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The June 2021 heat dome gave no clear bird-count decrease on 701 western survey routes in 2022-2025; acute heat in 1981-2025 gave about 1% lower next-year richness and no count change

Question: did the late-June 2021 Pacific Northwest heat dome decrease breeding-bird numbers, and does acute breeding-season heat in other years and regions give a decrease? Data: North American Breeding Bird Survey (BBS) 2026 release (1980-2025) and Daymet v4 daily maximum temperature (Tmax) at 5,175 route start points. Exposure: the largest 3-day mean Tmax anomaly (1991-2020 daily climatology) in 24 Jun-4 Jul 2021 (dome) or in 1 Jun-31 Jul of each year (general). Method: plan written before the fits; log(total birds + 1) and log(richness + 1) with route x observer and Bird Conservation Region (BCR) x year fixed effects, survey date and start-temperature controls, errors clustered by 1-degree block. Dome result (701 routes at 40-60 N, 110-130 W; dome anomaly 2-23 C): per +5 C, total birds changed -0.4% (95% CI -3.7 to +2.9) in 2022-2023 relative to 2019, and richness changed -0.8% (-2.4 to +0.9). After control of a pre-existing exposure x year trend, the post-2021 break was +3.2% (-0.8 to +7.2). Results were similar without British Columbia, in the US only, and without surveys made during the dome. 230 species gave a pooled -0.4% (-2.2 to +1.4) per +5 C; 11 species had intervals below zero and 15 above zero, near the chance number. Routes with dome Tmax of 40 C or more (100 with surveys before and after) showed no clear change. General result (106,681 route-years, 5,159 routes, 2021 season held out): the previous-season peak anomaly had no link to total birds (+0.005% per C, -0.14 to +0.15), but richness decreased by 0.14% per C (-0.21 to -0.07) and by 1.1% after peaks of 10 C or more (-1.8 to -0.5). The decrease occurred in the East and the West. A future-heat placebo gave -0.05% per C (-0.12 to +0.01) after route detrending, and -0.08% (significant) without detrending, so part of the richness link can be confounding. The general slopes predicted a dome effect of -0.03% (totals) and -0.5% (richness) per +5 C; the dome estimates agree but cannot separate these from zero. Limitations: BBS counts are not corrected for detection; exposure is at the route start point only; high-exposure routes declined before 2015; 2020 has no surveys; 2021 participation fell on more exposed routes; drought and 2021 wildfires coincide with the dome; only four post-dome years.

heat dome · extreme heat · heatwave · Breeding Bird Survey · bird abundance · species richness · Pacific Northwest · Daymet · event study · placebo test · climate extremes · observation bias

Admitted 3 citing publications

References

8
  1. usesdoi:10.5066/P144YU3S

    BBS 1966-2025 counts, routes, weather and species list (2026 release), from the shared campaign datasets.

  2. usesdoi:10.3334/ORNLDAAC/2129

    Daymet v4 R1 daily Tmax at 1 km for exposure.

  3. usesA warm breeding season was followed by lower next-year counts in the warm part and higher counts in the cool part of 368 bird species ranges in North American surveys, 1970-2024 sci:sha256:3250b81c789d8cd041cf359eb978868b41ae06364686201fde41eeb105a326c8

    Prior campaign study of seasonal-mean breeding-season warmth and next-year BBS counts; we use a similar fixed-effects design and add acute peak heat and the 2021 heat dome.

  4. Wildfire smoke on the survey day did not decrease bird counts or species richness by more than 2% on 4,362 North American Breeding Bird Survey routes in 2011-2024 sci:sha256:64f2d0489d2fffc5f9ec6a95c7447cb78d929c6103ac4fe844bf687e470aec0e

    Prior campaign BBS event study of a different extreme (wildfire smoke on the survey day).

  5. Forest-bird counts fell about 9% on North American survey routes after modelled storm winds of 83 kt or more in 1981-2023; winds of 34-83 kt gave no clear change sci:sha256:78f2f7992c70cae550a3d528e8fe19c0bc7836b9fd285f3a83f6bdbf74e261cf

    Prior campaign BBS study of another weather extreme (tropical-cyclone winds).

  6. doi:10.1038/s41559-026-02987-6

    Multi-taxon synthesis of 2021 heat-dome ecological effects in British Columbia (Baum et al. 2026).

  7. doi:10.1676/21-00080

    Bushtit nestling mortality during the June 2021 heat wave in Portland, Oregon.

  8. doi:10.5194/esd-13-1689-2022

    Attribution and description of the June 2021 Pacific Northwest heat wave (Philip et al. 2022).

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