LogoLogo
Savimbo homepageBuy creditsSpanish
  • 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
Powered by GitBook
LogoLogo

Follow us

  • Twitter
  • Instagram
  • TikTok
  • LinkedIn

About Savimbo

  • Science
  • Buy credits
  • About us
  • Donate

Indigenous authors

  • Jhony Lopez
  • Fernando Lezama
  • Blog

© 2023 Savimbo Inc. All rights reserved.

On this page

Was this helpful?

  1. Project description
  2. Project boundaries

Grouped projects

Designing for viral behavior change among IP and LC conservationists and their neighbors

PreviousTemporal limits of the BCPNextImplementation plan

Last updated 1 year ago

Was this helpful?

This methodology was specifically designed for behavior change and lateral spread between and among IP and LC, whether adjacent smallfarmers, around the borders of game parks, and between Indigenous groups and their smallfarming neighbors. Thus grouped projects are encouraged, and the design of grouped projects are specifically addressed.

Grouped projects benefit biodiversity as animals range outside the borders of conserved areas, and ecosystem connectivity is a clear global conservation target .

Projects can begin as, or convert to grouped projects, at any point in their progress. It is understood that IPs have an international right to , and both groups LCs specifically so they have the freedom to adjust to changing scientific standards or undesirable business relationships. Thus projects are allowed to reduce crediting area as long as the crediting period has been met.

Biodiversity is enhanced at the intersection of ecosystems, so it is possible a grouped project in the same geographic region may extend laterally to cover new ecosystems or indicator species. In this case, the project must provide segmentation and adjust the and if applicable. For instance, a wetland project extends into marine ecosystems, and when those projects are grouped, it enhances both environments. However, the indicator species may not be the same for those types of adjacent grouped projects.

Once a BCP has implemented scalable infrastructure for the monitoring and reporting, scaling should be fairly straightforward. Updated Project boundaries can be provided during verification times if the remains internally consistent.

As a note, given 5 year retroactivity, and clear monitoring data in the Leakage area, there is a strong financial incentive for neighboring lands to convert to conservation, and claim retroactive crediting. This is by design, should be encouraged, and contributes greatly to the 20% growth in conserved areas and behavior change in hunting of rare animals (jaguar and harpy eagle) witnessed in the for this methodology.

In BCP projects using this methodology in de novo sites, it is strongly encouraged to start with a small area, prove the model sufficiently to IP and LCs first with tangible results then grow laterally year-over-year based on conservation successes and earned-trust.

(Vilar et al. 2020)
ongoing consent
desire shorter-term contracts
1-year minimum
Project description
Baseline assessment
Monitoring plan
pilot project