Jose Luis Vicente-Vicente

Dr. Jose Luis Vicente-Vicente

Leibniz Centre for Agricultural Landscape Research (ZALF) e.V., Müncheberg, DE

Research Focus & Metrics

Academic Career Length

11Years (2016-Present)

(Calculated once Scilit publication data is synced: current year − year of first publication + 1)

Representative Publications

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21 May 2018 in Environmental Research Letters
Verified
Journal Article
Open access
PDF file
SFSabine Fuss
Sabine Fuss
WLWilliam F Lamb
William F Lamb
MCMax W Callaghan
Max W Callaghan
JHJérôme Hilaire
Jérôme Hilaire
FCFelix Creutzig
Felix Creutzig
JMJan C Minx
Jan C Minx

21 May 2018 in Environmental Research Letters
Verified
Journal Article
Open access
PDF file
JMJan C Minx
Jan C Minx
WLWilliam F Lamb
William F Lamb
MCMax W Callaghan
Max W Callaghan
SFSabine Fuss
Sabine Fuss
JHJérôme Hilaire
Jérôme Hilaire
MDMaria del Mar Zamora Dominguez
Maria del Mar Zamora Dominguez

17 October 2019 in Annual Review of Environment and Resources
Verified
Journal Article
Closed access
PSPete Smith
Pete Smith
JAJustin Adams
Justin Adams
DBDavid J. Beerling
David J. Beerling
TBTim Beringer
Tim Beringer
KCKatherine V. Calvin
Katherine V. Calvin
SKSaskia Keesstra
Saskia Keesstra
Land-management options for greenhouse gas removal (GGR) include afforestation or reforestation (AR), wetland restoration, soil carbon sequestration (SCS), biochar, terrestrial enhanced weathering (TEW), and bioenergy with carbon capture and storage (BECCS). We assess the opportunities and risks associated with these options through the lens of their potential impacts on ecosystem services (Nature's Contributions to People; NCPs) and the United Nations Sustainable Development Goals (SDGs). We find that all land-based GGR options contribute positively to at least some NCPs and SDGs. Wetland restoration and SCS almost exclusively deliver positive impacts. A few GGR options, such as afforestation, BECCS, and biochar potentially impact negatively some NCPs and SDGs, particularly when implemented at scale, largely through competition for land. For those that present risks or are least understood, more research is required, and demonstration projects need to proceed with caution. For options that present low risks and provide cobenefits, implementation can proceed more rapidly following no-regrets principles.

15 May 2020 in Global Change Biology
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Journal Article
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Alicia LedoAlicia Ledo
Alicia Ledo
PSPete Smith
Pete Smith
AZAyalsew Zerihun
Ayalsew Zerihun
JWJeanette Whitaker
Jeanette Whitaker
Jose Luis Vicente-VicenteJose Luis Vicente-Vicente
Jose Luis Vicente-Vicente
JHJon Hillier
Jon Hillier
This study evaluates the dynamics of soil organic carbon (SOC) under perennial crops across the globe. It quantifies the effect of change from annual to perennial crops and the subsequent temporal changes in SOC stocks during the perennial crop cycle. It also presents an empirical model to estimate changes in the SOC content under crops as a function of time, land use, and site characteristics. We used a harmonized global dataset containing paired‐comparison empirical values of SOC and different types of perennial crops (perennial grasses, palms, and woody plants) with different end uses: bioenergy, food, other bio‐products, and short rotation coppice. Salient outcomes include: a 20‐year period encompassing a change from annual to perennial crops led to an average 20% increase in SOC at 0–30 cm (6.0 ± 4.6 Mg/ha gain) and a total 10% increase over the 0–100 cm soil profile (5.7 ± 10.9 Mg/ha). A change from natural pasture to perennial crop decreased SOC stocks by 1% over 0–30 cm (−2.5 ± 4.2 Mg/ha) and 10% over 0–100 cm (−13.6 ± 8.9 Mg/ha). The effect of a land use change from forest to perennial crops did not show significant impacts, probably due to the limited number of plots; but the data indicated that while a 2% increase in SOC was observed at 0–30 cm (16.81 ± 55.1 Mg/ha), a decrease in 24% was observed at 30–100 cm (−40.1 ± 16.8 Mg/ha). Perennial crops generally accumulate SOC through time, especially woody crops; and temperature was the main driver explaining differences in SOC dynamics, followed by crop age, soil bulk density, clay content, and depth. We present empirical evidence showing that the FAO perennialization strategy is reasonable, underscoring the role of perennial crops as a useful component of climate change mitigation strategies.

22 February 2023 in Soil Systems
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Journal Article
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Rosa FrancavigliaRosa Francaviglia
Rosa Francaviglia
MAMaría Almagro
María Almagro
Jose Luis Vicente-VicenteJose Luis Vicente-Vicente
Jose Luis Vicente-Vicente
Intensive agriculture causes land degradation and other environmental problems, such as pollution, soil erosion, fertility loss, biodiversity decline, and greenhouse gas (GHG) emissions, which exacerbate climate change. Sustainable agricultural practices, such as reduced tillage, growing cover crops, and implementing crop residue retention measures, have been proposed as cost-effective solutions that can address land degradation, food security, and climate change mitigation and adaptation by enhancing soil organic carbon (SOC) sequestration in soils and its associated co-benefits. In this regard, extensive research has demonstrated that conservation agriculture (CA) improves soil physical, chemical, and biological properties that are crucial for maintaining soil health and increasing agroecosystem resilience to global change. However, despite the research that has been undertaken to implement the three principles of CA (minimum mechanical soil disturbance, permanent soil organic cover with crop residues and/or cover crops, and crop diversification) worldwide, there are still many technical and socio-economic barriers that restrict their adoption. In this review, we gather current knowledge on the potential agronomic, environmental, and socio-economic benefits and drawbacks of implementing CA principles and present the current agro-environmental policy frameworks. Research needs are identified, and more stringent policy measures are urgently encouraged to achieve climate change mitigation targets.

1 November 2016 in Agriculture, Ecosystems & Environment
Verified
Journal Article
Open access
Jose Luis Vicente-VicenteJose Luis Vicente-Vicente
Jose Luis Vicente-Vicente
RGRoberto García-Ruíz
Roberto García-Ruíz
Rosa FrancavigliaRosa Francaviglia
Rosa Francaviglia
Eduardo AguileraEduardo Aguilera
Eduardo Aguilera
PSPete Smith
Pete Smith
This work was supported by the projects: CARBOLIVAR (P11-RNM-7186) funded by Consejería de Innovación, Ciencia y Empresa of Junta de Andalucía and GEISpain project (CGL2014‐52838‐C2‐1‐R) funded by Ministerio de Economía y Competitividad, both including European Union ERDF funds. This work was also supported by the FPU 2012 grant program of the Ministerio de Educación, Cultura y Deporte of Spain. Dr. Roberto Garcia-Ruiz and Eduardo Aguilera gratefully acknowledge support by the Sustainable Farm Systems project (SSHRC 895-2011-1020) funded by the Canadian Social Sciences and Humanities Research Council.Peer reviewedPostprin