In RivFishTIME river fish (1964–2019), range position predicts abundance–temperature slopes between sites, but not between species at one site or abundance trends
Brown et al. (2024, PNAS) reported that river fish populations near the cold edge of the species range increase with warming more often than populations near the warm edge. Their model compared the same species at different sites, with species intercepts only. We tested this claim again with RivFishTIME: 89,993 native-range populations of 864 species in 10,636 time series (1964–2019, span of 10 years or more). We used native ranges from a basin-scale occurrence database and CRU TS temperature converted to water temperature. Range position is 0 at the warm edge and 1 at the cold edge. With species intercepts, the published response replicated: positive abundance–temperature slopes were 8.6 percentage points more frequent at the cold edge (95% CI 4.8 to 12.4, clustered by basin; logit 0.35 vs. 0.235 in the original). But range position did not predict the sign of the abundance trend over years (−0.9 points, CI −6.7 to 4.9). The association remained with detrended temperature (+6.8, CI 1.7 to 11.9), so it shows year-to-year covariation, not a trend. When we divided range position into the site mean and the deviation of each species from it, the between-site part was +13.7 (CI 9.2 to 18.2) and the within-site part was −6.4 (CI −14.4 to 1.6). The difference was −20.1 (CI −29.4 to −10.8). With site intercepts, species near their cold edge and species near their warm edge at the same site did not differ (−1.7, CI −6.0 to 2.6). A range-position effect for each population predicts the same sign in all these comparisons. Thus, in these data the pattern is better explained as a site-level relation: at cooler sites, catches of most species tend to be higher in warm years. The results were the same with thermal position, with 5 or more survey years, with or without the native filter, and without each of the four main countries. Limitations: basin-scale ranges and 0.5° air temperature are coarse; the within-site test has less leverage for Tmax and detrended temperature; the data come mostly from the USA, Great Britain, France and Sweden.
freshwater fish · RivFishTIME · range position · climate change fingerprint · population trends · replication · fixed effects · between-site confounding · native range · temperature sensitivity
References
8- challengesdoi:10.1073/pnas.2410355121
We re-test its range-position fingerprint in RivFishTIME. The published association replicates with species intercepts, but it comes from between-site differences and year-to-year covariation, not from species-specific trends.
- usesdoi:10.25829/idiv.1873-10-4000
RivFishTIME fish time series (iDiv dataset 1873 v12, CC BY 4.0).
- doi:10.1111/geb.13210
RivFishTIME data paper (Comte et al. 2021).
- usesdoi:10.5281/zenodo.19511163
Native basin occurrence lists and basin polygons (2024 update) for native ranges.
- doi:10.1038/sdata.2017.141
Original basin-scale freshwater fish occurrence database (Tedesco et al. 2017).
- usesdoi:10.1038/s41597-020-0453-3
CRU TS 4.10 monthly air temperature.
- doi:10.1073/pnas.2011639118
Earlier RivFishTIME study of thermophilization (Comte et al. 2021).
- On the same BBS routes, landbird populations in the warmer part of their species' thermal range declined relative to colder-range populations in 1994–2023, but not in 1970–1993 sci:sha256:0b3a500a77e7b948e13239d57f1b8375c2f28b6f677fe48b45c57f4b1647cd53
Analogous species-plus-route test in North American birds, which found relative declines of warm-range populations; our two-way estimates for river fish have the opposite sign.
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