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  • Executive summary
  • Front Material
    • Contents
    • Index of figures
    • Index of tables
    • Acronyms and abbreviations
    • Terms and definitions
  • Getting started
  • Introduction
    • The urgency of targeted biodiversity conservation
    • Simplicity, complexity theory, and biodiversity
    • Inclusion of Indigenous Peoples and local communities by design
    • Biodiversity methodology benefits
  • Overall description
    • Objectives
    • Scope
    • Limitations
  • Project description
    • Principles
      • Principles of working with IP
    • Eligibility criteria
      • Land ownership and law
    • Additionality
    • Project boundaries
      • Spatial limits of the BCP
      • Temporal limits of the BCP
      • Grouped projects
    • Implementation plan
      • Measurement approaches
      • Indicator species observations
      • Risks and uncertainty
    • Effective participation
      • Community involvement
      • Capacity for action
      • Financial transparency
      • Safeguards checklist
  • Calculation
    • Unit calculations
    • Area calculations
    • Time calculations
    • Integrity calculations
    • Value calculations
  • Baseline assessment
    • Baseline ecosystem categorization
    • Analysis of agents and drivers of biodiversity loss
    • Baseline biodiversity (optional)
    • Baseline risk of biodiversity loss
    • Indicator species selection
    • Indicator species integrity score
  • SDG contributions
  • Monitoring plan
    • Monitoring report
    • Additional monitoring requirements
  • Authors
  • References
  • Appendices
    • Appendix A: Biodiversity methodologies comparison table
    • Appendix B: Sample legal proof of land control
    • Appendix C: Sample baseline ecosystem categorization
    • Appendix D: Species categorization of richness
    • Appendix E: Sample selection of indicator species
    • Appendix F: Sample indicator-species observations
    • Appendix G: Sample open-source code and calculation
    • Appendix H: Indigenous authors
    • Appendix I: Letters of support
      • Fernando Ayerbe, Ornithology
      • Ned Hording, Biodiversity
      • Olber Llanos, Zoologist
      • Mike McColm, Ethnology
      • Peter Thomas, Anthropologist
      • Jesús Argente, Marine biology
      • Sara Andreotti, Marine Biologist
      • Carolina Romero, Lawyer.
      • Daniel Urbano, Herpetologist
      • Ramesh Boonratana PhD, Primatologist
      • Theodore Schmitt, Conservationists
      • Anja Hutschenreiter, Ecologist and Tropical Conservationist
      • Miguel Chindoy, Indigenous leader
    • Appendix J: Sample uses of biodiversity unit
    • Appendix K: How to do FPIC
    • Appendix L: Independent Expert Panel Checklist
    • Appendix M: How to calculate a biodiversity credit by hand
    • Appendix N: How to calculate home ranges
    • Appendix O: How to calculate integrity scores
  • Document history
  • Disclaimer
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  1. Project description

Additionality

Characterization of the project's need for biodiversity crediting

PreviousLand ownership and lawNextProject boundaries

Last updated 1 year ago

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General additionality of this methodology must be demonstrated by applying the decision tree that appears in the current version of the Cercarbono's and covers financial, normative, and regulatory surplus additionality scenarios, to demonstrate that the biodiversity conservation is directly related to the project activity(ies) and not an external source.

The additionality of actions measured by methodology in particular is simplified to enable IP and LC inclusion.

This methodology judges outcomes from the perspective of other species. Humans may make marginal improvements in degraded ecosystems, and certainly, for severely degraded ecosystems this can easily be a 200%-fold, or 300%-fold improvement. However, restored ecosystems can never be fully available to the complete variety of native species in the way that undisrupted ecosystems are.

Thus, for projects occurring in high-biodiversity, high-threat ecosystems, additionality is inherent in the and . For example, any intact ecosystem on an IUCN red list, or biodiversity hotspot ecosystem is inherently additional due to its threatened status.

The in this methodology are meant to establish acceptable proof of a conserved ecosystem. Thus instead of providing evidence for a change, they provide reasonable evidence of no change which is inherently additional in a threatened ecosystem.

In the context of conservation, where external sources have validated that an ecosystem is under threat, additionality merely needs to demonstrate that the project maintains the presence of biodiversity and that activities are not duplicated by other sources.

Biodiversity Certification Programme Protocol
Ecosystem characterization
Value normalization
Integrity calculations