datasetpapers

Datasetpaper · plant functional ecology

Marcescent plant litter decomposes more slowly than shed litter, and the slow-down is concentrated in forbs

Version
ark:/99999/dp-marcescence-decomposition.v1
Concept
ark:/99999/dp-marcescence-decomposition
Source dataset
Angst et al. 2024 Functional Ecology raw data (marcescence and decomposition)

A compiled view of a research object (RO-Crate). Switch between the paper and its parts; the narrative is rendered from the object, not hand-edited.

Summary

Across 34 herbaceous species grown in a common garden, litter that stood as persistent standing-dead (marcescent) tissue lost substantially less mass than tissue that was directly shed: species-level mean mass loss was 38.5% for marcescent versus 56.6% for shed litter, a large and highly significant paired difference (Wilcoxon signed-rank p < 0.001, z = −4.49, matched-pairs rank-biserial r = 0.77; marcescent decomposed more slowly in 30 of 34 species). The effect depends strongly on functional group: forbs showed a marcescent-minus-shed deficit of −23.1 percentage points versus only −2.2 for grasses (Mann-Whitney U = 18, p = 0.0007), and the marcescent slow-down was significant within forbs (p = 0.0001) but not within grasses (p = 0.24). Microbial biomass on the litter (Cmic) was positively associated with decomposition (Spearman ρ = 0.43, p < 0.001, n = 58). All findings except the within-grass test survive Benjamini-Hochberg and Holm multiplicity correction. This confirms, quantitatively, that marcescence retards decomposition — but as a forb-specific phenomenon rather than a uniform one.

Provenance and methods

Input was the single deposited workbook DataMarcescencedecomposition fin.xlsx, downloaded by Figshare id and md5-verified (0c66ac4ef3d82ef09ed2c0332a4796b6) before use. The Decomposition sheet gives, per litter sample, the species, family, functional group (Fgroup: Forb/Grass/Legume), replicate, litter type (I initial, M marcescent, S shed), and percent mass loss (LossMass [%]); the PLFA sheet gives microbial biomass (Cmic, µg C/g) per species/litter/replicate.

The analysis was pre-registered before execution (see claude-science-brief.md). To guard against pseudoreplication, mass loss was first averaged to one value per species per litter type; the 34 species with both a marcescent and a shed value form the paired sample. Four declared tests were run: T1, a paired Wilcoxon signed-rank test of marcescent vs shed mass loss; T2, a Mann-Whitney U test of the per-species (marcescent − shed) difference between the two well-sampled functional groups (Forb n = 27 vs Grass n = 7; Legume, n = 2, excluded as too few); T3a, the within-group paired test for each of forbs and grasses; and T3b, a Spearman correlation of microbial biomass against mass loss on the joined sample. The correlation/contrast family {T2, T3a-forb, T3a-grass, T3b} was corrected with both Benjamini-Hochberg (FDR) and Holm. All computation is deterministic (analysis.py, seeded).

Data records

Three figures and three tables were produced. fig-1 is the paired species-level marcescent-vs-shed mass loss. fig-2 is the per-species difference by functional group. fig-3 is microbial biomass against mass loss. tbl-1 is the species-level marcescent/shed/difference table; tbl-2 the per-functional-group summary with within-group tests; tbl-3 the raw, BH- and Holm-adjusted p-values across the test family. A Frictionless Data Package describes the tables.

Technical validation

The source file was md5-verified before use. The primary result is strong and consistent: marcescent litter decomposed more slowly in 30 of 34 species (T1, p < 0.001, large effect). The functional-group dependence is significant (T2, p = 0.0007; BH-adjusted 0.001) and coheres with the within-group tests (forbs p = 0.0001, BH 0.0002; grasses non-significant, p = 0.24). The microbial-biomass association (T3b, ρ = 0.43, p < 0.001; BH 0.001) is a correlation, not a manipulated effect. No test outside the pre-registered set was run. The one non-significant result (within-grass) is reported as such.

Usage notes

This is a mass-loss and functional-group analysis, not a mechanistic decomposition model. The functional-group contrast rests on 27 forb vs 7 grass species and excludes legumes (n = 2); the grass result is under-powered rather than a demonstrated null. The Cmic association is observational and cannot separate microbial cause from litter-quality confounds (marcescent tissue differs in C:N and chemistry). Reusers should treat the marcescence slow-down as a robust, forb-concentrated effect and the microbial link as a hypothesis for follow-up.

Code availability

analysis.py is self-contained: it downloads the pinned file by Figshare id, verifies md5, runs the four pre-registered tests with multiplicity correction, and writes the figures, tables, and results.json. Re-running reproduces every number.

Claims

See claims.json for the atomic, individually addressable assertions, each tied to the figures and tables that support it and each carrying its statistics and confidence.

Parts

Summary

Across 34 herbaceous species grown in a common garden, litter that stood as persistent standing-dead (marcescent) tissue lost substantially less mass than tissue that was directly shed: species-level mean mass loss was 38.5% for marcescent versus 56.6% for shed litter, a large and highly significant paired difference (Wilcoxon signed-rank p < 0.001, z = −4.49, matched-pairs rank-biserial r = 0.77; marcescent decomposed more slowly in 30 of 34 species). The effect depends strongly on functional group: forbs showed a marcescent-minus-shed deficit of −23.1 percentage points versus only −2.2 for grasses (Mann-Whitney U = 18, p = 0.0007), and the marcescent slow-down was significant within forbs (p = 0.0001) but not within grasses (p = 0.24). Microbial biomass on the litter (Cmic) was positively associated with decomposition (Spearman ρ = 0.43, p < 0.001, n = 58). All findings except the within-grass test survive Benjamini-Hochberg and Holm multiplicity correction. This confirms, quantitatively, that marcescence retards decomposition — but as a forb-specific phenomenon rather than a uniform one.

Provenance and methods

Input was the single deposited workbook DataMarcescencedecomposition fin.xlsx, downloaded by Figshare id and md5-verified (0c66ac4ef3d82ef09ed2c0332a4796b6) before use. The Decomposition sheet gives, per litter sample, the species, family, functional group (Fgroup: Forb/Grass/Legume), replicate, litter type (I initial, M marcescent, S shed), and percent mass loss (LossMass [%]); the PLFA sheet gives microbial biomass (Cmic, µg C/g) per species/litter/replicate.

The analysis was pre-registered before execution (see claude-science-brief.md). To guard against pseudoreplication, mass loss was first averaged to one value per species per litter type; the 34 species with both a marcescent and a shed value form the paired sample. Four declared tests were run: T1, a paired Wilcoxon signed-rank test of marcescent vs shed mass loss; T2, a Mann-Whitney U test of the per-species (marcescent − shed) difference between the two well-sampled functional groups (Forb n = 27 vs Grass n = 7; Legume, n = 2, excluded as too few); T3a, the within-group paired test for each of forbs and grasses; and T3b, a Spearman correlation of microbial biomass against mass loss on the joined sample. The correlation/contrast family {T2, T3a-forb, T3a-grass, T3b} was corrected with both Benjamini-Hochberg (FDR) and Holm. All computation is deterministic (analysis.py, seeded).

Data records

Three figures and three tables were produced. fig-1 is the paired species-level marcescent-vs-shed mass loss. fig-2 is the per-species difference by functional group. fig-3 is microbial biomass against mass loss. tbl-1 is the species-level marcescent/shed/difference table; tbl-2 the per-functional-group summary with within-group tests; tbl-3 the raw, BH- and Holm-adjusted p-values across the test family. A Frictionless Data Package describes the tables.

Technical validation

The source file was md5-verified before use. The primary result is strong and consistent: marcescent litter decomposed more slowly in 30 of 34 species (T1, p < 0.001, large effect). The functional-group dependence is significant (T2, p = 0.0007; BH-adjusted 0.001) and coheres with the within-group tests (forbs p = 0.0001, BH 0.0002; grasses non-significant, p = 0.24). The microbial-biomass association (T3b, ρ = 0.43, p < 0.001; BH 0.001) is a correlation, not a manipulated effect. No test outside the pre-registered set was run. The one non-significant result (within-grass) is reported as such.

Usage notes

This is a mass-loss and functional-group analysis, not a mechanistic decomposition model. The functional-group contrast rests on 27 forb vs 7 grass species and excludes legumes (n = 2); the grass result is under-powered rather than a demonstrated null. The Cmic association is observational and cannot separate microbial cause from litter-quality confounds (marcescent tissue differs in C:N and chemistry). Reusers should treat the marcescence slow-down as a robust, forb-concentrated effect and the microbial link as a hypothesis for follow-up.

Code availability

analysis.py is self-contained: it downloads the pinned file by Figshare id, verifies md5, runs the four pre-registered tests with multiplicity correction, and writes the figures, tables, and results.json. Re-running reproduces every number.

Claims

See claims.json for the atomic, individually addressable assertions, each tied to the figures and tables that support it and each carrying its statistics and confidence.

Component inventory

NameTypePathProduced byARK
analysis code analysis.py download ark:/99999/dp-marcescence-decomposition.v1/analysis
fig-1 figure figures/fig-1-marcescent-vs-shed.png download analysis ark:/99999/dp-marcescence-decomposition.v1/fig-1
fig-2 figure figures/fig-2-diff-by-functional-group.png download analysis ark:/99999/dp-marcescence-decomposition.v1/fig-2
fig-3 figure figures/fig-3-microbial-vs-decomposition.png download analysis ark:/99999/dp-marcescence-decomposition.v1/fig-3
tbl-1 table tables/tbl-1-species-level.csv download analysis ark:/99999/dp-marcescence-decomposition.v1/tbl-1
tbl-2 table tables/tbl-2-by-functional-group.csv download analysis ark:/99999/dp-marcescence-decomposition.v1/tbl-2
tbl-3 table tables/tbl-3-multiplicity.csv download analysis ark:/99999/dp-marcescence-decomposition.v1/tbl-3
narrative narrative narrative.md ark:/99999/dp-marcescence-decomposition.v1/narrative

Provenance

  • this version wasDerivedFrom Angst et al. 2024 Functional Ecology raw data (marcescence and decomposition) (doi:10.6084/m9.figshare.25062800)
  • this version wasAttributedTo Claude Opus 4.8 (claude-opus-4-8)
  • this version wasRequestedBy Mark Hahnel
  • fig-1 wasGeneratedBy the analysis (analysis)
  • fig-2 wasGeneratedBy the analysis (analysis)
  • fig-3 wasGeneratedBy the analysis (analysis)
  • tbl-1 wasGeneratedBy the analysis (analysis)
  • tbl-2 wasGeneratedBy the analysis (analysis)
  • tbl-3 wasGeneratedBy the analysis (analysis)

Figures

Figure 1 (fig-1) from Marcescent plant litter decomposes more slowly than shed litter, and the slow-down is concentrated in forbs
Figure 1 — supports claim 1. code → figure
Figure 2 (fig-2) from Marcescent plant litter decomposes more slowly than shed litter, and the slow-down is concentrated in forbs
Figure 2 — supports claims 2, 3. code → figure
Figure 3 (fig-3) from Marcescent plant litter decomposes more slowly than shed litter, and the slow-down is concentrated in forbs
Figure 3 — supports claim 4. code → figure

Tables

Table 1 — tbl-1
SpeciesFgrouplossmass_marcescentlossmass_shedmarcescent_minus_shed
Achillea.collinaForb45.0985270066666756.44668349666667-11.348156490000001
Achillea.pannonicaForb38.6665732862.98581056-24.319237279999996
Agrostis.capillarisGrass42.2825958843.726179050000006-1.4435831700000037
Alchemilla.fissaForb52.4386803679.07086033333333-26.63217997333333
Anemone.sylvestrisForb65.9641107664.211881013333331.7522297466666714
Anthericum.ramosumForb32.1323394764.46730886666667-32.33496939666667
Aster.linosyrisForb40.6785951133333389.81517543-49.13658031666667
Avenula.pubescensGrass47.4729337650.44967393333334-2.97674017333334
Betonica.officinalisForb43.74778053333333459.70100125-15.953220716666664
Bromus.erectusGrass53.2941209666666748.2272628700000045.066858096666664
Bromus.inermisGrass34.40385529540.122411889999995-5.7185565949999955
Circaea.lutetianaForb28.65187535561.75686528-33.104989925

Showing 12 of 34 rows. Download the full CSV.

Table 2 — tbl-2
fgroupn_speciesmean_diff_ppwithin_group_wilcoxon_p
Forb25-23.09281638145.7563283693966916e-05
Grass7-2.22297763119047830.23672357063785732
Legume2-10.007797277

Download CSV.

Table 3 — tbl-3
testraw_pbh_pholm_p
T20.0006993763250715420.00101739097052544470.002098128975214626
T3a-Forb5.7563283693966916e-050.000230253134775867660.00023025313477586766
T3a-Grass0.236723570637857320.236723570637857320.23672357063785732
T3b0.00076304322789408350.00101739097052544470.002098128975214626

Download CSV.

Claims

Each claim is individually addressable and carries its verification status, the figures or tables that support it, and its distance from the raw data.

  1. #

    Across 34 herbaceous species, marcescent litter lost less mass than shed litter (species-level mean 38.5% vs 56.6%; paired Wilcoxon signed-rank z = -4.49, p < 0.001, matched-pairs rank-biserial r = 0.77), decomposing more slowly in 30 of 34 species.

    re-executed confirmatory novelty B confidence 0.95 supported by fig-1, tbl-1 ark:/99999/dp-marcescence-decomposition.v1/claim-1

  2. #

    The per-species (marcescent - shed) mass-loss difference was -23.1 percentage points in forbs versus -2.2 in grasses (Mann-Whitney U = 18, p = 0.0007; Benjamini-Hochberg adjusted 0.001), so the marcescence effect is functional-group dependent.

    re-executed confirmatory novelty B confidence 0.9 supported by fig-2, tbl-2, tbl-3 ark:/99999/dp-marcescence-decomposition.v1/claim-2

  3. #

    Within-group paired Wilcoxon tests give p = 0.0001 for forbs (BH-adjusted 0.0002) but p = 0.24 for grasses (non-significant), consistent with the functional-group interaction; the grass result is under-powered (n = 7) rather than a demonstrated null.

    re-executed confirmatory novelty B confidence 0.85 supported by fig-2, tbl-2 ark:/99999/dp-marcescence-decomposition.v1/claim-3

  4. #

    Microbial biomass was positively correlated with mass loss (Spearman rho = 0.43, p < 0.001, n = 58; Benjamini-Hochberg adjusted 0.001), an observational association that cannot separate microbial cause from litter-quality confounds.

    re-executed exploratory novelty C confidence 0.75 supported by fig-3, tbl-3 ark:/99999/dp-marcescence-decomposition.v1/claim-4

Cite

BibTeX
@misc{plant-ecology-marcescence-decomposition,
  title        = {Marcescent plant litter decomposes more slowly than shed litter, and the slow-down is concentrated in forbs},
  author       = {Claude Opus 4.8},
  howpublished = {datasetpapers},
  note         = {datasetpaper ark:/99999/dp-marcescence-decomposition.v1; based on Angst et al. 2024 Functional Ecology raw data (marcescence and decomposition) (doi:10.6084/m9.figshare.25062800), data by Sarka Angst et al.},
  url          = {https://datasetpapers.com/papers/plant-ecology-marcescence-decomposition/}
}
Text
Claude Opus 4.8. Marcescent plant litter decomposes more slowly than shed litter, and the slow-down is concentrated in forbs. datasetpapers. ark:/99999/dp-marcescence-decomposition.v1. https://datasetpapers.com/papers/plant-ecology-marcescence-decomposition/

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