Calculation of diversification indicators and other covariates
Summary
Indicators
| Indicator | Data | Format |
|---|---|---|
| perimeter and area of the field | RPG+ | vectoriel |
| mean field size within buffer | RPG+ | vectoriel |
| crop rotation (N-4:N) | RPG+ | vectoriel |
| hedgerows around field | RPG+ & BD Haie Liu 2023 |
vectoriel raster 30m |
| % land cover within buffer | RPG+ & CLCplus | raster 10m |
| edge density | Not available | NA |
Datasets
Registre Parcellaire Graphique (RPG): annual field crop data for the period 2015-2024 available for France on IGN website: https://cartes.gouv.fr/rechercher-une-donnee/dataset/IGNF_RPG. The dataset differentiates 366 crop categories
Geodienste - nutzungsflaechen (Nutzung): Swiss equivalent of the RPG with annual field crop data for the period 2020-2025: https://geodienste.ch/services/lwb_nutzungsflaechen. The data is not entirely open yet but raw data were provided by Selma Cadot. The dataset differentiates 146 categories including hedgerows and semi-natural habitat.
Corine Land Cover plus (CLCplus): land use land cover at European scale with 10m resolution and 11 basic land cover classes, available on Corine Land Monitoring Service https://land.copernicus.eu/en/products/clc-backbone. The data is availble for 2018, 2021 and 2023.
Liu et al. (2023): European tree cover and biomass map at 30m resolution for Europe https://zenodo.org/records/8154445 derived from 3m resolution PlanetScope imagery of 2019.
BD Haie v2 (6.8Gb): hedgerows dataset for France available on the IGN website: https://geoservices.ign.fr/bdhaie. BD Haie v2 was produced from satellite images of 2020-2022.
Land cover class harmonization: list all classes from RPG, Nutzung and CLCplus and how to harmonize them. This file has been completed during WS3 and can be further customized for the project objectives. It groups all crops and land cover classes into 57 groups.
Orchards and vineyards from individual projects to further complete the agricultural land use for perenial crops in France.
Field observations
| 2014 | 2015 | 2016 | 2017 | 2018 | 2019 | 2020 | 2021 | 2022 | 2023 | 2024 | 2025 | TOTAL | |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Agrim2019 | 0 | 0 | 0 | 0 | 0 | 40 | 0 | 0 | 0 | 0 | 0 | 0 | 40 |
| BACCHUS_OPERA | 0 | 0 | 0 | 0 | 40 | 38 | 40 | 40 | 38 | 38 | 38 | 0 | 272 |
| BIOMHE | 0 | 0 | 0 | 0 | 0 | 0 | 40 | 0 | 0 | 0 | 0 | 0 | 40 |
| BISCO | 0 | 0 | 0 | 27 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 27 |
| DIVAG | 0 | 0 | 0 | 0 | 0 | 40 | 0 | 0 | 0 | 0 | 0 | 0 | 40 |
| DURUM_MIX_GM | 0 | 0 | 0 | 0 | 226 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 226 |
| EXCLU_BVD | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 7 | 12 | 16 | 0 | 0 | 35 |
| FRAMEwork_BVD | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 36 | 0 | 0 | 0 | 0 | 36 |
| Herrera2026 | 0 | 0 | 0 | 0 | 0 | 0 | 30 | 35 | 40 | 0 | 0 | 0 | 105 |
| lepibats | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 33 | 0 | 0 | 0 | 0 | 33 |
| muesli | 0 | 0 | 29 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 29 |
| OSCAR | 0 | 0 | 0 | 0 | 21 | 44 | 50 | 80 | 100 | 102 | 115 | 0 | 512 |
| PestiRed | 0 | 0 | 0 | 0 | 0 | 0 | 76 | 60 | 62 | 79 | 62 | 70 | 409 |
| Pigot2023 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 156 | 144 | 0 | 0 | 0 | 300 |
| SEBIOPAG_BVD | 0 | 0 | 0 | 0 | 0 | 0 | 20 | 21 | 20 | 0 | 0 | 0 | 61 |
| SEBIOPAG_Plaine de Dijon | 20 | 20 | 20 | 20 | 20 | 20 | 20 | 20 | 20 | 20 | 20 | 0 | 220 |
| SEBIOPAG_VcG | 20 | 19 | 17 | 17 | 17 | 17 | 17 | 17 | 17 | 17 | 0 | 0 | 175 |
| SEBIOPAG_ZAAr | 0 | 0 | 0 | 0 | 20 | 0 | 0 | 17 | 0 | 16 | 0 | 0 | 53 |
| Seree2022 | 0 | 0 | 0 | 0 | 0 | 14 | 19 | 0 | 0 | 0 | 0 | 0 | 33 |
| SERIPAGE | 0 | 0 | 9 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 0 | 9 |
| TOTAL | 40 | 39 | 75 | 64 | 344 | 213 | 312 | 522 | 453 | 288 | 235 | 70 | 2655 |
More detailled overview of the field observations can be found here
Identification of the crop field
Because of data availability, we will only focus on the observations made in the period 2015-2025 with field coordinates. The project DURUM_MIX_GM has a single coordinate leading to the entrance of the Institut Agro-Montpellier, without registered crop field within 1000m from the coordinates so it was excluded.
We identified the crop field from RPG or Nutzung dataset based on the coordinates and the year of the sampling.
| Nobs | in_RPG | in_VineOrchard | Perc | |
|---|---|---|---|---|
| Agrim2019 | 40 | 40 | 0 | 100.00 |
| BACCHUS_OPERA | 272 | 1 | 268 | 98.90 |
| BIOMHE | 40 | 39 | 0 | 97.50 |
| BISCO | 27 | 26 | 0 | 96.30 |
| DIVAG | 40 | 40 | 0 | 100.00 |
| EXCLU_BVD | 35 | 0 | 35 | 100.00 |
| FRAMEwork_BVD | 36 | 0 | 36 | 100.00 |
| Herrera2026 | 105 | 94 | 0 | 89.52 |
| lepibats | 33 | 30 | 0 | 90.91 |
| muesli | 29 | 29 | 0 | 100.00 |
| OSCAR | 512 | 448 | 11 | 89.65 |
| PestiRed | 339 | 303 | 0 | 89.38 |
| Pigot2023 | 300 | 299 | 0 | 99.67 |
| SEBIOPAG_BVD | 61 | 0 | 61 | 100.00 |
| SEBIOPAG_Plaine de Dijon | 200 | 200 | 0 | 100.00 |
| SEBIOPAG_VcG | 155 | 152 | 0 | 98.06 |
| SEBIOPAG_ZAAr | 53 | 53 | 0 | 100.00 |
| Seree2022 | 33 | 30 | 0 | 90.91 |
| SERIPAGE | 9 | 9 | 0 | 100.00 |
Remarks:
- In total,
95% of the fields observations (N=2204) are covered with information on crop field.
- It is important to acknowledge that
RPGis incomplete but the vineyards and orchards provided by data providers helps characterizing projects with permanent crops.
Field size
We calculated the area and the perimeter of the crop fields corresponding to the samplings.
| Min. | 1st Qu. | Median | Mean | 3rd Qu. | Max. | |
|---|---|---|---|---|---|---|
| Agrim2019 | 0.97 | 2.21 | 3.02 | 3.80 | 4.99 | 10.21 |
| BACCHUS_OPERA | 0.23 | 0.58 | 0.78 | 1.07 | 1.40 | 3.15 |
| BIOMHE | 0.68 | 1.59 | 3.69 | 4.48 | 6.29 | 13.99 |
| BISCO | 0.50 | 1.10 | 1.71 | 3.22 | 3.15 | 23.69 |
| DIVAG | 0.97 | 2.21 | 2.98 | 3.17 | 4.02 | 6.01 |
| EXCLU_BVD | 0.45 | 0.58 | 0.72 | 0.94 | 1.29 | 2.20 |
| FRAMEwork_BVD | 0.29 | 0.58 | 0.84 | 1.25 | 1.77 | 3.28 |
| Herrera2026 | 0.87 | 4.58 | 7.88 | 8.76 | 11.91 | 37.52 |
| lepibats | 1.40 | 2.77 | 6.18 | 11.89 | 13.96 | 55.47 |
| muesli | 0.41 | 1.90 | 3.84 | 5.46 | 7.61 | 34.05 |
| OSCAR | 0.22 | 0.48 | 1.00 | 1.71 | 1.70 | 21.35 |
| PestiRed | 0.10 | 0.97 | 1.06 | 1.32 | 1.40 | 5.19 |
| Pigot2023 | 2.40 | 7.93 | 10.46 | 12.87 | 17.05 | 44.15 |
| SEBIOPAG_BVD | 0.29 | 0.60 | 0.87 | 1.37 | 1.77 | 5.68 |
| SEBIOPAG_Plaine de Dijon | 0.53 | 5.11 | 6.83 | 7.46 | 8.92 | 17.82 |
| SEBIOPAG_VcG | 0.85 | 2.90 | 4.27 | 5.56 | 7.00 | 24.06 |
| SEBIOPAG_ZAAr | 1.21 | 3.16 | 4.73 | 4.96 | 6.94 | 16.22 |
| Seree2022 | 0.90 | 2.60 | 4.81 | 9.17 | 12.85 | 37.52 |
| SERIPAGE | 1.55 | 2.19 | 3.51 | 4.04 | 5.19 | 7.60 |
| Min. | 1st Qu. | Median | Mean | 3rd Qu. | Max. | |
|---|---|---|---|---|---|---|
| Agrim2019 | 485.39 | 691.18 | 797.06 | 889.45 | 1053.13 | 1674.45 |
| BACCHUS_OPERA | 214.18 | 330.40 | 398.22 | 449.45 | 552.24 | 1157.85 |
| BIOMHE | 354.03 | 592.12 | 835.73 | 907.71 | 1072.08 | 1807.17 |
| BISCO | 307.54 | 503.97 | 593.59 | 743.08 | 846.90 | 2550.45 |
| DIVAG | 485.39 | 654.90 | 799.78 | 816.22 | 937.89 | 1275.08 |
| EXCLU_BVD | 269.15 | 324.13 | 459.31 | 452.72 | 550.25 | 669.28 |
| FRAMEwork_BVD | 247.58 | 445.90 | 509.95 | 523.05 | 602.94 | 938.87 |
| Herrera2026 | 527.24 | 1056.08 | 1423.60 | 1450.42 | 1727.66 | 5991.28 |
| lepibats | 488.44 | 824.10 | 1260.50 | 1789.15 | 2670.28 | 6828.99 |
| muesli | 257.24 | 608.61 | 939.47 | 1060.52 | 1338.17 | 4021.15 |
| OSCAR | 200.02 | 358.30 | 493.46 | 583.72 | 749.38 | 2728.54 |
| PestiRed | 278.44 | 454.92 | 513.90 | 551.14 | 611.12 | 1126.50 |
| Pigot2023 | 707.30 | 1381.42 | 1616.08 | 1735.90 | 2089.44 | 4574.97 |
| SEBIOPAG_BVD | 247.58 | 366.24 | 500.45 | 525.22 | 643.19 | 984.37 |
| SEBIOPAG_Plaine de Dijon | 393.53 | 1075.19 | 1240.09 | 1297.87 | 1558.72 | 2220.91 |
| SEBIOPAG_VcG | 377.85 | 815.28 | 1171.63 | 1202.13 | 1505.30 | 4249.39 |
| SEBIOPAG_ZAAr | 451.97 | 793.52 | 949.02 | 1061.93 | 1207.41 | 3466.03 |
| Seree2022 | 378.99 | 778.39 | 1272.30 | 1482.71 | 2076.89 | 5991.28 |
| SERIPAGE | 494.30 | 750.53 | 776.57 | 928.22 | 1227.43 | 1466.38 |
There is a strong relation between area and perimeter (Figure 5). In median, field size is 2.1 ha and field perimeter is 703m.
Outliers
Remarks:
The overall pattern of field size per projects matches the expectations. Project focussing on wineyards (e.g. Bacchus, OSCAR), orchards (in BVD - Basse Vallée de la Durance) have smaller fields than average; while project focusing on large cereals (e.g. muesli, Plaine de Dijon) have larger fields.
Yet, when looking for outliers, we can see that:
Field size within buffer
Using the coordinates of the sampling sites, we calculated the average area of all crop fields within a buffer (500m and 1000m).
| B_500m | B_1000m | |
|---|---|---|
| Min. | 0.02 | 0.16 |
| 1st Qu. | 0.73 | 0.72 |
| Median | 1.29 | 1.19 |
| Mean | 2.39 | 1.97 |
| 3rd Qu. | 2.94 | 2.37 |
| Max. | 21.98 | 16.35 |
| NA’s | 2.00 | 1.00 |
We see that some observations don’t have crop field within 500m (N=2 in Table 5). These observations (listed in Table 6) would need to be checked and ensure that they are close to agricultural lands.
| Study_ID | Plot_ID | Year | |
|---|---|---|---|
| 181 | OSCAR | 33_2011_00002 | 2018 |
| 481 | OSCAR | 11_2023_00004 | 2023 |
Outliers
Remarks:
- The field size within buffer is a good proxy for agricultural practices at landscape level.
- The values with a buffer of 500m and 1km are highly correlated (r =
0.86). Yet values with a buffer of 1km are slightly less extreme (higher minimum and lower maximum).
Crop rotation (N-4:N)
| 0 | 1 | 2 | 3 | 4 | 5 | |
|---|---|---|---|---|---|---|
| Agrim2019 | 0 | 0 | 0 | 0 | 1 | 39 |
| BACCHUS_OPERA | 1 | 0 | 0 | 1 | 2 | 268 |
| BIOMHE | 1 | 0 | 1 | 0 | 0 | 38 |
| BISCO | 1 | 0 | 0 | 26 | 0 | 0 |
| DIVAG | 0 | 0 | 0 | 0 | 0 | 40 |
| EXCLU_BVD | 0 | 0 | 0 | 0 | 0 | 35 |
| FRAMEwork_BVD | 0 | 0 | 0 | 0 | 0 | 36 |
| Herrera2026 | 9 | 0 | 0 | 0 | 2 | 94 |
| lepibats | 2 | 1 | 4 | 0 | 3 | 23 |
| muesli | 0 | 0 | 29 | 0 | 0 | 0 |
| OSCAR | 34 | 1 | 26 | 36 | 79 | 336 |
| PestiRed | 1 | 2 | 7 | 38 | 144 | 147 |
| Pigot2023 | 1 | 0 | 0 | 0 | 0 | 299 |
| SEBIOPAG_BVD | 0 | 0 | 0 | 0 | 0 | 61 |
| SEBIOPAG_Plaine de Dijon | 0 | 20 | 20 | 20 | 20 | 120 |
| SEBIOPAG_VcG | 1 | 18 | 17 | 17 | 19 | 83 |
| SEBIOPAG_ZAAr | 0 | 0 | 0 | 0 | 20 | 33 |
| Seree2022 | 3 | 0 | 0 | 0 | 0 | 30 |
| SERIPAGE | 0 | 0 | 9 | 0 | 0 | 0 |
The number of observations in the period N-4:N in Table 7 is a results of the number of observations per year (Table 1). Most observations have 5 years of data on crop rotation (73%, N=1682).
Let’s zoom on the crop rotations over the 5-year period (i.e. excluding observations with incomplete crop rotation data).
From the 1682 observations with complete crop rotation information in [N-4:N], 535 have the same crop for the whole time period, while 112 fields have five different crop groups in the past 5 years (Figure 16).
| Var1 | Freq |
|---|---|
| vignes | 488 |
| vergers | 132 |
| ble_tendre_hiver,colza_hiver,orge_hiver | 75 |
| divers,vignes | 26 |
| gel_sans_prod,vignes | 24 |
| ble_tendre_hiver,prairies_temporaires | 17 |
| ble_tendre_hiver,colza_hiver,proteagineux | 16 |
| ble_tendre_hiver,mais_ensilage | 14 |
| ble_tendre_hiver,colza_hiver,orge_hiver,proteagineux | 13 |
| ble_tendre_hiver,colza_hiver,lin_non_textile,proteagineux | 12 |
| ble_tendre_hiver,colza_hiver,orge_printemps,proteagineux | 12 |
| autres_cult_indus,ble_tendre_hiver,orge_hiver | 11 |
| ble_tendre_hiver,mais_grain_semence | 10 |
| mais_grain_semence,vignes | 10 |
| ble_dur_hiver,colza_hiver | 9 |
| ble_dur_hiver,ble_tendre_hiver,colza_hiver,orge_printemps | 8 |
| ble_tendre_hiver,colza_hiver,mais_ensilage,orge_hiver | 8 |
| autres_cult_indus,ble_tendre_hiver,mais_grain_semence,orge_hiver | 7 |
| ble_dur_hiver,ble_tendre_hiver,tournesol | 7 |
| ble_tendre_hiver,colza_hiver,fourrage_fabacees | 7 |
Remarks:
- The level of crop rotation depends strongly on the project targeting either annual vs perrenial cropping systems.
- In France, the spatial dataset about orchard and wineyards was set as constant during the study period, which artificially ignores any changes in agricultural practices in these perrenial systems. So crop rotation information must be ignored for the perrenial crops in France.
Hedgerows length
We overlaid the field as defined in RPG+ (+ a 10m buffer) with the tree cover density from Liu et al. 2023 and with other national information on hedgerows (BD Haie and Nutzung).
| Liu | National | |
|---|---|---|
| Agrim2019 | 100.00 | 100.00 |
| BACCHUS_OPERA | 40.07 | 26.10 |
| BIOMHE | 92.50 | 97.50 |
| BISCO | 96.30 | 96.30 |
| DIVAG | 92.50 | 95.00 |
| EXCLU_BVD | 100.00 | 100.00 |
| FRAMEwork_BVD | 100.00 | 100.00 |
| Herrera2026 | 51.43 | 49.52 |
| lepibats | 54.55 | 48.48 |
| muesli | 100.00 | 96.55 |
| OSCAR | 58.01 | 47.07 |
| PestiRed | 45.72 | 7.67 |
| Pigot2023 | 29.00 | 38.00 |
| SEBIOPAG_BVD | 100.00 | 100.00 |
| SEBIOPAG_Plaine de Dijon | 54.50 | 39.50 |
| SEBIOPAG_VcG | 89.03 | 98.06 |
| SEBIOPAG_ZAAr | 94.34 | 100.00 |
| Seree2022 | 24.24 | 45.45 |
| SERIPAGE | 100.00 | 100.00 |
Outliers
Remarks:
- There is a relatively good correlation among the percentage of hedgerows cover in Liu_2023 dataset and the national dataset (r=
0.66for France, and0.46for Switzerland).
- Liu et al. 2023 might consider orchards as hedgerow as seen for the BVD projects in Figure 21.
- In Switzerland, the percentage of fields with hedgerows is extremely low (
7.67%, Table 9) while the values are not so different when considering Liu_2023. This observation seems to indicate a difference in how hedgerows were defined in France and in Switzerland and would suggest the use of Liu_2023 when comparing both datasets.
Land cover within buffer
| n_classes | av_perc_rpg | |
|---|---|---|
| Agrim2019 | 36 | 76.36 |
| BACCHUS_OPERA | 32 | 70.18 |
| BIOMHE | 40 | 71.01 |
| BISCO | 30 | 70.56 |
| DIVAG | 38 | 74.85 |
| EXCLU_BVD | 39 | 48.25 |
| FRAMEwork_BVD | 38 | 44.08 |
| Herrera2026 | 51 | 77.05 |
| lepibats | 36 | 52.21 |
| muesli | 36 | 73.81 |
| OSCAR | 51 | 61.48 |
| PestiRed | 40 | 56.05 |
| Pigot2023 | 47 | 78.15 |
| SEBIOPAG_BVD | 42 | 47.28 |
| SEBIOPAG_Plaine de Dijon | 44 | 68.43 |
| SEBIOPAG_VcG | 44 | 75.48 |
| SEBIOPAG_ZAAr | 45 | 73.34 |
| Seree2022 | 42 | 76.67 |
| SERIPAGE | 28 | 76.63 |
After grouping, there are 54 different categories covered by the 1000m buffers .
forest vignes ble_tendre_hiver
15.51 14.96 10.43
permanent.herbaceous prairies_permanentes sealed
9.38 5.63 5.45
colza_hiver prairies_temporaires low.growing.woody.plants
3.48 3.46 3.27
orge_hiver
3.10
In average, 67 % of the buffer areas are filled with land cover classes from RPG+ (Table 10). The remaining 33% are filled with CLCplus classes, especially forest (15.5%), permanent harbaceous (9.4%) and sealed (5.4%) (Table 11).
| Min. | 1st Qu. | Median | Mean | 3rd Qu. | Max. | |
|---|---|---|---|---|---|---|
| Agrim2019 | 2.02 | 2.27 | 2.33 | 2.34 | 2.41 | 2.63 |
| BACCHUS_OPERA | 0.56 | 1.07 | 1.16 | 1.15 | 1.32 | 1.73 |
| BIOMHE | 2.07 | 2.28 | 2.35 | 2.35 | 2.44 | 2.61 |
| BISCO | 1.99 | 2.12 | 2.21 | 2.19 | 2.27 | 2.35 |
| DIVAG | 2.22 | 2.30 | 2.36 | 2.39 | 2.48 | 2.63 |
| EXCLU_BVD | 1.14 | 1.50 | 1.66 | 1.69 | 1.84 | 2.24 |
| FRAMEwork_BVD | 1.27 | 1.70 | 1.87 | 1.84 | 1.99 | 2.16 |
| Herrera2026 | 1.25 | 2.09 | 2.32 | 2.28 | 2.49 | 2.83 |
| lepibats | 1.10 | 1.54 | 1.88 | 1.78 | 2.05 | 2.35 |
| muesli | 1.76 | 2.22 | 2.30 | 2.27 | 2.39 | 2.62 |
| OSCAR | 0.96 | 1.42 | 1.74 | 1.75 | 2.02 | 2.84 |
| PestiRed | 1.14 | 2.04 | 2.31 | 2.22 | 2.51 | 2.84 |
| Pigot2023 | 1.29 | 1.98 | 2.09 | 2.14 | 2.30 | 2.85 |
| SEBIOPAG_BVD | 1.23 | 1.74 | 1.87 | 1.87 | 2.00 | 2.25 |
| SEBIOPAG_Plaine de Dijon | 1.02 | 1.99 | 2.21 | 2.13 | 2.34 | 2.78 |
| SEBIOPAG_VcG | 1.86 | 2.25 | 2.37 | 2.35 | 2.45 | 2.66 |
| SEBIOPAG_ZAAr | 1.97 | 2.24 | 2.34 | 2.34 | 2.45 | 2.70 |
| Seree2022 | 1.73 | 1.96 | 2.14 | 2.17 | 2.33 | 2.71 |
| SERIPAGE | 1.88 | 2.16 | 2.18 | 2.13 | 2.19 | 2.28 |
Remarks:
- All buffers include some amount of forest (5-20%) and sealed area (5-10%), while the crop composition is highly project specific with project with perrenial crops (Bacchus, BVD, Oscar) being less diverse than project focussing on annual crops.
Correlation
Remarks:
- There is a high positive correlation between field size and the median field size within buffer : the size of the field is related to the average field size in the landscape.
- There is a high positive correlation between spatial and temporal crop diversity (land cover within a buffer and crop rotation).
- Landscape with high percentage of vineyards have low diversity of landscape and low crop rotation. On the contrary, landscape with high percentage of wheat have larger field size, and higher diversity of crop spatially and temporally. This observation might be bias by the high number of crop groups compare to other classes of land cover considered.
Summary
Material and method
To characterize the cropping practices, we used the Registre Parcellaire Graphique (RPG) for France and the Geodienste - nutzungsflaechen (Nutzung) for Switzerland. The two datasets are vectorial spatial data that provide the crop field boundaries and categorize the crops into refined categories: 366 crops are considered in France, and 146 in Swizerland. RPG is available annually since 2015 while Nutzung is available since 2019. Because RPG is known to lack data for small wineyards and orchards (ref needed?), we complemented the crop data with local dataset for the samples made in regions dominated by permanent crops.
We intersected the sampling coordinates with the national crop dataset corresponding to the sampling year and extracted the perimeter and the area of the fields. Additionnally, we calculated the mean field size within a buffer of 1km around the sampling position. When available, we exctracted information about the cropping patterns for the 4 years before sampling.
We complemented the crop dataset with the land use land cover data from Corine Land Cover plus (CLCplus). It caracterize the land cover into 11 classes. The dataset is available for Europe with a spatial resolution of 10 m. There has been three release: 2018, 2021, and 2023. We filled the holes of the national crop dataset with the CLCplus information closest to the year of sampling. Then, we extracted the percentage of cover per buffer of 1km around the sampling location. We grouped the land cover and crop classes into 57 classes and calculated the Shannon index of the simplified land cover classes.
Hedgerow density was quantify from national datasets: BD Haies v2 for France in 2021 and Geodienste - nutzungsflaechen for Switzerland in 2023. or Hedgerow density was quantify using European dataset (Liu et al. 2023) providing estimates of the cover and the biomass of trees at 30m resolution for 2019. We extracted the length/area of hedgerows within the fieldw and a 10m buffer around them.
All analysis were performed in R 4.4.1() using terra() and exactextract() packages.
Results
In total, 95 % of the fields samplings are covered with information on crop field, and 73% of the samples (N=1682) have complete 5 years crop rotation data.
- Most observations have a corresponding crop field in RPG dataset or in complementary dataset (Table 2).
- All buffers include some amount of forest (5-20%) and sealed area (5-10%), while the crop composition is highly project specific.