Strip differences account for 47% of the richness slope in relative biomass variance in 154 Cedar Creek plots, 2011–2021
We tested how spatial samples affect the relation between plant diversity and biomass variation at Cedar Creek, Minnesota. We used two strips in each of 154 plots with 1, 2, 4, 8 or 16 planted species in 2011–2021. An exact identity separates temporal variance of the strip mean into cross-strip covariance and one quarter of the variance of strip differences. We divided each component by the square of mean biomass. The observed richness slope was −0.01326 per doubling of planted species. Strip differences supplied −0.00628, or 47% of that slope. The shared component supplied −0.00698, with a 95% plot bootstrap interval of −0.01449 to +0.00017. The relation thus became smaller and less certain. However, the shared slope remained clearly negative after removal of linear trends and for adjacent-year squared changes. An independent CSV calculation matched all 3,388 strip totals and the primary variance estimates. Known-model simulations showed that covariance can remove independent sample variation, but shared sample errors can retain a false temporal relation. Strip differences include real spatial variation and sample processing differences. Their removal estimates whole-plot temporal variance only under error assumptions which two strips cannot identify. The result does not show that diversity has no stability effect. It provides a fixed-data audit and a method for separating components of measured variation. The package contains source data, provenance, code, all results, bootstrap draws, figures, and reproduction instructions.
biodiversity · Cedar Creek · grassland · biomass · temporal stability · spatial variation · sampling error · paired samples · variance decomposition · reproducibility
References
6- usesdoi:10.6073/pasta/87b179ac496a0343e6860b19f33158fc
Unchanged source biomass data and EML metadata, Cedar Creek Biodiversity II, version knb-lter-cdr.273.12, CC BY 4.0.
- 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 later-period loss analysis and stated spatial-sampling limit motivated this paired-strip variance audit and its primary 2011–2021 period. Our metric differs from its log-loss metric.
- 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 reused its retained unchanged source data and examined its biomass history and harvest conventions. The present code independently rebuilds labelled strip totals.
- doi:10.1038/nature04742
Earlier temporal stability result in the Cedar Creek diversity experiment.
- doi:10.1038/s41559-018-0647-7
Prior work on several parts of the diversity–stability relation.
- supportsdoi:10.1038/s41467-023-37395-y
It reports lower spatial biomass variation at greater plant diversity across 83 grasslands. This provides context for the real ecological variation within our strip component.
Cited by
1 publicationPublic catalog entries on Sciscape.
- Removal of linear trends reduced the geometric mean variance ratio for CSV-listed plants from 1.33 to 1.07 in 35 Cedar Creek 16-species plots, 2010–2021
Recent evidence that spatial strip variation affects temporal variance measures.