Abstract

The spatial monitoring of plant diversity in the endangered species-rich grasslands of European mountain pastoral systems is an important step for fairer and more efficient Agri-Environmental policy schemes supporting conservation. This study assessed the underlying support for a spatially explicit monitoring of plant species richness at parcel level (policy making scale) in Southern European mountain grasslands, with statistical models informed by Sentinel-2 satellite and environmental factors. Twenty-four grassland parcels were surveyed for species richness in the Peneda-Gerês National Park, northern Portugal. Using a multi-model inference approach, three competing hypotheses guided by the species-scaling theoretical framework were established: species–area (P1), species–energy (P2) and species–spectral heterogeneity (P3), each representing a candidate spatial pathway to predict species richness. To evaluate the statistical support of each spatial pathway, generalized linear models were fitted and model selection based on Akaike information criterion (AIC) was conducted. Later, the performance of the most supported spatial pathway(s) was assessed using a leave-one-out cross validation. A model guided by the species–energy hypothesis (P2) was the most parsimonious spatial pathway to monitor plant species richness in mountain grassland parcels (P2, AICc = 137.6, ∆AIC = 0.0, wi = 0.97). Species–area and species–spectral heterogeneity pathways (P1 and P3) were less statistically supported (ΔAICc values in the range 5.7–10.0). The underlying support of the species–energy spatial pathway was based on Sentinel-2 satellite data, namely on the near-infrared (NIR) green ratio in the spring season (NIR/Greenspring) and on its ratio of change between spring and summer (NIR/Greenchange). Both predictor variables related negatively to species richness. Grassland parcels with lower values of near-infrared (NIR) green ratio and lower seasonal amplitude presented higher species richness records. The leave-one-out cross validation indicated a moderate performance of the species–energy spatial pathway in predicting species richness in the grassland parcels covered by the dataset (R2 = 0.44, RMSE = 4.3 species, MAE = 3.5 species). Overall, a species–energy framework based on Sentinel 2 data resulted in a promising spatial pathway for the monitoring of species richness in mountain grassland parcels and for informing decision making on Agri-Environmental policy schemes. The near-infrared (NIR) green ratio and its change in time seems a relevant variable to deliver predictions for plant species richness and further research should be conducted on that.

Highlights

  • Agri-Environmental policy schemes are the most powerful tools to support conservation measures in the European agricultural landscapes (e.g., Common Agriculture Policy, CAP) and to ensure that they are supporting biodiversity and the best possible agricultural production is essential [1]

  • This study addresses the spatially explicit monitoring of plant diversity in mountain grasslands in view of more effective Agri-Environmental policy schemes devoted to their protection and management (e.g., CAP)

  • The results of generalized linear modeling and AICc model selection indicated the spatial pathway guided by the species–energy scaling relationship as the most parsimonious to monitor plant species richness in mountain grassland parcels (P2, AICc = 137.6, ∆Akaike information criterion (AIC) = 0.0, wi = 0.97, Table 1)

Read more

Summary

Introduction

Agri-Environmental policy schemes are the most powerful tools to support conservation measures in the European agricultural landscapes (e.g., Common Agriculture Policy, CAP) and to ensure that they are supporting biodiversity and the best possible agricultural production is essential [1]. Among the different strategies that can be followed to pursue this goal, the spatially explicit monitoring of biodiversity represents one of the most relevant. Among the systems that would benefit most from a spatially explicit development of policy are the European mountain pastoral systems and their endangered species-rich grasslands [2]. Allowing the spatial monitoring of plant diversity at policy making levels (e.g., parcel level, unit of payment of conservation schemes to farmers) is fundamental to efficiently allocate subsidies and delineate local protection schemes for species-rich sites

Methods
Results
Conclusion

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call

Disclaimer: All third-party content on this website/platform is and will remain the property of their respective owners and is provided on "as is" basis without any warranties, express or implied. Use of third-party content does not indicate any affiliation, sponsorship with or endorsement by them. Any references to third-party content is to identify the corresponding services and shall be considered fair use under The CopyrightLaw.