Advancing Systematic Conservation Planning for Ecosystem Services
Notice bibliographique
Résumé
We are at a critical time to ensure long-term prosperity for people and nature. This is reflected by international policy frameworks such as the United Nations Sustainable Development Goals. Systematic conservation planning (SCP) has been applied as a rigorous and transparent approach to inform solutions for biodiversity conservation by private and government conservation organizations globally. This approach has gained increased attention for safeguarding ecosystem services. Nevertheless, inappropriate incorporation of the social and biophysical components of ecosystem services could result in landscape plans that fail to generate the expected benefits for people. Taking inspiration from decision theory, we provide guidance on how to incorporate ecosystem service components into SCP to secure nature’s contributions to human well-being. Conservation and sustainable management activities are critical for enhancing ecosystem services. Systematic conservation planning (SCP) is a spatial decision support process used to identify the most cost-effective places for intervention and is increasingly incorporating ecosystem services thinking. Yet, there is no clear guidance on how to incorporate ecosystem service components (i.e., supply, demand, and flow) for multiple beneficiaries into the decision problem underpinning SCP. As such, conservation plans may fall short of maximizing benefits for both people and nature. We propose a benefit-based approach to integrate ecosystem service components into SCP that uses the principles of decision theory. Our approach will improve the likelihood that ecosystem service benefits are enhanced in spatial planning applications. Conservation and sustainable management activities are critical for enhancing ecosystem services. Systematic conservation planning (SCP) is a spatial decision support process used to identify the most cost-effective places for intervention and is increasingly incorporating ecosystem services thinking. Yet, there is no clear guidance on how to incorporate ecosystem service components (i.e., supply, demand, and flow) for multiple beneficiaries into the decision problem underpinning SCP. As such, conservation plans may fall short of maximizing benefits for both people and nature. We propose a benefit-based approach to integrate ecosystem service components into SCP that uses the principles of decision theory. Our approach will improve the likelihood that ecosystem service benefits are enhanced in spatial planning applications. iterative framework for learning-based decision-making that pursues the reduction of uncertainty through monitoring the outcomes of management interventions [46.Birge H. et al.Adaptive management for ecosystem services.J. Environ. Manag. 2016; 183: 343-352Crossref PubMed Scopus (46) Google Scholar,47.McCarthy M.A. Possingham H.P. Active adaptive management for conservation.Conserv. Biol. 2007; 21: 956-963Crossref PubMed Scopus (226) Google Scholar]. people whose well-being is influenced by ecosystem services [25.Daw T. et al.Applying the ecosystem services concept to poverty alleviation: the need to disaggregate human well-being.Environ. Conserv. 2011; 38: 370-379Crossref Scopus (422) Google Scholar,32.Keeler B.L. et al.Linking water quality and well-being for improved assessment and valuation of ecosystem services.Proc. Natl. Acad. Sci. U. S. A. 2012; 109: 18619-18624Crossref PubMed Scopus (303) Google Scholar]. direct or indirect gains that people receive from ecosystem services measured in aspects of human well-being [1.Millennium Ecosystem Assessment Ecosystems and Human Well-Being: Biodiversity Synthesis. World Resources Institute, Washington, DC2005Google Scholar,64.Díaz S. et al.The IPBES Conceptual Framework — connecting nature and people.Curr. Opin. Environ. Sustain. 2015; 14: 1-16Crossref Scopus (1178) Google Scholar]. disciplined protocol for problem solving based on decision theory, which attempts to achieve explicitly stated objectives while acknowledging the levels of uncertainty involved with the decision process (i.e., describe the problem, set objectives, define variables, list actions, identify constraints, and model the system) [23.Possingham H.P. et al.Making smart conservation decisions.in: Orians G. Soule M. Research Priorities for Conservation Biology. Island Press, 2001: 225-244Google Scholar]. extent to which an ecosystem service is currently or potentially used, needed, or preferred by people [65.Villamagna A.M. et al.Capacity, pressure, demand, and flow: a conceptual framework for analyzing ecosystem service provision and delivery.Ecol. Complex. 2013; 15: 114-121Crossref Scopus (382) Google Scholar,66.Bagstad K.J. et al.Spatial dynamics of ecosystem service flows: a comprehensive approach to quantifying actual services.Ecosyst. Serv. 2013; 4: 117-125Crossref Scopus (327) Google Scholar]. recognition of the variation in demand and potential to derive ecosystem service benefits among beneficiaries [25.Daw T. et al.Applying the ecosystem services concept to poverty alleviation: the need to disaggregate human well-being.Environ. Conserv. 2011; 38: 370-379Crossref Scopus (422) Google Scholar,58.Horcea-Milcu A. et al.Disaggregated contributions of ecosystem services to human well-being: a case study from Eastern Europe.Reg. Environ. Chang. 2016; 16: 1779-1791Crossref Scopus (38) Google Scholar]. biophysical and social conditions and processes by which people, directly or indirectly, obtain benefits from ecosystems that sustain and fulfil human well-being [1.Millennium Ecosystem Assessment Ecosystems and Human Well-Being: Biodiversity Synthesis. World Resources Institute, Washington, DC2005Google Scholar,64.Díaz S. et al.The IPBES Conceptual Framework — connecting nature and people.Curr. Opin. Environ. Sustain. 2015; 14: 1-16Crossref Scopus (1178) Google Scholar]. interactions and processes that connect supply and demand [65.Villamagna A.M. et al.Capacity, pressure, demand, and flow: a conceptual framework for analyzing ecosystem service provision and delivery.Ecol. Complex. 2013; 15: 114-121Crossref Scopus (382) Google Scholar, 66.Bagstad K.J. et al.Spatial dynamics of ecosystem service flows: a comprehensive approach to quantifying actual services.Ecosyst. Serv. 2013; 4: 117-125Crossref Scopus (327) Google Scholar, 67.Fisher B. et al.Defining and classifying ecosystem services for decision making.Ecol. Econom. 2009; 68: 643-653Crossref Scopus (1878) Google Scholar]. Broadly, it includes flow direction (spatial relationship that describes where the benefit is received) and flow type (classification of flow into biophysical, human capital-driven through transportation or infrastructure, or mediated by information transmission) [65.Villamagna A.M. et al.Capacity, pressure, demand, and flow: a conceptual framework for analyzing ecosystem service provision and delivery.Ecol. Complex. 2013; 15: 114-121Crossref Scopus (382) Google Scholar, 66.Bagstad K.J. et al.Spatial dynamics of ecosystem service flows: a comprehensive approach to quantifying actual services.Ecosyst. Serv. 2013; 4: 117-125Crossref Scopus (327) Google Scholar, 67.Fisher B. et al.Defining and classifying ecosystem services for decision making.Ecol. Econom. 2009; 68: 643-653Crossref Scopus (1878) Google Scholar]. the world’s stocks of natural assets including geology, soil, air, water, and all living things [1.Millennium Ecosystem Assessment Ecosystems and Human Well-Being: Biodiversity Synthesis. World Resources Institute, Washington, DC2005Google Scholar]. mathematical formulation describing the problem of finding the best solution from all feasible solutions [7.Moilanen A. et al.Spatial Conservation Prioritization. Quantitative Methods and Computational Tools. Oxford University Press, 2009Google Scholar]. ecosystem conditions and processes that contribute to the potential delivery of a particular ecosystem service [65.Villamagna A.M. et al.Capacity, pressure, demand, and flow: a conceptual framework for analyzing ecosystem service provision and delivery.Ecol. Complex. 2013; 15: 114-121Crossref Scopus (382) Google Scholar, 66.Bagstad K.J. et al.Spatial dynamics of ecosystem service flows: a comprehensive approach to quantifying actual services.Ecosyst. Serv. 2013; 4: 117-125Crossref Scopus (327) Google Scholar, 67.Fisher B. et al.Defining and classifying ecosystem services for decision making.Ecol. Econom. 2009; 68: 643-653Crossref Scopus (1878) Google Scholar]. structured decision analysis approach with a series of stages that concern both the design and implementation of conservation actions to meet specific objectives, usually through the spatial prioritization of the most feasible places for conservation investment [7.Moilanen A. et al.Spatial Conservation Prioritization. Quantitative Methods and Computational Tools. Oxford University Press, 2009Google Scholar, 8.Pressey R. Bottrill M. Approaches to landscape- and seascape-scale conservation planning: convergence, contrasts and challenges.Oryx. 2009; 43: 464-475Crossref Scopus (196) Google Scholar, 9.Margules C.R. Pressey R.L. Systematic conservation planning.Nature. 2000; 405: 243-253Crossref PubMed Scopus (3929) Google Scholar].
Récupéré en direct depuis OpenAlex et désinversé. Les résumés ne sont pas conservés dans cette base de données : les index inversés représentent 8,6 Go des 9,3 Go de texte de la base, et le serveur dispose de 13 Go libres.
Comment cette classification a été obtenuedéplier
Prédiction distillée sur la base complète
Imitation des enseignantsNi prévalence calibrée, ni vérité terrain. Validation humaine à venir. Apprise à partir de 10 348 étiquettes directes de Codex et de 10 348 étiquettes directes de Gemma. Le mode candidate est l'union des têtes enseignantes seuillées; le consensus est leur intersection. Ces sorties portent le statut machine_predicted_unvalidated et ne sont ni des étiquettes humaines ni des étiquettes directes de modèles de pointe.
Scores Codex et Gemma par catégorie
| Catégorie | Codex | Gemma |
|---|---|---|
| Métarecherche | 0,001 | 0,000 |
| Méta-épidémiologie (sens strict) | 0,000 | 0,000 |
| Méta-épidémiologie (sens large) | 0,002 | 0,000 |
| Bibliométrie | 0,000 | 0,001 |
| Études des sciences et des technologies | 0,000 | 0,000 |
| Communication savante | 0,000 | 0,000 |
| Science ouverte | 0,000 | 0,000 |
| Intégrité de la recherche | 0,000 | 0,000 |
| Charge utile insuffisante (le modèle a refusé de juger) | 0,000 | 0,000 |
Scores machine (provisoires)
Les deux têtes enseignantes du modèle étudiant, lues sur ce travail. Un score ordonne la base pour la relecture; il n'affirme jamais une catégorie, et le statut de validation accompagne chaque rangée tel quel.
Scores de référence d'un modèle non mature (critères de maturité non atteints, 7 itérations). Un score ordonne; il n'affirme jamais une catégorie.
score_only:v0-immature-baseline · tel quel depuis la passe de notation : score_only signifie que le nombre peut ordonner les travaux, et qu'aucune étiquette de catégorie n'en découleClassification
machine, non validéePrédiction automatique; un appel candidat d’une seule tête enseignante, pas un consensus.
Le détail, modèle par modèle et score par score, se trouve en fin de page sous « Comment cette classification a été obtenue ».