In: Umweltwissenschaften und Schadstoff-Forschung: UWSF ; Zeitschrift für Umweltchemie und Ökotoxikologie ; Organ des Verbandes für Geoökologie in Deutschland (VGöD) und der Eco-Informa, Band 16, Heft 3, S. 161-167
Viticulture and winemaking are important socioeconomic sectors in many European regions. Climate plays a vital role in the terroir of a given wine region, as it strongly controls canopy microclimate, vine growth, vine physiology, yield, and berry composition, which together determine wine attributes and typicity. New challenges are, however, predicted to arise from climate change, as grapevine cultivation is deeply dependent on weather and climate conditions. Changes in viticultural suitability over the last decades, for viticulture in general or the use of specific varieties, have already been reported for many wine regions. Despite spatially heterogeneous impacts, climate change is anticipated to exacerbate these recent trends on suitability for wine production. These shifts may reshape the geographical distribution of wine regions, while wine typicity may also be threatened in most cases. Changing climates will thereby urge for the implementation of timely, suitable, and cost-effective adaptation strategies, which should also be thoroughly planned and tuned to local conditions for an effective risk reduction. Although the potential of the different adaptation options is not yet fully investigated, deserving further research activities, their adoption will be of utmost relevance to maintain the socioeconomic and environmental sustainability of the highly valued viticulture and winemaking sector in Europe. ; This study was funded by Clim4Vitis project—"Climate change impact mitigation for European viticulture: knowledge transfer for an integrated approach", funded by the European Union's Horizon 2020 Research and Innovation Programme, under grant agreement no. 810176; it was also supported by FCT—Portuguese Foundation for Science and Technology, under the project UIDB/04033/2020.
Budbreak date in grapevine is strictly dependent on temperature, and the correct simulation of its occurrence is of great interest since it may have major consequences on the final yield and quality. In this study, we evaluated the reliability for budbreak simulation of two modeling approaches, the chilling-forcing (CF), which describes the entire dormancy period (endo- and eco-dormancy) and the forcing approach (F), which only describes the eco-dormancy. For this, we selected six phenological models that apply CF and F in different ways, which were tested on budbreak simulation of eight grapevine varieties cultivated at different latitudes in Europe. Although none of the compared models showed a clear supremacy over the others, models based on CF showed a generally higher estimation accuracy than F where fixed starting dates were adopted. In the latter models, the accurate simulation of budbreak was dependent on the selection of the starting date for forcing accumulation that changes according to the latitude, whereas CF models were independent. Indeed, distinct thermal requirements were found for the grapevine varieties cultivated in Northern and Southern Europe. This implies the need to improve modeling of the dormancy period to avoid under- or over-estimations of budbreak date under different environmental conditions. ; This research was funded by the European Union's Horizon 2020 Research and Innovation Programme, under the Clim4Vitis project: "Climate change impact mitigation for European viticulture: knowledge transfer for an integrated approach", grant agreement no. 810176. It was also supported by FCT-Portuguese Foundation for Science and Technology, under the project UIDB/04033/2020 and the French National Research Agency (ANR) in the frame of the Investments for the Future Program, within the cluster of excellence COTE (ANR-10-LABX-45).
The EU Water Framework Directive aims to ensure restoration of Europe's water bodies to "good ecological status" by 2027. Many Member States will struggle to meet this target, with around half of EU river catchments currently reporting below standard water quality. Diffuse pollution from agriculture represents a major pressure, affecting over 90% of river basins. Accumulating evidence shows that recent improvements to agricultural practices are benefiting water quality but in many cases will be insufficient to achieve WFD objectives. There is growing support for land use change to help bridge the gap, with a particular focus on targeted tree planting to intercept and reduce the delivery of diffuse pollutants to water. This form of integrated catchment management offers multiple benefits to society but a significant cost to landowners and managers. New economic instruments, in combination with spatial targeting, need to be developed to ensure cost effective solutions – including tree planting for water benefits - are realised. Payments for Ecosystem Services (PES) are flexible, incentive-based mechanisms that could play an important role in promoting land use change to deliver water quality targets. The PESFOR-W COST Action will consolidate learning from existing woodlands for water PES schemes in Europe and help standardize approaches to evaluating the environmental effectiveness and cost-effectiveness of woodland measures. It will also create a European network through which PES schemes can be facilitated, extended and improved, for example by incorporating other ecosystem services linking with aims of the wider forests-carbon policy nexus.
In: Valatin , G , Abildtrup , J , Accastello , C , Said Al-Tawaha , A R M , Andreucci , M-B , Atanasova , S , Avdibegović , M , Baksic , N , Banasik , K , Barquin , J , Barstad , J , Bastakova , V , Becirovic , D , Begueria , S , Bethers , U , Bihunova , M , Blagojevic , B , Bösch , M , Bournaris , T , Cao , Y , Carvalho-Santos , C , Chikalanov , A , A. Cunha e Sá , M , Czyżyk , K , Daly , H , Davies , H , Del Campo , A , de Groot , R , De Vreese , R , Dostál , T , El Mokaddem , A , Finér , L , Evans , R , Fiquepron , J , Frac , M , Futter , M , Garcia , S , Gatto , P , Geneletti , D , Gezik , V , Giupponi , C , González-Sanchís , M , Gordillo , F , Gorriz , E , Grigorova , Y , Heinsoo , K , Hochbichler , E , Högbom , L , Image , M , Jacobsen , J B , Japelj , A , Jelic , S , Junk , J , Juhasz , C , Kagalou , I , Kelly-Quinn , M , Klamerus-Iwan , A , Kluvankova , T , Koeck , R , Konovska , I , Krajter Ostoic , S , Krc , J , Lavnyy , V , Leonardi , A , Libiete , Z , Little , D , Lo Porto , A , Loukas , A , Lyubenova , M I , Maric , B , Martínez-López , J , Martinez , I , Maxim , A , Metslaid , M , Melvin , A , Costică , M , Mincev , I , Morkvenas , Z , Nevenic , R , Nisbet , T , O'hUallachain , D , Olschewski , R , Östberg , J , Oszust , K , Ovando , P , Paletto , A , Parpan , T , Pettenella , D , Pezdevšek Malovrh , Š , Planinšek , Š , Podlipná , R , Posavec , S , Potočki , K , Prokofieva , I , Quinteiro , P , Radocz , L , Ristic , R , Robert , N , Rugani , B , Sabanovic , J , Sarvasova , Z , Savoska , S , Schleppi , P , Schueler , G , Shannon , M , Silgram , M , Srdjevic , B , Stefan , G , Stijovic , A , Strange , N , Tattari , S , Teofilovski , A , Termansen , M , Thorsen , B J , Toth , A , Trebs , I , Tmušić , N , Vasiliades , L , Vedel , S E , Ventrubová , K , Vuletic , D , Winkel , G , Yao , R , Young , S , Yousefpour , R , Zahvoyska , L , Zhang , D , Zhou , J & Žižková , E 2017 , ' PESFOR-W : improving the design and environmental effectiveness of woodlands for water payments for ecosystem services ' , Research Ideas and Outcomes , vol. 3 , e13828 . https://doi.org/10.3897/rio.3.e13828
The EU Water Framework Directive aims to ensure restoration of Europe's water bodies to "good ecological status" by 2027. Many Member States will struggle to meet this target, with around half of EU river catchments currently reporting below standard water quality. Diffuse pollution from agriculture represents a major pressure, affecting over 90% of river basins. Accumulating evidence shows that recent improvements to agricultural practices are benefiting water quality but in many cases will be insufficient to achieve WFD objectives. There is growing support for land use change to help bridge the gap, with a particular focus on targeted tree planting to intercept and reduce the delivery of diffuse pollutants to water. This form of integrated catchment management offers multiple benefits to society but a significant cost to landowners and managers. New economic instruments, in combination with spatial targeting, need to be developed to ensure cost effective solutions – including tree planting for water benefits - are realised. Payments for Ecosystem Services (PES) are flexible, incentive-based mechanisms that could play an important role in promoting land use change to deliver water quality targets. The PESFOR-W COST Action will consolidate learning from existing woodlands for water PES schemes in Europe and help standardize approaches to evaluating the environmental effectiveness and cost-effectiveness of woodland measures. It will also create a European network through which PES schemes can be facilitated, extended and improved, for example by incorporating other ecosystem services linking with aims of the wider forests-carbon policy nexus. ; The EU Water Framework Directive aims to ensure restoration of Europe's water bodies to "good ecological status" by 2027. Many Member States will struggle to meet this target, with around half of EU river catchments currently reporting below standard water quality. Diffuse pollution from agriculture represents a major pressure, affecting over 90% of river basins. Accumulating evidence shows that recent improvements to agricultural practices are benefiting water quality but in many cases will be insufficient to achieve WFD objectives. There is growing support for land use change to help bridge the gap, with a particular focus on targeted tree planting to intercept and reduce the delivery of diffuse pollutants to water. This form of integrated catchment management offers multiple benefits to society but a significant cost to landowners and managers. New economic instruments, in combination with spatial targeting, need to be developed to ensure cost effective solutions – including tree planting for water benefits - are realised. Payments for Ecosystem Services (PES) are flexible, incentive-based mechanisms that could play an important role in promoting land use change to deliver water quality targets. The PESFOR-W COST Action will consolidate learning from existing woodlands for water PES schemes in Europe and help standardize approaches to evaluating the environmental effectiveness and cost-effectiveness of woodland measures. It will also create a European network through which PES schemes can be facilitated, extended and improved, for example by incorporating other ecosystem services linking with aims of the wider forests-carbon policy nexus.