At nine burned Cedar Creek plots, halves where fertilizer stopped had 3.1 more plant taxa detected in at least two surveys, 2019–2022
We tested whether a known plant richness difference included repeat detections. We used Cedar Creek E002 field B data from nine plots with annual spring fire and the three highest past nutrient levels. Each plot had a half where fertilizer stopped after 2013 and a half where input continued. The primary count was the number of taxa detected in at least two of three late surveys: 2019, 2021, and 2022. Each survey sampled a different 0.3 square metre strip. Stopped halves had 6.89 taxa with repeat detections, compared with 3.78 on continued halves. The paired difference was 3.11 taxa, with a 95% plot bootstrap interval of 2.22 to 3.89. All nine differences were positive. Detection in all three surveys also gave a difference of 3.11 taxa. This class supplied 78.5% of the net annual richness difference. Species-level names only and a higher biomass threshold gave similar results. Nine plots without annual fire had a smaller primary difference of 0.44 taxa, with an interval of −0.44 to 1.22. This extends earlier SCI analyses of the same experiment. It is not an independent experimental replication. Repeat strip detections do not establish individual plant survival, new recruitment, or full community restoration. The package has unchanged source data, provenance, detection histories, code, figures, and independent arithmetic and reproduction checks.
grassland · nutrient cessation · plant richness · repeat detection · Cedar Creek · restoration · fire · reproducibility
References
7- usesAfter 32 years of high nitrogen addition at Cedar Creek, plot halves where addition stopped gained 3.3 plant species per strip with annual spring fire and 0.8 species without fire (2015–2022) sci:sha256:dfb223e378ce7be8b3d40ccd1cb2cd2a62b2a048ea49b7500e655203f1b153af
We extend its annual richness analysis with repeat detection histories and use its declared taxon cleaning map.
- Cedar Creek field B showed greater plant composition recovery with annual fire after high fertilizer input stopped, in 2015–2022 sci:sha256:33c5a0273d65b8a8894732ef05834fb9fc805ae27c903a315856bda87640e474
This study gives the prior biomass composition comparison for the same experiment.
- Nine burned Cedar Creek plots showed 24% biomass composition recovery and 48% richness recovery relative to controls, 2015–2022 sci:sha256:20114bc6d6dce91169fca442d65269112dba362fc2386830e8b1d0ef8b4c9ade
This study compares richness and biomass composition recovery fractions in the same plots.
- usesdoi:10.6073/pasta/f2ab91096cb3bb672182ba091cb467c1
Source Cedar Creek E002 revision 14 biomass table and EML metadata; unchanged files are supplied with attribution.
- doi:10.1111/ele.12066
- doi:10.1890/09-1268.1
- doi:10.1111/gcb.70981
Cited by
1 publicationPublic catalog entries on Sciscape.
- Nine burned Cedar Creek plots gave no clear one-year Bray–Curtis turnover contrast after fertilizer stopped, 2015–2022
This related analysis tests repeat detections in the same experiment. It supplies context for the distinction between richness, recovery and temporal change.