Integrating Solar Energy into German Vineyards: A Geospatial Framework for Identifying Agrivoltaic Potential
Abstract
1. Introduction
2. Materials and Methods
2.1. The Study Area
2.2. The Methodological Framework
- Planted area: The analysis uses the cadastral vineyard area to assess agrivoltaic potential. This reflects current regulatory frameworks, which require that agricultural productivity (a minimum required yield per hectare) must be maintained for land to be recognized as ‘agrivoltaic’. Installing PV modules over the whole property area would compromise the agricultural function of the site and violate the intended crop-integrated character of agrivoltaic systems. ‘Planted area’ denotes the actively cultivated vineyard area within a cadastral plot.
- Slope: Vineyards in Germany are commonly classified according to their slope gradient [31]. German law distinguishes between hillside locations and flat sites. Steep-slope vineyards are defined as those with a slope of more than 30%. This classification is widely used in viticultural practice, as slope has direct implications for vineyard management, mechanization, microclimate, and, in this context, the technical feasibility of elevated agrivoltaic systems. Due to technical considerations, particularly the increasing construction complexity on steeper terrain, we differentiated vineyard plots by slope gradient into three classes: 0–5% (low), 5–15% (moderate), and >15% (high). Slopes above 15% typically entail significant additional construction effort and may require adapted mounting structures or specialized installation techniques [20].
- Plot size: Plot size influences both grid integration requirements and economic viability, as larger systems may benefit from economies of scale but place greater demands on infrastructure. Following the approach proposed by Rösch et al. (2025), systems are differentiated by a threshold of 2.5 hectares, as German building law allows simplified approval procedures for agrivoltaic installations below this size [20,21].
- Restricted area: As part of the spatial filtering process, areas designated under the Natura 2000 network were excluded from the analysis. Although viticulture exists within some Natura 2000 sites, the installation of agrivoltaic systems in these protected areas is highly unlikely due to regulatory restrictions and potential conflicts with conservation objectives [22]. Construction may be legally permitted in individual cases under building law. However, new agrivoltaic installations in these areas are excluded from public funding under the German Renewable Energy Sources Act (EEG), § 37 (3), further limiting their practical feasibility [32].
- Vine age: This parameter enables the identification of either young vineyards that may require adapted agrivoltaic designs, or older vineyards approaching the end of their productive lifecycle, which may be more compatible with structural retrofitting. To account for the age of the vineyard plots, the planting year was used to calculate the vine age as of the 2025 growing season. Based on viticultural lifecycle stages and practical decision-making horizons, vine age was grouped into five discrete classes: 0–5 years, 6–10 years, 11–15 years, 16–20 years, and more than 20 years. This categorization serves as a proxy and addresses an assessment of potential age-related constraints or opportunities for agrivoltaics implementation.
- Grape variety: Based on ongoing field trials, selected grape varieties can be filtered. For this study, the most common grape varieties in Germany are categorized into white and red grape varieties. Given the significant diversity of grape varieties cultivated in Germany, the 12 most commonly planted varieties were selected. In our framework, grape variety is treated as a descriptive variable that can be filtered to reflect the distribution of grape varieties. However, this does not imply any inference about varietal shade tolerance, which is beyond the scope of the present analysis.
3. Results
3.1. Integration of Grid Infrastructure Data
Distance to Grid Connection Point | Planted Area | Share of Total Planted Area (%) | Installable Capacity (GWp) |
---|---|---|---|
All | 54,078.0 | 100% | 37.85 |
≤1500 m grid distance | 37,964.7 | 70% | 24.68 |
≤1000 m grid distance | 24,031.5 | 44% | 15.62 |
≤750 m grid distance | 15,416.7 | 29% | 10.02 |
≤500 m grid distance | 7578.4 | 14% | 4.93 |
≤250 m grid distance | 2155.3 | 4% | 1.40 |
≤100 m grid distance | 405.1 | 1% | 0.26 |
3.2. Filtering by Agronomic Criteria
4. Discussion
4.1. Discussion of Results in Relation to Existing Research
4.2. Critical Reflection on Methodological Robustness
4.3. Practical Implications
4.4. Future Research Needs
5. Conclusions
Author Contributions
Funding
Data Availability Statement
Acknowledgments
Conflicts of Interest
Abbreviations
approx. | approximately |
BLE | Federal Office for Agriculture and Food |
BMLEH | Federal Ministry of Agriculture, Food, and Regional Identity |
GHI | global horizontal irradiation |
GWp | gigawatt peak |
Ha | hectare |
m | meter |
MCDA | multi-criteria decision-making analysis |
MWp | megawatt peak |
OAT | one-at-a-time |
PV | photovoltaics |
Appendix A
Appendix A.1
Appendix A.2
Appendix A.3
Appendix B
- Coordination of the reference system. All distance-based operations were carried out in a metric CRS (EPSG:25832, UTM 32N). Layers used for proximity calculations were projected to EPSG:25832 before the main analysis.
- Geometry validation (QA). The Rhineland-Palatinate (RLP) boundary (WFS vermkv:landesgrenze_rlp) and Natura 2000 polygons were checked for geometry validity using qgis:checkvalidity to avoid topology issues in downstream overlays.
- Study-area clipping of protected areas. Natura 2000 polygons were clipped to the RLP boundary (native:clip/native:intersection) to restrict protected-area geometries to the study area and to improve the efficiency of analytical runs.
- Consolidation of potential grid-access points. Power-grid point layers from powergrid_2024-11-25.gpkg (substation, switch, minor_distribution, distribution, connection, and generator_renewable filtered to source = ‘wind’) were unified through a multi-step native:union sequence to produce a single consolidated multipoint dataset.
- Reprojection of the consolidated grid dataset. The consolidated grid-access points were reprojected to EPSG:25832 (native:reprojectlayer) to ensure that all subsequent distance thresholds were interpreted in meters.
- Plot proximity classification. Aggregated vineyard plots were classified by distance to the consolidated grid-access points using native:selectwithindistance. Reported distance bands were 100 m, 500 m, and 1000 m (additional thresholds were explored for exploratory reasons only).
- Protected-area flagging/exclusion. Plots intersecting Natura 2000 (RLP-clipped) were identified with native:selectbylocation (predicates including intersects/within/touches) and were flagged or excluded for the main analysis and sensitivity checks.
Step | What Was Done | Input Data | Key Parameter | Output | Purpose |
---|---|---|---|---|---|
1 | Project setup and coordinate system | — | Target CRS for all distance operations: ETRS_1989_UTM_Zone_32N | Common metric coordinate basis | Ensures all buffers/proximity calculations are in meters (consistent, comparable distances). |
2 | Geometry validity check | Rhineland-Palatinate boundary (WFS vermkv:landesgrenze_rlp), Natura 2000 polygons (Natura2000_end2023.gpkg) | qgis:checkvalidity (default settings) | Valid (cleaned) geometries | Reduces topology errors and prevents failures in overlay/clip operations. |
3 | Clip Natura 2000 to study area | Natura 2000 polygons + RLP boundary | native:clip/native:intersection | Natura 2000 polygons restricted to RLP | Guarantees protected-area layers match the study extent; avoids cross-border artefacts. |
4 | Consolidate potential grid-access points | powergrid_2024-11-25.gpkg point layers: substation, switch, minor_distribution, distribution, connection, generator_renewable (filtered to source = ‘wind’) | Sequence of native:union operations | Consolidated multipoint dataset of potential grid-access locations | Unifies all relevant grid POIs into a single, robust candidate set for proximity analysis. |
5 | Reproject consolidated points to metric CRS | Consolidated grid-access points (from Step 4) | native:reprojectlayer: ETRS_1989_UTM_Zone_32N | Grid-access points in uniform projected system | Required so distance thresholds are interpreted in meters. |
6 | Classify vineyard plots by proximity to grid-access points | Vineyard plots (aggregated cadastral layer) + consolidated grid-access points | native:selectwithindistance; thresholds used in reporting: 100 m, 500 m, 1000 m | Selection per distance band | Produces the proximity classes cited in the main text (e.g., the 1 km figure). |
7 | Flag/exclude plots with protected-area overlap | Vineyard plots + Natura 2000 (RLP-clipped) | native:selectbylocation; predicates incl. intersects/within/touches | Plots flagged or excluded if intersecting Natura 2000 | Reflects ecological/regulatory constraints in the site selection and sensitivity analysis. |
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Parameter | Unit/Scale | Relevance | Data Source |
---|---|---|---|
Slope | % | Limits technical feasibility, affects machinery use | Cadastral data |
Plot size | ha | Total plot size, including landscape elements | Cadastral data |
Planted area | ha | Planted area that is used for viticulture | Cadastral data |
Grid connection proximity | Distance (m) | Determines connection cost and feasibility | Open Street Map (2024-11-25) |
Vine age | Year | Indicates replanting cycles and investment timing | Cadastral data |
Land use | Land use entry | Active viticultural management | Cadastral data |
Restricted area (Natura 2000) | ha | Excluded due to environmental protection | European Environment Agency |
Grape variety | Variety name | Determines shading tolerance and suitability | Cadastral data |
Solar irradiance (GHI) | kWh/m2/year | Indicates PV energy potential | Global Solar Atlas (2.12) |
Slope (%) | Planted Area (ha) |
---|---|
0–5% | 19,352.7 |
5–10% | 15,705.2 |
10–15% | 7874.3 |
15–20% | 3849.4 |
more than 20% | 6135.6 |
NA | 1160.8 |
Overall | 54,078.0 |
Slope (%) | Plot Size < 2.5 ha | Plot Size ≥ 2.5 ha | Total |
---|---|---|---|
0–5% | 19,235.99 | 116.7 | 19,352.7 |
5–10% | 15,652.3 | 52.9 | 15,705.2 |
10–15% | 7868.7 | 5.6 | 7874.3 |
15–20% | 3846.8 | 2.6 | 3849.4 |
more than 20% | 6113.2 | 22.4 | 6135.6 |
NA | 1153.1 | 7.7 | 1160.8 |
Total | 53,870.1 | 207.9 | 54,078.0 |
Grape Variety Category | Planted Area (ha) | Share of Total Planted Area (%) |
---|---|---|
White | 33,261.5 | 62% |
Red | 8451.6 | 16% |
Other | 12,364.9 | 23% |
Total | 54,078.0 | 100% |
Year Category | Planted Area (ha) | Share of Total Planted Area (%) |
---|---|---|
0–5 years | 7279.6 | 13% |
6–10 years | 6964.5 | 13% |
11–15 years | 6608.7 | 12% |
16–20 years | 6628.9 | 12% |
more than 20 years | 24,851.1 | 46% |
NA | 1755.3 | 3% |
Overall | 54,078.0 | 100% |
Scenario | Planted Area (ha) | Share of Total Area (%) | Installable Capacity (GWp) 1 |
---|---|---|---|
High Priority | 844.2 | 1.6% | 0.55 |
Balanced Feasibility | 4126.9 | 7.6% | 2.68 |
Extended Potential | 14,111.1 | 26.1% | 9.17 |
In-Field Integration | 792.4 | 1.5% | 0.52 |
Scenario | Planted Area (ha) | Installable Capacity (GWp, 0.65 Factor) | Capacity Range (GWp, ±15%) |
---|---|---|---|
Baseline | 5836.26 | 3.79 | 3.22–4.36 |
OAT—Age ≥ 10 years | 4126.92 | 2.68 | 2.28–3.08 |
OAT—Age ≥ 15 years | 3388.86 | 2.20 | 1.87–2.53 |
OAT—Grid ≤ 250 m | 1774.7 | 1.15 | 0.98–1.33 |
OAT—Grid ≤ 1000 m | 18,404.83 | 11.96 | 10.17–13.76 |
OAT—Variety (White) | 2796.71 | 1.82 | 1.55–2.09 |
High Priority | 844.2 | 0.55 | 0.47–0.63 |
Balanced Feasibility | 4126.9 | 2.68 | 2.28–3.08 |
Extended Potential | 14,111.1 | 9.17 | 7.80–10.55 |
In-Field Integration | 792.4 | 0.52 | 0.44–0.59 |
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Christ, M.; Wagner, M. Integrating Solar Energy into German Vineyards: A Geospatial Framework for Identifying Agrivoltaic Potential. Agronomy 2025, 15, 2174. https://doi.org/10.3390/agronomy15092174
Christ M, Wagner M. Integrating Solar Energy into German Vineyards: A Geospatial Framework for Identifying Agrivoltaic Potential. Agronomy. 2025; 15(9):2174. https://doi.org/10.3390/agronomy15092174
Chicago/Turabian StyleChrist, Marcel, and Moritz Wagner. 2025. "Integrating Solar Energy into German Vineyards: A Geospatial Framework for Identifying Agrivoltaic Potential" Agronomy 15, no. 9: 2174. https://doi.org/10.3390/agronomy15092174
APA StyleChrist, M., & Wagner, M. (2025). Integrating Solar Energy into German Vineyards: A Geospatial Framework for Identifying Agrivoltaic Potential. Agronomy, 15(9), 2174. https://doi.org/10.3390/agronomy15092174