dimension -- Seasonal variability along the vertical dimension -- Seasonal variability along the lateral dimension -- Interannual Variability in Physicochemistry: Some Factors Involved -- Temporal Variability at Longer Scales: IRES in the Context of Global Change -- 3.1.4 Changes in Water Physicochemistry During Drying and Rewetting -- Physicochemistry in Remnant Pools -- Temperature -- Dissolved oxygen -- Salinity -- Turbidity -- pH -- Physicochemistry During Complete Drying and the Rewetting Front -- 3.1.5 Conclusions -- References -- Further Reading -- Chapter 3.2: Nutrient and Organic Matter Dynamics in Intermittent Rivers and Ephemeral Streams -- 3.2.1 The 'Biogeochemical Heartbeat' of IRES -- 3.2.2 Nutrient and OM Dynamics Across Hydrological Phases in IRES -- Contraction -- Fragmentation -- Drying (Desiccation) -- Expansion -- 3.2.3 Knowledge Gaps and Research Opportunities -- References -- Chapter 4.1: The Biota of Intermittent Rivers and Ephemeral Streams: Prokaryotes, Fungi, and Protozoans. , 4.1.1 Role and Relevance of Microbes in IRES -- 4.1.2 Diversity of Prokaryotes in IRES -- Factors Controlling Prokaryotic Communities in IRES -- Prokaryotic Diversity in IRES vs perennial rivers and streams -- 4.1.3 Diversity of Fungi in IRES -- Factors Controlling Fungal Communities in IRES -- Fungal Diversity in IRES vs perennial rivers and streams -- 4.1.4 Diversity of Protozoans in IRES -- Factors Controlling Protozoan Communities in IRES -- Protozoan Diversity in IRES vs. Perennial Rivers and Streams -- 4.1.5 Resistance and Resilience of Microbes in IRES -- Refugial Habitats -- Microbial Life Strategies -- 4.1.6 Microbial Diversity and Ecosystem Functioning in IRES -- Roles of Microbes in River Ecosystem Functioning -- Microbial Functioning in IRES and Links With Microbial Community Structure -- 4.1.7 Future Challenges -- References -- Chapter 4.2: The Biota of Intermittent Rivers and Ephemeral Streams: Algae and Vascular Plants -- 4.2.1 Introduction: Primary Producers in IRES -- 4.2.2 Microbial Primary Producers in IRES: Cyanobacteria and Algae -- Morphological and Physiological Adaptations to Drying -- Algal-Derived Stream Metabolism in IRES -- Latitudinal Variation in Algal Community Composition -- Mediterranean IRES -- Hot-desert IRES -- Cold-desert IRES -- 4.2.3 Vascular Aquatic Plants -- Vascular Macrophytes in IRES -- Vascular Plant Adaptations to Drying -- Functional groups -- Life History Traits Involved in Tolerance to Drying -- Implications of Drying for Vascular Plant Species Richness -- 4.2.4 Vascular Riparian Plants -- Riparian Vegetation Along IRES in Different Ecoregions -- Riparian Plant Adaptations in IRES -- Reproductive Trait Adaptations and Trade-Offs -- Landscape Biodiversity Patterns -- Landscape context and connectivity -- Rare and endemic riparian species -- Riparian community context. , 4.2.5 Conservation and Management Issues of Primary Producers in IRES -- References -- Further Reading -- Chapter 4.3: The Biota of Intermittent Rivers and Ephemeral Streams: Aquatic Invertebrates -- 4.3.1 Introduction -- 4.3.2 IRES as Habitats for Aquatic Invertebrates -- 4.3.3 Taxonomic Diversity of IRES Invertebrate Communities -- Temporal Variability in Taxonomic Diversity -- Spatial Variability in Taxonomic Diversity -- Phylogenetic Diversity -- 4.3.4 Functional Diversity of IRES Invertebrate Communities -- 4.3.5 Invertebrate Adaptations to Flow Intermittence -- Refuge Use Promotes Persistence in IRES -- Life Cycle Adaptations and Refuge Use Interact to Promote Survival -- Adaptations to IRES Are Trade-Offs That Also Influence Other Aspects of Survival -- 4.3.6 Threats to IRES Invertebrate Communities -- 4.3.7 Managing IRES to Promote Aquatic Invertebrate Biodiversity -- 4.3.8 Conclusions and Future Research Priorities -- References -- Chapter 4.4: The Biota of Intermittent Rivers and Ephemeral Streams: Terrestrial AND Semiaquatic Invertebrates -- 4.4.1 Introduction -- 4.4.2 Habitat Requirements of IRES Invertebrates -- 4.4.3 Taxonomic Diversity of TSAI Communities -- 4.4.4 Functional Diversity of TSAI Communities -- 4.4.5 Adaptations of TSAI to Flow Intermittence -- 4.4.6 Threats to the TSAI Communities of IRES -- 4.4.7 Managing IRES to Preserve TSAI Diversity and Their Ecological Functions -- 4.4.8 Knowledge Gaps and Research Needs -- 4.4.9 Conclusions -- References -- Chapter 4.5: The Biota of Intermittent Rivers and Ephemeral Streams: Fishes -- 4.5.1 Introduction -- 4.5.2 The fish fauna of IRES -- African IRES and Their Fishes -- Australian IRES and Their Fishes -- North American IRES and Their Fishes -- IRES of Mediterranean Europe and Their Fishes -- 4.5.3 Why Do Fish Live in IRES? -- 4.5.4 How Do Fish Survive in IRES?. , 4.5.5 Threats to Fishes in Intermittent Rivers -- Drought and Climate Change -- Water Extraction, River Regulation, and Fragmentation of Habitat -- Alien Species -- 4.5.6 Conservation Priorities for Fish in IRES -- 4.5.7 Conclusions -- References -- Chapter 4.6: The Biota of Intermittent and Ephemeral Rivers: Amphibians, Reptiles, Birds, and Mammals -- 4.6.1 Introduction -- 4.6.2 Importance of IRES for Amphibians, Reptiles, Birds, and Mammals -- Water and Food Resources -- Breeding and Nesting Sites -- Aquatic and Terrestrial Movement Corridors -- Migration Stopovers and Resting and Shelter Areas -- 4.6.3 Ecological Roles of Wildlife in IRES -- Consumers, Prey, and Seed Dispersal Agents -- Landscape Engineers -- Nutrient Cycling -- 4.6.4 Flow Intermittence Effects on Wildlife -- Amphibians -- Reptiles -- Birds -- Mammals -- 4.6.5 Wildlife Adaptations to Cope With Flow Intermittence -- Morphological Adaptations -- Physiological Adaptation -- Behavioral Adaptations -- 4.6.6 Vulnerability, Conservation, and Management of Wildlife in IRES -- Flow Alteration and Habitat Degradation -- Water Pollution -- Spread of Invasive Species and Diseases -- Climate Change -- Recommendations for Conservation and Management in the Context of Global Change -- 4.6.7 Conclusions -- Acknowledgments -- References -- Chapter 4.7: Food Webs and Trophic Interactions in Intermittent Rivers and Ephemeral Streams -- 4.7.1 Introduction -- 4.7.2 The Base of IRES Food Webs -- 4.7.3 Consumer-Resource Dynamics in IRES -- 4.7.4 Multidimensional Interactions Within IRES -- Longitudinal Interactions -- Lateral Interactions -- Vertical Interactions -- 4.7.5 Effects of Regional Differences on Food Webs in IRES -- 4.7.6 Structure of IRES Food Webs -- 4.7.7 Trophic Interactions in IRES in the Future -- References -- Further Reading. , Chapter 4.8: Resistance, Resilience, and Community Recovery in Intermittent Rivers and Ephemeral Streams.
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  • 2
    Publication Date: 2024-02-07
    Description: Aim: Invasive alien species are a growing problem worldwide due to their ecological, economic and human health impacts. The “killer shrimp” Dikerogammarus villosus is a notorious invasive alien amphipod from the Ponto-Caspian region that has invaded many fresh and brackish waters across Europe. Understandings of large-scale population dynamics of highly impactful invaders such as D. villosus are lacking, inhibiting predictions of impact and efficient timing of management strategies. Hence, our aim was to assess trends and dynamics of D. villosus as well as its impacts in freshwater rivers and streams. Location: Europe. Methods: We analysed 96 European time series between 1994 and 2019 and identified trends in the relative abundance (i.e. dominance %) of D. villosus in invaded time series, as well as a set of site-specific characteristics to identify drivers and determinants of population changes and invasion dynamics using meta-regression modelling. We also looked at the spread over space and time to estimate the invasion speed (km/year) of D. villosus in Europe. We investigated the impact of D. villosus abundance on recipient community metrics (i.e. abundance, taxa richness, temporal turnover, Shannon diversity and Pielou evenness) using generalized linear models. Results: Population trends varied across the time series. Nevertheless, community dominance of D. villosus increased over time across all time series. The frequency of occurrences (used as a proxy for invader spread) was well described by a Pareto distribution, whereby we estimated a lag phase (i.e. the time between introduction and spatial expansion) of approximately 28 years, followed by a gradual increase before new occurrences declined rapidly in the long term. D. villosus population change was associated with decreased taxa richness, community turnover and Shannon diversity. Main Conclusion: Our results show that D. villosus is well-established in European waters and its abundance significantly alters ecological communities. However, the multidecadal lag phase prior to observed spatial expansion suggests that initial introductions by D. villosus are cryptic, thus signalling the need for more effective early detection methods.
    Type: Article , PeerReviewed
    Format: text
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  • 3
    Publication Date: 2024-02-07
    Description: Globalization has led to the introduction of thousands of alien species worldwide. With growing impacts by invasive species, understanding the invasion process remains critical for predicting adverse effects and informing efficient management. Theoretically, invasion dynamics have been assumed to follow an “invasion curve” (S-shaped curve of available area invaded over time), but this dynamic has lacked empirical testing using large-scale data and neglects to consider invader abundances. We propose an “impact curve” describing the impacts generated by invasive species over time based on cumulative abundances. To test this curve's large-scale applicability, we used the data-rich New Zealand mud snail Potamopyrgus antipodarum, one of the most damaging freshwater invaders that has invaded almost all of Europe. Using long-term (1979–2020) abundance and environmental data collected across 306 European sites, we observed that P. antipodarum abundance generally increased through time, with slower population growth at higher latitudes and with lower runoff depth. Fifty-nine percent of these populations followed the impact curve, characterized by first occurrence, exponential growth, then long-term saturation. This behaviour is consistent with boom-bust dynamics, as saturation occurs due to a rapid decline in abundance over time. Across sites, we estimated that impact peaked approximately two decades after first detection, but the rate of progression along the invasion process was influenced by local abiotic conditions. The S-shaped impact curve may be common among many invasive species that undergo complex invasion dynamics. This provides a potentially unifying approach to advance understanding of large-scale invasion dynamics and could inform timely management actions to mitigate impacts on ecosystems and economies.
    Type: Article , PeerReviewed
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  • 4
    Publication Date: 2024-02-07
    Description: As alien invasive species are a key driver of biodiversity loss, understanding patterns of rapidly changing global species compositions depends upon knowledge of invasive species population dynamics and trends at large scales. Within this context, the Ponto-Caspian region is among the most notable donor regions for aquatic invasive species in Europe. Using macroinvertebrate time series collected over 52 years (1968–2020) at 265 sites across 11 central and western European countries, we examined the occurrences, invasion rates, and abundances of freshwater Ponto-Caspian fauna. We examined whether: (i) successive Ponto-Caspian invasions follow a consistent pattern of composition pioneered by the same species, and (ii) Ponto-Caspian invasion accelerates subsequent invasion rates. In our dataset, Ponto-Caspian macroinvertebrates increased from two species in 1972 to 29 species in 2012. This trend was parallelled by a non-significant increasing trend in the abundances of Ponto-Caspian taxa. Trends in Ponto-Caspian invader richness increased significantly over time. We found a relatively uniform distribution of Ponto-Caspian macroinvertebrates across Europe without any relation to the distance to their native region. The Ponto-Caspian species that arrived first were often bivalves (46.5% of cases), particularly Dreissena polymorpha, followed secondarily by amphipods (83.8%; primarily Chelicorophium curvispinum and Dikerogammarus villosus). The time between consecutive invasions decreased significantly at our coarse regional scale, suggesting that previous alien establishments may facilitate invasions of subsequent taxa. Should alien species continue to translocate from the Ponto-Caspian region, our results suggest a high potential for their future invasion success highly connected central and western European waters. However, each species’ population may decline after an initial ‘boom’ phase or after the arrival of new invasive species, resulting in different alien species dominating over time.
    Type: Article , PeerReviewed
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  • 5
    Publication Date: 2024-02-07
    Description: Europe has experienced a substantial increase in non-indigenous crayfish species (NICS) since the mid-20th century due to their extensive use in fisheries, aquaculture and, more recently, pet trade. Despite relatively long invasion histories of some NICS and negative impacts on biodiversity and ecosystem functioning, large spatio-temporal analyses of their occurrences are lacking. Here, we used a large freshwater macroinvertebrate database to evaluate what information on NICS can be obtained from widely applied biomonitoring approaches and how usable such data is for descriptions of trends in identified NICS species. We found 160 time-series containing NICS between 1983 and 2019, to infer temporal patterns and environmental drivers of species and region-specific trends. Using a combination of meta-regression and generalized linear models, we found no significant temporal trend for the abundance of any species (Procambarus clarkii, Pacifastacus leniusculus or Faxonius limosus) at the European scale, but identified species-specific predictors of abundances. While analysis of the spatial range expansion of NICS was positive (i.e. increasing spread) in England and negative (significant retreat) in northern Spain, no trend was detected in Hungary and the Dutch-German-Luxembourg region. The average invasion velocity varied among countries, ranging from 30 km/year in England to 90 km/year in Hungary. The average invasion velocity gradually decreased over time in the long term, with declines being fastest in the Dutch-German-Luxembourg region, and much slower in England. Considering that NICS pose a substantial threat to aquatic biodiversity across Europe, our study highlights the utility and importance of collecting high resolution (i.e. annual) biomonitoring data using a sampling protocol that is able to estimate crayfish abundance, enabling a more profound understanding of NICS impacts on biodiversity.
    Type: Article , PeerReviewed
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  • 6
    Publication Date: 2024-04-11
    Description: The zebra mussel Dreissena polymorpha is one of the most successful, notorious, and detrimental aquatic invasive non-native species worldwide, having invaded Europe and North America while causing substantial ecological and socio-economic impacts. Here, we investigated the spatiotemporal trends in this species' invasion success using 178 macroinvertebrate abundance time series, containing 1451 records of D. polymorpha collected across nine European countries between 1972–2019. Using these raw (absolute) abundance data, we examined trends and drivers of occurrences and relative abundances of D. polymorpha within invaded communities. Meta-regression models revealed non-significant trends both at the European level and for the majority of the invaded countries, except for France (significant decreasing trend) and Hungary (marginally positive trend). At the European level, the number of D. polymorpha occurrences over time followed a flat-top bell-shaped distribution, with a steep increase between 1973–1989 followed by a plateau phase prior to significantly declining post-1998. Using a series of climatic and hydromorphological site-specific characteristics of invaded and uninvaded sites from two periods (1998–2002; 2011–2015), we found that native richness, non-native abundance, distance to the next barrier, and elevation were associated with the occurrence of D. polymorpha. We also found that higher native richness and lower latitude were related to lower relative abundances. Using Cohen's D as a measure of D. polymorpha impact, we found that biodiversity within the invaded sites was initially higher than in uninvaded ones, but then declined, suggesting differences in biodiversity trends across invaded and uninvaded sites. While our results emphasise the high invasion success of D. polymorpha, increasing stressors within the context of global change – particularly ongoing climate change – are likely to enhance invasion rates and the impact of D. polymorpha in the near future, exacerbated by the lack of timely and effective management actions.
    Type: Article , PeerReviewed
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