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English river fish communities did not shift toward warm-water species as local air warmed 0.28 C per decade in 1990-2025; warm summers raised the next-year index only slightly

Question: did the community temperature index (CTI) of English river fish follow local warming, and does a warm summer change the CTI in the next year? Approach: we used 24,945 Environment Agency electric-fishing surveys at 2,297 sites in six regions, 1990-2025. The species thermal index (STI) is the mean 1991-2020 E-OBS air temperature of the European cells where GBIF density maps show the species. Models had site, month, method and strategy fixed effects. The short-term test used the previous June-August anomaly and a next-summer placebo, with standard errors clustered by year. Results: local air temperature increased 0.276 C per decade, but the presence CTI decreased 0.021 C per decade (95% CI -0.028 to -0.013). The European eel decrease caused most of this; without eel the trend was +0.005 (-0.001 to +0.012), 2% of the warming rate. Regional trends without eel were from -0.052 to +0.056 C per decade, and the trend changed with survey season and period. A 1 C warmer previous summer raised the CTI by 0.009 C (0.002 to 0.016); the placebo was 0.004 (-0.007 to 0.014). Without eel the values were 0.012 and 0.000. Warm-water cyprinids (bleak, barbel, gudgeon, bream) carried this response, but across 25 species the response did not clearly increase with STI. This short-term slope predicts only +0.002 to +0.003 C per decade. Eel collapse, salmon decrease and increases of small benthic species changed the CTI more than warming. Limitations: air temperature is a proxy for water temperature; the short-term test has about 34 independent years and weak regional replication; the abundance-weighted CTI failed the placebo; water quality was not modelled.

river fish · community temperature index · thermophilization · climate change · summer temperature · European eel · cyprinid recruitment · observation bias · placebo test · Environment Agency · NFPD · E-OBS · GBIF · England · regional replication · climate debt

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References

8
  1. reviewsdoi:10.1073/pnas.2011639118

    Reported global thermophilization of river fish communities; we test the CTI response in English rivers to 2025.

  2. doi:10.1016/j.watres.2025.123163

    Fish response to water-quality improvement in English rivers from the same database.

  3. usesdoi:10.1029/2017JD028200

    E-OBS gridded temperature (Cornes et al. 2018).

  4. useshttps://www.data.gov.uk/dataset/823e7de7-33a2-4fc6-9a79-4c7672130094/freshwater-fish-surveys-nfpd

    Environment Agency National Fish Populations Database, Open Government Licence v3.

  5. useshttps://www.gbif.org

    GBIF occurrence density maps used to compute species thermal indices.

  6. Trawl community thermal indices followed year-to-year SST at 0.14-0.44 C per C in 6 of 9 Atlantic and Gulf surveys and at most 0.09 in 5 Pacific surveys, 1970-2020; early slopes gave no forecast gain sci:sha256:edec25d0faea54bfa8e98e8d103351c0014eb2f4703edf9966b42f9cbc7833da

    Campaign study of trawl fish CTI tracking of sea temperature; a marine comparison.

  7. Winter feeder-bird communities in North America shifted to warmer-adapted species in 2002-2024, but year-to-year and local winter temperature did not explain the shift sci:sha256:c94acf78273342e4059d41fb6b8494821e7960ffeaf617f2c1e88631488fe9f2

    Campaign study where CTI changed without a link to local temperature (winter birds).

  8. Warmer winters did not lower spring river invertebrate abundance at 1,503 English sites in 1991-2017; warm-summer richness gains were smaller at high-ammonia sites sci:sha256:f25760cd730cef83fb8c57919cadc682c94f68f367bad864195074fc7e13dbc2

    Campaign study of temperature effects on English river invertebrates.

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