Abstract
Inland navigation in Europe is proposed to increase in the coming years, being promoted as a low-carbon form of transport. However, we currently lack knowledge on how this would impact biodiversity at large scales and interact with existing stressors. Here we addressed this knowledge gap by analysing fish and macroinvertebrate community time series across large European rivers comprising 19,592 observations from 4,049 sampling sites spanning the past 32 years. We found ship traffic to be associated with biodiversity declines, that is, loss of fish and macroinvertebrate taxonomic richness, diversity and trait richness. Ship traffic was also associated with increases in taxonomic evenness, which, in concert with richness decreases, was attributed to losses in rare taxa. Ship traffic was especially harmful for benthic taxa and those preferring slow flows. These effects often depended on local land use and riparian degradation. In fish, negative impacts of shipping were highest in urban and agricultural landscapes. Regarding navigation infrastructure, the negative impact of channelization on macroinvertebrates was evident only when riparian degradation was also high. Our results demonstrate the risk of increasing inland navigation on freshwater biodiversity. Integrative waterway management accounting for riparian habitats and landscape characteristics could help to mitigate these impacts.
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Data availability
All data and R code used in this study are available in an open-source repository (https://github.com/aaronsexton/Sextonetal_Navigation_Biodiversity_Supplementals).
Code availability
R code used in this study are also available in the same open-source repository as the data (https://github.com/aaronsexton/Sextonetal_Navigation_Biodiversity_Supplementals).
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Acknowledgements
We thank N. Casajus for providing continued assistance and recommendations on analyses and data representation. Additionally, we thank the UNECE for providing locations of inland ports locks and canals. This research is a product of the NAVIDIV group funded by the synthesis centre CESAB of the French Foundation for Research on Biodiversity (FRB; www.fondationbiodiversite.fr) and by the French National Research Program on Transport Infrastructure, Territories, Ecosystems and Landscapes (ITTECOP; https://www.ittecop.fr/en/) of the French Ministry of Ecological Transition (MTE). S.C.J acknowledges funding through the Leibniz Competition project ‘Freshwater Megafauna Futures’. P.H. received funding from the EU Horizon 2020 project eLTER PLUS (grant agreement no. 871128). A.L. received funding from the Spanish Ministry of Science and Innovation (project PID2020-115830GB-100). A.D.B. received funding from EU Horizon 2020 MERLIN project (grant agreement no. 101036337).
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A.N.S., A.J. and J.-N.B. conceived of the study. C.S., C.W., E.T., J.B., A.D.B., V.M.F., K.M.W., S.C.J., C.G.L. and A.S.-K. contributed to initial ideas. A.N.S. and A.J. designed and conducted analyses. P.H., M.A.E.F, G.A., J.-F.F., A.D., V.E., Z.C., M.F., P.G., G.V., M.C.-A., A.L. A.M., R.B.S., J.S.S., R.V., E.W., C.W., E.T. and J.B. provided biodiversity data, A.N.S. wrote the first draft of the manuscript and all authors provided important input on manuscript writing.
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Extended data
Extended Data Fig. 1 Macroinvertebrate’s response to channelization is dependent on riparian degradation and agricultural cover.
The panels show the marginal effect of channelization from the GLMMs on macroinvertebrate communities along a gradient of riparian degradation and agricultural land use. A negative value on the y-axis indicates a negative impact of channelization on said metric (for example a decrease in taxonomic richness), and a value at 0 (grey horizontal line) indicates a null effect. Left panel shows the relationships of taxonomic richness and right panel shows the prevalence of invasive taxa. Predictors were standardized to zero mean and a SD of ±1.
Extended Data Fig. 2 Fish and macroinvertebrate trait relationships with ship traffic across different land use scenarios.
Trait scores associated with the environmental axis of heightened ship traffic in the RLQ analysis are shown in the ‘Full Dataset’ column, and are the values shown in the ordination of Figs. 4 and 5. Columns two and three of each table show the trait associations with heightened ship traffic when the RLQ is re-run in highly agricultural sites (those with the top 25% of agricultural cover across the datasets) and in highly urbanized sites.
Extended Data Fig. 3 Relationships between taxonomic evenness and the abundance and occurrences of rare species in fish and macroinvertebrates.
We defined a rare species as a species whose abundance accounting for less than 25% of the total community abundance (see Supplementary File 2 for details). Blue line represents the model regression and the area in grey surrounding the line represented the 95% confidence interval.
Supplementary information
Supplementary Information
Supplementary Figs. 1–5.
Supplementary Table 1–5
Supplementary Tables 1–5.
Supplementary File 1
Code for reproducing the subcatchment level selection for models.
Supplementary File 2
Code for reproducing the models run to show a relationship between rare species and community evenness.
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Sexton, A.N., Beisel, JN., Staentzel, C. et al. Inland navigation and land use interact to impact European freshwater biodiversity. Nat Ecol Evol 8, 1098–1108 (2024). https://doi.org/10.1038/s41559-024-02414-8
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DOI: https://doi.org/10.1038/s41559-024-02414-8
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