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Annual biomass growth covariance is less negative across strips than within strips at Cedar Creek in 2010–2021

We tested how repeated strip samples affect the covariance of consecutive annual biomass growth values. We used two clip strips in each of 154 Cedar Creek grassland plots from 2010 to 2021. We calculated log growth and removed the mean of each strip in each year. Adjacent growth covariance was -0.08846 within strips and -0.03375 across strips. Its negative magnitude was 61.8% smaller across strips. The covariance gap was 0.05471, with a 95% plot bootstrap interval of 0.04633 to 0.06278. The gap was positive in all ten annual pairs and in checks of earlier years, sorting roles, and biomass units. Normalization changed the comparison. Observed associations were -0.490 within strips and -0.187 across strips. Under an independent strip-error model, the normalized shared component was -0.436. Its difference from the within-strip association was uncertain. Thus, a large covariance difference did not establish a large change in the normalized shared association. Sorting methods, spatial variation, and shared errors limit interpretation. The strip contrast also had time structure at a two-year lag. Negative covariance of consecutive growth values can arise from differencing independent annual values, so these estimates do not measure ecological recovery speed. The package preserves unchanged source data, provenance, code, results, figures, model checks, and offline reproduction steps.

grassland · biodiversity · biomass · sampling error · temporal covariance · Cedar Creek · reproducibility

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References

6
  1. usesdoi:10.6073/pasta/87b179ac496a0343e6860b19f33158fc

    Original Cedar Creek Biodiversity II biomass data, version knb-lter-cdr.273.12. Unchanged source files are preserved.

  2. doi:10.1038/nature04742

    Prior evidence on plant diversity and temporal biomass stability in this experiment.

  3. doi:10.1111/ele.12088

    Prior theory explicitly includes observation error and spatial sample variation in biomass stability.

  4. doi:10.1371/journal.pone.0087084

    Prior method for separating sample error from population synchrony.

  5. usesCedar Creek e120, 1997–2021: the richness effect on total live biomass stopped increasing after about 2005, but the effect on planted-species biomass continued to increase sci:sha256:6bc19f30a8ffdf3c8c7098f9e84c102f63c16e650fd3f65e84c7ef82d0da36b4

    We reuse its retained original source files and harvest conventions. The present code independently builds strip biomass and tests a different endpoint.

  6. usesCedar Creek plots with more planted species had lower mean annual log biomass loss and higher mass loss in 2011–2021 sci:sha256:f5f19fb12897fb117912d465d27e9e5e19bc7b040e1c4830e95147a90a5165af

    Its annual-loss result and stated strip-sampling limit informed the present question. We test adjacent growth covariance with separate strips.

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