Data from: Undersowing rare arable plants in cereals as a new instrument in weed management - restoration ecology meets weed science
Data files
Oct 30, 2025 version files 63.45 KB
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README.md
3.98 KB
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Undersowing_rare_arable_plants_raw_data.xlsx
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Abstract
Weed control is necessary in agriculture, but it is also known to be one of the main drivers of plant biodiversity loss in agricultural landscapes. Since biodiversity is essential for ecosystem service provision, new approaches in weed management are needed to simultaneously increase biodiversity and prevent yield losses due to weed competition. In this study, we investigated the establishment of undersowing cereals with rare arable plant (RAP) species, their weed suppression ability, and influence on spring barley yield. We collected data at the species level for RAP and weed coverage and their fluctuations during a three-year on-farm trial (Hirrlingen), supplemented by a second one-year on-farm trial (Bettenreute) to confirm the results, both located in Southwestern Germany. The experiments were set up as randomised complete block designs with four treatments consisting of a control (1), a topsoil translocation (4), and two treatments with seeded RAP species mixtures at two levels (low (2) vs. high (3) number of seeds). Main analyses were done using plant coverage data (assessed according to Braun-Blanquet and re-transformed according to van der Maarel (2007)), and yield data (spring barley; each location for one season) for both locations. Biomass was only analysed for Bettenreute.
Dataset DOI: 10.5061/dryad.9s4mw6mw6
Description of the data and file structure
We set up two trials as randomised complete block designs with four repetitions. The treatment plot size at Hirrlingen was 2 m x 5 m and, at Bettenreute, 1.35 m x 8 m, all with the longer side of the plots in sowing direction of the crop. To evaluate the growth behaviour of RAP as well as common weeds over the years, we used nondestructive vegetation surveys. In each growing season, we conducted a vegetation survey before crop harvest when RAP were in BBCH growth stages 55 – 75. For the vegetation surveys, we assessed whole treatment plots using the extended Braun-Blanquet cover-abundance scale (Wilmanns, 1998). Each species of segetal plants in each replicate of every treatment was assigned a Braun-Blanquet score. Later, we transformed the Braun-Blanquet scores into coverage (%) by using the median of the proposed percentage classes of each score for better applicability according to van der Maarel (2007). Crop cover was excluded in the surveys. To support the coverage data, we additionally conducted a biomass cut at Bettenreute one day after the vegetation survey for each RAP species, respectively, and jointly for all common weeds (in dry biomass g m -2). For the yield assessment at Hirrlingen in 2021 and at Bettenreute in 2023 we counted tillers of spring barley four times per plot randomly via sampling quadrats of 33 cm x 33 cm and number of grains per ear four times at five randomly chosen ears. To determine the thousand grain weight (TGW), we randomly cut 50 ears of barley four times per plot and threshed them with a laboratory thresher (Haldrup, Ilshofen, Germany). Then we counted the thousand grains for every repetition of every plot by seed counter (Pfeuffer, Kitzingen, Germany), dried those for 24 h, and weighted each sample afterwards.
Yield predictions were calculated in t ha -1 according to equation (1):
yield = ((tillers x grains per ear x thousand grain weight)/1000)/100 (1)
Files and variables
File: Undersowing_rare_arable_plants_raw_data.xlsx
Description: Used raw data for the analysis of the Manuscript "Undersowing rare arable plants in cereals as a new instrument in weed management – restoration ecology meets weed science".
Sheets:
- Site_Year of the respective survey on rare arable plants (RAP)
- Replicate (Block 1 - 4)
- Treatment (1 = control, 2 = RAP sown in low densities, 3 = RAP sown in high densities, 4 = topsoil translocation)
- Plot number (not in order, just as the plots were layed out across the experimental sites)
- Total abundance arable plant (coverage of all plants except crop for the respective plot) / RAP coverage (coverage of all RAP for the respective plot, only at Bettenreute)
- Species / Species EPPO (Name and/or EPPO Code (https://gd.eppo.int/) of the assessed species)
- Abundance species in perc (% coverage of the respective species, according to Braun-Blanquet and back-transformed according to van der Maarel (2007))
- Yield -> including both sites with each one year of data
- Site (Hirrlingen or Bettenreute)
- Year (2021 for Hirrlingen, 2023 for Bettenreute)
- Treatment / Replicate (s.o.)
- Yield in t ha -1 ( Yield of spring barley)
- Biomass_ Bettenreute -> Only biomass data from this site 2023
- Biomass weed g m -2 (Bomass of all weed plants for the respective plot calculated in g m -2)
- Biomass RAP g m -2 (Biomass of all RAP plants for the respective plot calculated in g m -2)
- Biomass Species g m -2 (Biomass of all weed and RAP plants combined for the respective plot calculated in g m -2)
Code/software
Microsoft Excel is needed to view the data.
