Guidelines on Business and KBAs:
Managing Risk to Biodiversity

Guidelines on Business and KBAs:
Managing Risk to Biodiversity

The designation of geographical entities in this document, and the presentation of the material, do not imply the expressionof any opinion whatsoever on the part of IUCN or other participating organisations concerning the legal status of any country,
territory, or area, or of its authorities, or concerning the delimitation of its frontiers or boundaries.
The views expressed in this document do not necessarily reflect those of IUCN or other participating organisations.
The development of this document was made possible with the generous support of The Tiffany & Co. Foundation.
Published by:

IUCN, Gland, Switzerland in collaboration with KBA partners

Copyright:© 2018 IUCN, International Union for Conservation of Nature and Natural Resources
Reproduction of this publication for educational or other non-commercial purposes is authorised
without prior written permission from the copyright holder, provided the source is fully acknowledged.
Reproduction of this publication for resale or other commercial purposes is prohibited without priorwritten permission of the copyright holder.

Citation:

The KBA Partnership (2018) Guidelines on Business and KBAs: Managing Risk to Biodiversity.
Gland: IUCN. 24pp, 2018

ISBN:

978-2-8317-1894-1

DOI:

https://doi.org/10.2305/IUCN.CH.2018.05.en

Cover photo:

Oil drilling in the Queen Elizabeth National Park, Uganda © A.Plumptre/WCS

Layout by:

Imre Sebestyén, jr / UNITgraphics

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Guidelines on Business and KBAs: Managing Risk to Biodiversity

TABLE OF CONTENTS

About the KBA Partnership. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . iv
Foreword. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .  v
Acknowledgments. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . vi
Terms used in defining KBAs. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . vi
Glossary. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .  viiExecutive summary. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . xi
1. BUSINESS AND KBAs. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1
Risks and opportunities for biodiversity …and for people . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1
Business as a positive force for the conservation of KBAs. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 1
2. MORE ABOUT KBAs. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2
A strengthened approach to the conservation of global biodiversity . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2
A global standard for identifying sites of biodiversity importance . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2
Some facts about KBAs . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2
Defining the boundaries of KBAs. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 2
The World Database of Key Biodiversity AreasTM. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 9
Key Biodiversity Areas, protected areas, and conservation priorities. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 3
3. GUIDELINES FOR BUSINESS ACTIVITIES. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .4
Applicability . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 4
Conditions for successful implementation. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 5
Project-level Guidelines. . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6
1. Project biodiversity baseline . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 6
2. Priority to avoidance . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7
3. Implementation of early minimisation . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7
4. Limits to impact restoration . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 7
5. Limits to biodiversity offsets . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 8
6. Biodiversity impact monitoring . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 9
7. Long-term financing of the mitigation measures . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 9
8. Responsibilities in case of divestment . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 9
9. Participation and consultation . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 9
10. Responsibility for existing operations . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . 9
Corporate-level Guidelines . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .  10
11. Reporting on KBAs as part of the company’s environmental performance . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .  10
12. Additional conservation actions . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .  10
13. KBAs as targets for offsetting impacts elsewhere . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .  11
14. Sharing biodiversity data . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .  11
15. Compliance with certification schemes and financial institutions’ safeguard policies. . . . . . . . . . . . . . . . . . .  11
Resources . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . .  12iii

Guidelines on Business and KBAs: Managing Risk to Biodiversity

About the KBA Partnership
The Key Biodiversity Area (KBA) Partnership is made up of 12 of the world´s leading international nature
conservation organizations. Together, they will mobilise the expertise, experience and resources of the partnerorganizations to:•••

Identify, map, document and monitor KBAs worldwide
Promote targeted conservation actions in KBAs andInform and influence public policy and private sector decision-making to safeguard KBAs and ensure theireffective conservation.

The KBA Partnership comprises 12 partners:
BirdLife International www.birdlife.org
IUCN www.iucn.org
Amphibian Survival Alliance www.amphibians.org
Conservation International www.conservation.org
Critical Ecosystem Partnership Fund www.cepf.net
Global Environment Facility www.thegef.org
Global Wildlife Conservation globalwildlife.org
NatureServe www.natureserve.org
Rainforest Trust www.rainforesttrust.org
Royal Society for the Protection of Birds www.rspb.org.uk
WWF www.panda.org
Wildlife Conservation Society www.wcs.org
BirdLife International manages the World Database of Key Biodiversity Areas on behalf of the KBA Partnership.
The KBA Partners stand ready to provide support to any business interested in operating in accordance withthese Guidelines, in particular through the KBA Consultative Forum. The KBA Consultative Forum consistsof a wide range of end-users of the KBA Data who provide input and advice to the KBA Committee on thedissemination and use of KBA data, management decisions, marketing, funding, etc. of the KBA Programme,
and who in turn are informed about progress and plans in the implementation of the KBA Programme. End
users include, among others, national governments, multilateral environmental agreements (e.g. Convention
on Biological Diversity, Ramsar Convention), international financing institutions, private sector companies,
intergovernmental agencies, indigenous peoples organizations and non-governmental organizations.
The primary role of the KBA Consultative Forum is to communicate needs and challenges in the use andapplication of KBA Data to the KBA Committee, and conversely to be informed by the KBA Committee about
decisions, progress and plans regarding the implementation of the KBA Programme.
The Consultative Forum is established by the KBA Committee. The current Co-Chairs of the Consultative
Forum are: Olivier Langrand, Critical Ecosystems Partnership Fund, Daniela Raik, Conservation International(chair.consultative.forum@keybiodiversityareas.org).
Main document: Terms of Reference of the KBA Consultative Forumiv

Guidelines on Business and KBAs: Managing Risk to Biodiversity

FOREWORD
The destruction, degradation, and overexploitation of natural habitats is leading to a rapid loss of
biodiversity, jeopardising the ecosystem services upon which human society depends. To halt thistrend, it is vital to know which places on the planet make particularly significant contributions to theglobal persistence of biodiversity, so that we can facilitate management of these areas and ensurethat they continue to support their important species, ecosystems, and genetic diversity.
Responding to this need, IUCN’s WCPA-SSC Joint Task Force on Biodiversity and Protected Areas
led a multi-year consultation process to develop a set of globally standardised, quantitative criteria for
the identification of Key Biodiversity Areas (KBAs) worldwide. A Global Standard for the Identificationof Key Biodiversity Areas provides an overarching common framework for the identification of sitesthat contribute significantly to the global persistence of biodiversity. Since its launch at the IUCNWorld Conservation Congress in 2016, the KBA Standard has been an important step forward for
global biodiversity conservation. Building on this effort, 12 of the world’s leading nature conservation
organisations2 have launched an ambitious new Key Biodiversity Areas Partnership, to map, monitor,and conserve the most important places for life on earth.
The KBA Standard also offers a platform to reach out to the many key actors who have the ability toboth positively and negatively affect biodiversity conservation, in particular the business community.
Given that some business activities can have a significant role in driving biodiversity loss – forexample through land-use changes, pollution, or introduction of invasive species – stemming the
global biodiversity crisis requires mainstreaming best practices for mitigating biodiversity risks andimpacts into all facets of business operations.
The KBA Partners have embraced this challenge. For the past two years, we have worked to
distil key guidelines for supporting the effective management of biodiversity risks to KBAs that
may arise from business activities. The resulting 15 Guidelines on Business and KBAs reflect a
consensus among the KBA Partners on how to address challenging topics, such as avoidance of
impacts, biodiversity offsets in KBAs, financial guarantees, corporate reporting, and other criticalissues. These Guidelines are designed to help businesses, certification scheme operators, financial
institutions, civil society organisations, and public authorities develop policies and standards tomanage biodiversity risks in KBAs.
The process of developing these Guidelines has been at times quite challenging, as there are different
values at stake and a wide range of approaches to responsible land use. However, despite thesedifferences, we are united by our recognition of the urgency of changing the way we relate to nature.
Our hope is that companies will embed these Guidelines in their biodiversity policies, voluntarysustainability standards, financial safeguards, and regulations, thus creating a level playing field among
businesses and leading to more effective conservation of Key Biodiversity Areas around the world.
January 2018
The KBA Partners

2 BirdLife International, IUCN, Amphibian Survival Alliance, Conservation International, Critical Ecosystem Partnership Fund, Global Environment Facility,
Global Wildlife Conservation, NatureServe, Rainforest Trust, Royal Society for the Protection of Birds, WWF, Wildlife Conservation Society.

v

Guidelines on Business and KBAs: Managing Risk to Biodiversity

Acknowledgments
This document has been prepared by IUCN, based on the guidance and input provided by representatives of the
KBA Partners. This document also builds on the input provided by the participants to the End Users Consultation
workshop (held in Gland, Switzerland, 4–5 July 2016) and by the organisations that submitted comments during
the public consultation period (2 December 2016–17 March 2017).
The Tiffany & Co. Foundation supported the development of these guidelines as part of its Responsible Mining
Program. The Foundation values collaboration from civil society to help businesses, certification systems,
governments and others define and implement more responsible practices in order to protect Key Biodiversity
Areas worldwide.
These guidelines are recommended minimum requirements for business operations having direct, indirect, andcumulative impacts on a Key Biodiversity Area, unless the national or local law is more stringent, in which casethe law shall prevail.
The KBA Partners will collect feedback on this first version of the Guidelines and organise a revision within 5 years.

Terms used in defining KBAs
Key Biodiversity Areas (KBA) are sites contributing significantly to the global persistence of biodiversity1.
Biodiversity: Biodiversity is ‘the variability among living organisms from all sources including, inter alia, terrestrial,
marine and other aquatic ecosystems and the ecological complexes of which they are part; this includes diversity
within species, between species and of ecosystems’, according to the Convention on Biological Diversity (CBD)(UN 1992).
Contributing/Contribution: The contribution of a site to the global persistence of biodiversity depends on the
global distribution and the abundance of the biodiversity elements for which the site is important. Sites holding
biodiversity elements that are globally restricted, or at risk of disappearing, make high contributions to thepersistence of those elements. The global persistence of a biodiversity element occurring at any given KBA, unless
it is entirely confined to the site, depends not only on the fate of the site itself but also on that of other sites and of
the land-/seascapes where it occurs.
Global: Global implies that the contributions of a site to the persistence of a given biodiversity element aremeasured in relation to its worldwide population size or extent.
Persistence: Persistence of a biodiversity element means that its loss (e.g. species extinction, ecosystem collapse)
or decline (e.g. of numbers of mature individuals of a species, ecosystem extent and condition) is avoided, both
now and into the foreseeable future.
Significantly/Significant: Significant means that an outstanding proportion of a biodiversity element (e.g. species
population size or ecosystem extent) occurs at the site, as defined by a quantitative threshold.
Site: A geographical area on land and/or in water, with defined ecological, physical, administrative, or managementboundaries, that is actually or potentially manageable as a single unit (e.g. a protected area or other managed
conservation unit). For this reason, large-scale biogeographic regions such as ecoregions, Endemic Bird Areas
and Biodiversity Hotspots, and land-/seascapes containing multiple management units, are not considered to besites. In the context of KBAs, ‘site’ and ‘area’ are used interchangeably.
1 IUCN (2016). A Global Standard for the Identification of Key Biodiversity Areas, Version 1.0. First edition. Gland, Switzerland: IUCN.
https://portals.iucn.org/union/sites/union/files/doc/a_global_standard_for_the_identification_of_key_biodiversity_areas_final_web.pdf

viGuidelines on Business and KBAs: Managing Risk to Biodiversity

Glossary
Additional Conservation Actions: A broad range of activities that are intended to beneﬁt biodiversity, where
the effects or outcomes can be difficult to quantify. (Biodiversity A to Z )Avoidance: Measures taken to prevent impacts from occurring in the first place, for instance by changing or
adjusting the development project’s location and/or the scope, nature, and timing of its activities. (Glossary(2012), BBOP)
Baseline: A description of existing conditions to provide a starting point (e.g. pre-project condition of
biodiversity) against which comparisons can be made (e.g. post-impact condition of biodiversity), allowing thechange to be quantified. (Glossary (2012), BBOP)
Biological diversity: The variability among living organisms from all sources including, inter alia, terrestrial,
marine and other aquatic ecosystems and the ecological complexes of which they are part; this includes
diversity within species, between species and of ecosystems. (Convention on Biological Diversity, 1992)
Biological resources: The genetic resources, organisms or parts thereof, populations, or any other biotic
component of ecosystems with actual or potential use or value for humanity. (Convention on Biological
Diversity, 1992)
Biodiversity element: Genes, species, or ecosystems, as used by the Convention on Biological Diversity(CBD) definition of biodiversity. (A Global Standard for the Identification of Key Biodiversity Areas (2016), IUCN)
Biodiversity loss: Biodiversity loss is usually observed as one or all of: (1) reduced area occupied bypopulations, species, and community types, (2) loss of populations and the genetic diversity they contribute to
the whole species, and (3) reduced abundance (of populations and species) or condition (of communities andecosystems). The likelihood of any biodiversity component persisting (the persistence probability) in the longterm declines with lower abundance and genetic diversity and reduced habitat area. (Glossary (2012), BBOP)
Biodiversity offsets: Biodiversity offsets are measurable conservation outcomes resulting from actions
designed to compensate for significant residual adverse biodiversity impacts arising from project development
after appropriate mitigation measures have been taken. The goal of biodiversity offsets is to achieve no net loss
and preferably a net gain of biodiversity on the ground with respect to species composition, habitat structure,and ecosystem function, and people’s use and cultural values associated with biodiversity. (Glossary (2012),
BBOP)
Conservation outcome: A conservation outcome is the result of a conservation intervention aimed
at addressing direct threats to biodiversity or their underlying socio-political, cultural, and/or economic
causes. Conservation outcomes are typically in the form of: (a) extinctions avoided (i.e. outcomes thatlead to improvements in a species’ national or global threat status); (b) sites protected (i.e. outcomes thatlead to designation of a site as a formal or informal protection area, or to improvement in the management
effectiveness of an existing protected area); and (c) corridors created (i.e. outcomes that lead to the creationof interconnected networks of sites at the landscape scale, capable of maintaining intact biotic assemblages
and natural processes, and, thereby, enhancing the long-term viability of natural ecosystems). Conservation
outcomes would also include any other intervention that leads to conservation gains. (Glossary (2012), BBOP)
Critical habitat: A number of lending institutions have recently defined ‘critical habitat’, accompanied byconditions for clients whose projects may impact upon it. Common themes mentioned by these definitions
include threatened species, endemic or geographically restricted species, congregations of migratory andother species, assemblages that support key processes or services, and biodiversity of social, economic, or
cultural value. Examples of definitions include the following:vii

Guidelines on Business and KBAs: Managing Risk to Biodiversity

1. Critical habitats are areas with high biodiversity value, including (i) habitat of significant importanceto Critically Endangered and/or Endangered species; (ii) habitat of significant importance to endemic
and/or restricted-range species; (iii) habitat supporting globally significant concentrations of migratory
species and/or congregatory species; (iv) highly threatened and/or unique ecosystems; and/or (v)areas associated with key evolutionary processes. This definition adds in a footnote that ‘CriticallyEndangered and/or Endangered species’ are as listed on the International Union for the Conservationof Nature (IUCN) Red List of Threatened Species. The determination of critical habitat based onother listings is as follows: (i) If the species is listed nationally/regionally as critically endangered or
endangered, in countries that have adhered to IUCN guidance, the critical habitat determination will bemade on a project-by-project basis in consultation with competent professionals; and (ii) In instanceswhere nationally or regionally listed species’ categorisations do not correspond well to those of IUCN(e.g., some countries more generally list species as ‘protected’ or ‘restricted’), an assessment will
be conducted to determine the rationale and purpose of the listing. In this case, the critical habitat
determination will be based on such an assessment. (IFC Performance Standard 6, January 2012)
2. Irrespective of whether it is natural or modified, some habitat may be considered to be critical by virtueof (i) its high biodiversity value, (ii) its importance to the survival of endangered or critically endangered
species, (iii) its importance to endemic or geographically restricted species and sub-species, (iv) its
importance to migratory or congregatory species, (v) its role in supporting assemblages of species
associated with key evolutionary processes, (vi) its role in supporting biodiversity of significant social,economical, or cultural importance to local communities, or (vii) its importance to species that are vitalto the ecosystem as a whole (keystone species). (EBRD Environmental and Social Policy, 12 May 2008)
Cumulative impact: The total impact arising from the project (under the control of the developer); otheractivities (that may be under the control of others, including other developers, local communities, government),
and other background pressures and trends which may be unregulated. The project’s impact is therefore
one part of the total cumulative impact on the environment. The analysis of a project’s incremental impacts
combined with the effects of other projects can often give a more accurate understanding of the likely resultsof the project’s presence than just considering its impacts in isolation. (Glossary (2012), BBOP)
Direct impact: An outcome directly attributable to a defined action or project activity (often also called primary
impact). (Glossary (2012), BBOP)
Ecosystem: A dynamic complex of plant, animal and micro-organism communities and their non-living
environment interacting as a functional unit. (Convention on Biological Diversity, 1992)
Ecosystem services: The benefits people obtain from ecosystems. These include provisioning services suchas food, water, timber, and fibre; regulating services that affect climate, floods, disease, wastes, and water
quality; cultural services that provide recreational, aesthetic, and spiritual benefits; and supporting services
such as soil formation, photosynthesis, and nutrient cycling. (Glossary (2012), BBOP)
Go/No Go: The decision as to whether a project should proceed or not, usually taken by regulators and/or
companies prior to project inception and based on a complex dialogue involving a range of stakeholders andconcerns, of which impacts on biodiversity are only one. A ‘No Go’ decision may be taken because a project
is not suitable for reasons other than its impacts on biodiversity. Equally, a project with a very significant, nonoffsetable impact on biodiversity may still result in a ‘Go’ decision based on other benefits (such as needed
infrastructure, jobs, or development), considered to outweigh its environmental costs. (Glossary (2012), BBOP)
Habitat: The place or type of site where an organism or population naturally occurs. (Convention on Biological
Diversity, 1992)
High Conservation Value area: High Conservation Value areas are critical areas in a landscape which need
to be appropriately managed in order to maintain or enhance High Conservation Values (HCVs). There are six
main types of HCV area, based on the definition originally developed by the Forest Stewardship Council for
certification of forest ecosystems. (HCV Resource Network Charter (2015), HCV Resource Network)viii

Guidelines on Business and KBAs: Managing Risk to Biodiversity

Indirect impacts: Indirect impacts (sometimes called secondary impacts or induced impacts), are impacts
triggered in response to the presence of the project, rather than being directly caused by the project’s own
operations. For instance, the presence of a project such as an oil and gas facility may lead to an increased
local workforce and associated increases in demand for food. This may have knock-on effects on biodiversity,for example due to increased land conversion for farming or increased levels of hunting. Indirect impacts
may reach outside project boundaries and may begin before or extend beyond a project’s lifecycle. Indirect
impacts should be predicted with a thorough Environmental and Social Impact Assessment (ESIA) processthat includes biodiversity issues and explicitly links environmental and social issues, although there is a risk thatthe potential for such impacts may not be identified until later in the project cycle. As a general rule, indirect
impacts are more difficult to map and quantify than direct impacts. (Glossary (2012), BBOP)
Like-for-like or better: A common approach to biodiversity offsets is to require conservation (through thebiodiversity offset) of the same type of biodiversity as that affected by the project. This is known as ‘like-for-like’.
This is sometimes modified to ‘like-for-like or better’, in which the offset conserves components of biodiversitythat are a higher conservation priority (for example because they are more irreplaceable and vulnerable) thanthose affected by the development project for which the offset is envisaged. This is also known as ‘trading up’.
(Glossary (2012), BBOP)
Monitoring: Activities undertaken after the decision is made to adopt the plan, programme, or project toexamine its implementation. For example, monitoring to examine whether the significant environmental effects
occur as predicted or to establish whether mitigation measures are implemented. (Glossary (2012), BBOP)
No net loss/Net gain: A target for a development project in which the impacts on biodiversity caused by
the project are balanced or outweighed by measures taken to avoid and minimise the project’s impacts, toundertake on-site restoration, and finally to offset the residual impacts, so that no loss remains. Where thegain exceeds the loss, the term ‘net gain’ may be used instead of no net loss. No net loss (or net gain) of
biodiversity is a policy goal in several countries, and is also the goal of voluntary biodiversity offsets. (Glossary(2012), BBOP)
Protected area: A protected area is a clearly defined geographical space, recognised, dedicated, andmanaged, through legal or other effective means, to achieve the long-term conservation of nature withassociated ecosystem services and cultural values. (Guidelines for Appling Protected Areas Management
Categories (2008), IUCN)
Residual impact: The remaining adverse impact on biodiversity after appropriate avoidance, minimisation,and rehabilitation measures have been taken according to the mitigation hierarchy. (Glossary (2012), BBOP)
Restoration: The process of assisting the recovery of an area or ecosystem that has been degraded, damaged,
or destroyed. The aim of ecological restoration is to re-establish the ecosystem’s composition, structure, andfunction, usually bringing it back to its original (pre-disturbance) state or to a healthy state close to the original.
An ecosystem is restored when it contains sufficient biotic and abiotic resources to sustain itself structurally
and functionally and can continue its development without further assistance or subsidy. It will demonstrate
resilience to normal ranges of environmental stress and disturbance and interact with contiguous ecosystems
in terms of biotic and abiotic flows and cultural interactions. Ecological restoration strives to alter the biota andphysical conditions at a site, and is frequently confused with rehabilitation. While restoration aims to return anecosystem to a former natural condition, rehabilitation implies putting the landscape to a new or altered use
to serve a particular human purpose. Activities such as ecological engineering and various kinds of resource
management, including wildlife, fisheries and range management, agroforestry, and forestry may qualify as
ecological restoration if they satisfy the criteria set out by the Society for Ecological Restoration. This Society
lists nine attributes as a basis for determining when restoration has been accomplished. (Society for Ecological
Restoration)
Thresholds: Numeric or percentage minima which determine whether the presence of a biodiversity element
at a site is significant enough for the site to be considered a KBA under a given criterion or sub-criterion.
(A Global Standard for the Identification of Key Biodiversity Areas (2016), IUCN)

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Guidelines on Business and KBAs: Managing Risk to Biodiversity

Trading up: Conserving, through an offset, components of biodiversity that are a higher conservation priority(for example because they are more irreplaceable and vulnerable) than those affected by the development
project for which the offset is envisaged. (Glossary (2012), BBOP)
Trigger: A biodiversity element (e.g. species or ecosystem) by which at least one KBA criterion and associatedthreshold is met. (A Global Standard for the Identification of Key Biodiversity Areas (2016), IUCN)x

Guidelines on Business and KBAs: Managing Risk to Biodiversity

EXECUTIVE SUMMARY
Biodiversity3 underpins the capacity of nature to function and deliver the ecosystem goods and services
upon which the world depends. Yet, biodiversity is being lost at an alarming rate across the world’s
terrestrial, freshwater, and marine biomes, and current rates of extinction are about 1,000 times the likely
background rate. Evidence is mounting that the loss of genes, species, and ecosystems – a crisis in its
own right -- jeopardises the delivery of services provided by biodiversity to human communities. Reversing
this trend requires slowing and eventually stopping the destruction, degradation, and overexploitation ofnatural habitats and, where appropriate, restoring these habitats.
One of the most effective ways to safeguard biodiversity is through conservation of sites that have highbiodiversity value. Knowing, with precision, the location of those places that contribute significantly to
the global persistence of biodiversity is therefore critical information for a wide range of end users acrosssociety, from national decision makers to private companies, as well as for use by international conventions
and, ultimately, to direct conservation actions to halt further losses and address existing and emerging
threats. The identification of Key Biodiversity Areas (KBAs), which are ‘sites contributing significantly
to the global persistence of biodiversity’, is an important step towards more effective management of
biodiversity.
Recognising that KBAs often include areas that are commercially productive (e.g. cultivated areas,
managed forests, fisheries, mineral sites), it is important that businesses take action to influence how suchareas are managed, either directly through their operations or indirectly through their supply chains. When
operating in and around, or sourcing from, areas within KBAs (and/or within proximity of KBAs, potentiallycausing impacts), businesses can benefit from guidelines that facilitate their management decisions, inorder to maintain the biodiversity values for which the KBA has been identified.
These Guidelines on Business and KBAs have been developed by the KBA Partners to support businesses
in managing risk to biodiversity. They will be of use to business and certification scheme operators, financial
institutions, civil society organisations, and public authorities in numerous situations, such as:
1. implementing the mitigation hierarchy for managing biodiversity risks associated with operations
impacting biodiversity for which the KBA is important;
2. implementing international financial institutions’ safeguards and environmental standards (see Box 1)
for projects affecting biodiversity for which the KBA is important;
3. designing and reviewing sustainability standards, including for certification systems and project finance;
4. setting the permitting requirements for business operations having a potential impact on biodiversity
for which the KBA is important;
5. guiding and informing engagements between civil society organisations and business entities; and6. public reporting, including the Global Reporting Initiative (GRI) for sustainability reporting.
These Guidelines can be applied by businesses of all sizes and in all sectors, and by existing and new
businesses having direct, indirect, and cumulative impacts on a KBA. They are applicable to the businesses’
entire area of influence, as well as throughout the life cycle of the operation, from pre-feasibility to closure (and,where relevant, site rehabilitation). The Guidelines can also be integrated into responsible sourcing policies forgoods and services, the production of which could have direct, indirect, and cumulative impacts on KBAs.
To support the implementation of the Guidelines, a section of the KBA website dedicated to Business andKBAs provides additional information that can make each of the Guidelines more actionable. It includes links
to existing resources and examples from field projects.

3Convention on Biological Diversity (1992), Article 2

xiGuidelines on Business and KBAs: Managing Risk to Biodiversity

Box 1. International financial institutions’ safeguard policies andenvironmental standards
A number of safeguard policies and environmental standards have been established to inform decisions
on allocation of resources for development and ensure sustainability in the lending and project-granting
processes. These include safeguard policies from development banks, such as the World Bank
Environmental and Social Framework, the Asian Development Bank (ADB) Safeguard Policy Statement,
the Inter-American Development Bank (IDB) Environment and Safeguards Compliance Policy, and theEuropean Bank for Reconstruction and Development (EBRD) Environmental and Social Policy, as wellas the Organisation for Economic Co-operation and Development (OECD) Environmental and Social
Due Diligence policy. There are also safeguards from private sector financial bodies, such as the Equator
Principles Association, and the Sustainability Framework of the International Finance Corporation (IFC),
which is part of the World Bank Group. IFC’s Performance Standard 6 (PS6) on Biodiversity Conservationand Sustainable Management of Living Natural Resources is fast becoming a global benchmark forcorporate best practice in relation to biodiversity. Critical habitats and natural habitats as defined in IFC
PS6 are terms used by many other safeguard policies to describe habitats that are either especiallysensitive to impacts or of high biodiversity significance. Because the criteria used to identify critical
habitats and the KBA criteria are closely aligned, KBAs can be considered candidates to be classified as
critical or natural habitats, and their use is specifically recommended in IFC PS6.

It is also critical to recognise that the business community can play a positive role in the conservation of KBAs,
by supporting the World Database of Key Biodiversity AreasTM, sharing biodiversity data collected during thevarious stages of a project’s operations, and financing the conservation of KBAs, either through philanthropic/
corporate social responsibility initiatives or offsets within KBAs for the residual impacts from other sites.
Finally, the effective management of a Key Biodiversity Area will only result from the joint efforts of actors thatare directly and indirectly responsible for impacting the area. These actors include businesses with operations
that directly or indirectly affect the area, as well as regulators who are responsible for setting land-use plans andperformance requirements for the various users, local communities that are directly or indirectly conserving or
affecting the area, and civil society organisations engaged in its conservation and development. The successfulconservation of the biodiversity for which the KBA is important will depend on the participation, collaboration,and contributions of all these actors.

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Guidelines on Business and KBAs: Managing Risk to Biodiversity

1. BUSINESS AND KBAs
Risks and opportunities for biodiversity… Increasing consumption rates and population growth, combinedwith unsustainable production patterns, play a major role in the dramatic loss of biodiversity, driven by land-use
change, climate change, invasive species, overexploitation of natural resources, and pollution. The reversal ofthe direct relationship between economic growth and biodiversity loss has been and is still at the centre ofmany public policies and conservation organisations’ initiatives. Reversing this trend is even more importantin areas that have been identified as critical for the global persistence of biodiversity. The paradigm in whichbusiness operations are the source of impacts can be turned around and transformed into a system in whichbusiness operations generate biodiversity conservation gains through their operations and funding.
…and for people. As the degradation of ecosystem services, underpinned by biodiversity, has a direct
impact on people, the value of biodiversity for people should be at the centre of KBA conservation strategies.
Much of the world’s biodiversity can be found in the lands and territories of indigenous peoples and local
communities, and has been and continues to be actively conserved by them. The loss of biodiversity hasoften disproportionately affected indigenous peoples and local communities across the world, with many ofthem dependent on natural ecosystems and the ecosystem services provided for their cultural, social, andeconomic well-being. Their cultures, identities, and physical survival as distinct peoples are sustained by lands
and territories; in many cases habitat loss and reduced access to resources has led to scarcity of livelihood
materials, decreasing food security, poor nutrition, ill health, severe hardship, and an increased risk of floods
and soil instability. Indigenous and local communities play an essential role in conserving biodiversity, and inmany cases community area-based conservation has proven to be more effective than conventional protectedarea management.
Business as a positive force for the conservation of KBAs. Businesses and other relevant actors cangreatly contribute to the conservation of the biodiversity for which the KBA is important in a number of ways,
including but not limited to:•

Making available to civil society and the scientific community the information gathered during theirproject and biodiversity management operations, including the data collected during the risk and impact
assessments and the monitoring operations. This will be particularly important if the assessments
conducted by the business show that the biodiversity values have already been degraded.

•

Prioritising KBAs as the target of philanthropic and corporate social responsibility initiatives. This will
generally ensure great visibility for the donors by providing a narrative based on an internationallyrecognised identification.

•

Prioritising KBAs as recipients of offsets to compensate residual impacts in non-KBA sites, where thisdoesn’t affect compensation for significant losses of other nationally or regionally important biodiversity
or ecosystems. This approach could lead to investing in an area with an opportunity for greater
conservation impact than the one affected by the project for which the offset is envisaged. This would
provide the opportunity for businesses to invest in offsets that would achieve better conservation
outcomes, effectively ‘trading up’ the net outcomes.

1Guidelines on Business and KBAs: Managing Risk to Biodiversity

2. MORE ABOUT KBAs
A strengthened approach to the conservation of global biodiversity. One of the most effective ways
to safeguard biodiversity is through conservation of sites that have high biodiversity value. Knowing, with
precision, the location of those places that contribute significantly to the global persistence of biodiversity
is therefore critical information for a wide range of end users across society, from national decision makers
and international conventions to private companies and local communities, ultimately, to direct conservation
actions to halt further losses and address existing and emerging threats4. The identification of Key Biodiversity
Areas, which are ‘sites contributing significantly to the global persistence of biodiversity’, is an important step
towards more effective management of biodiversity.
A global standard for identifying sites of biodiversity importance. A Global Standard for the Identificationof Key Biodiversity Areas, hereafter the ‘KBA Standard’, was adopted by IUCN in April 2016 and launchedat the 2016 IUCN World Conservation Congress. The KBA Standard establishes a consultative, sciencebased process for site identification, founded on the consistent application of global criteria with quantitative
thresholds that have been developed through an extensive consultation exercise spanning several years. It
builds on existing approaches to the identification of important sites for biodiversity, such as Important Bird andBiodiversity Areas and Alliance for Zero Extinction sites. The KBA criteria encompass threatened biodiversity,
geographically restricted biodiversity, ecological integrity, biological processes, and irreplaceability, and areapplicable to species and ecosystems in terrestrial, inland water, and marine environments.
Some facts about KBAs. As in nature, diversity is what defines the areas identified to date as Key Biodiversity
Areas. To illustrate this, consider:• Total number of KBAs: 15,861• Average size: 1,283.4 sq km• Smallest: 0.01 sq km (There are several this size, mostly ponds or small breeding colonies.)• Largest: 905,664 sq km (Proposed Central Pacific World Heritage Site, Kiribati)• Mean percentage area of each KBA covered by protected areas: 46%• Percent of KBAs wholly covered (i.e. >98%) by protected areas: 25%
Defining the boundaries of KBAs. Delineation is the process through which the boundaries of a KBA are
drawn on a map. It is possible that a KBA may sometimes be smaller than the area of continuous habitat
supporting a trigger species, for example if the habitat covers a protected area and also habitat outside, but
for reasons of manageability, only the protected area portion is designated as a KBA. The KBA may also belarger than the area in which the trigger biodiversity element occurs, for example if that area is entirely within alarger protected area or some other management boundary.
The World Database of Key Biodiversity AreasTM. The World Database of Key Biodiversity AreasTM,
managed by BirdLife International on behalf of the KBA Partnership, includes an interactive online map of
KBAs with links to documentation for each site. In addition, KBA shapefiles are available on request for noncommercial use and are currently provided via the Integrated Biodiversity Assessment Tool (see Box 2). Thesesites will be re-assessed over time against the new KBA Standard. In addition, new sites will be identified asadditional taxonomic groups and ecosystems are considered and all criteria in the KBA Standard are applied.

4 Dudley, N., Boucher, J.L., Cuttelod, A., Brooks, T.M., and Langhammer, P.F. (Eds). 2014. Applications of Key Biodiversity Areas: end-user consultations.
Cambridge, UK and Gland, Switzerland: IUCN.

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Guidelines on Business and KBAs: Managing Risk to Biodiversity

Key Biodiversity Areas, protected areas, and conservation priorities. As clarified in the KBA Standard,
KBAs are sites of importance for the global persistence of biodiversity. However, this does not imply that a
specific conservation action, such as protected area designation, is required. KBAs may or may not receive
formal protection, but they should be managed in ways that ensure the persistence of the biodiversity elements
for which they are important. Such management decisions should be based on conservation priority-setting
exercises, which typically combine data on biodiversity importance with available information on sitevulnerability and management actions needed to safeguard the biodiversity for which the site is important.

Box 2. The Integrated Biodiversity Assessment Tool (IBAT)
For commercial use, the data in the World Database of Key Biodiversity AreasTM can be accessed throughthe Integrated Biodiversity Assessment Tool (IBAT) at www.ibat-alliance.org. IBAT is a partnership between
BirdLife International, Conservation International, IUCN, and the UN Environment World Conservation
Monitoring Centre (UNEP-WCMC). It is an online tool designed to facilitate access to currently identified
KBAs, the World Database on Protected Areas, and the IUCN Red List of Threatened SpeciesTM,
combined with other relevant ecological datasets. All information can be accessed through a simple
user interface that allows users to display dynamic georeferenced maps and submit specific queries.
IBAT helps businesses incorporate biodiversity considerations into key project planning and management
decisions, including screening potential investments, siting an operation in a given region, developing
action plans to manage biodiversity impacts, assessing risks associated with potential sourcing regions,and reporting on corporate biodiversity performance.

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Guidelines on Business and KBAs: Managing Risk to Biodiversity

3. GUIDELINES FOR BUSINESSACTIVITIESApplicability. The Guidelines can be applied by businesses of all sizes and in all sectors, and by existingand new business operations having, and potentially having, direct, indirect, and cumulative impacts on a
Key Biodiversity Area. They are designed assuming their application to the businesses’ area of influence (seeBox 3) and to the entire life cycle of the operation, from pre-feasibility to closure (and, where relevant, site
rehabilitation). The Guidelines can also be integrated into responsible sourcing policies for goods and services,the production of which could have direct, indirect, and cumulative impacts on KBAs.

Box 3. Area of Influence
A business operation’s area of influence encompasses, as appropriate:•••

The area likely to be affected by: (i) the project and the business’s activities and facilities thatare directly owned, operated, or managed (including by contractors) and that are a componentof the project; (ii) impacts from unplanned but predictable developments caused by the projectthat may occur later or at a different location; or (iii) indirect project impacts on biodiversity or on
ecosystem services upon which affected communities’ livelihoods are dependent.
Associated facilities, which are facilities that are not funded as part of the project, that would nothave been constructed or expanded if the project did not exist, and without which the project
would not be viable.
Cumulative impacts that result from the incremental impact, on areas or resources used or directly
impacted by the project, from other existing, planned, or reasonably defined developments at thetime the risks and impacts identification process is conducted.

Source: International Finance Corporation’s Policy on Environmental and Social Sustainability (2012)

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Guidelines on Business and KBAs: Managing Risk to Biodiversity

Conditions for successful implementation. A number of factors can contribute to the successful
implementation of the Guidelines, including:•

The various stages of the mitigation hierarchy and these Guidelines are designed and implemented in
the context of a changing environment, in particular in light of the effects of climate change.

•

KBAs are subject to different governance models. It is vital that these Guidelines are contextualised
appropriately in each situation, taking into consideration formal and informal governance arrangements,
land and natural resource tenure and rights, and the needs and rights of local communities and/orindigenous peoples living in or around the KBA.

•

If a KBA is designated as a protected area, when implementing the mitigation hierarchy, the businesstakes into consideration zoning, management plans, and legal restrictions set by the relevant authorities.

•

The establishment of an inclusive and transparent stakeholder and right-holder engagement process(including, for example, representatives of national, regional, and local government; indigenous
peoples; local communities; and other elements of civil society) in planning and decision making is
recommended. International best practices for stakeholder and right-holder engagement, including arights-based approach and Free, Prior, and Informed Consent (FPIC) for engaging with indigenous andtraditional peoples and local communities, are implemented as early as possible in the project cycleand follow recognised best practices.

•

Where indigenous peoples and local communities live in or near a KBA, their engagement in restorationand offset activities is prioritised, not only to increase the likelihood of successful and socially acceptable
remediation results, but also to provide important socio-economic benefits to communities.

•

Where possible, indigenous and local knowledge is included alongside the sciences, as complementary
systems of knowledge for achieving a fuller and richer understanding of biodiversity values, functioning,
status, and trends, as well as the consequences of its loss at different scales. For example, traditional
knowledge can provide many contributions to ecological restoration, including through the constructionof reference ecosystems (particularly when historical information is not available), input into species
and site selection for restoration activities, knowledge of historical land-management practices, input
into management of invasive species, and post-restoration monitoring.

Access to data on Key Biodiversity Areas for commercial use. All commercial users of these Guidelines
should access data on Key Biodiversity Areas through IBAT for Business. Commercial use means any use by,on behalf of, or to inform or assist the activities of, a commercial entity (an entity that operates ‘for profit’), or
use by any individual or non-profit entity for the purposes of revenue generation.
A web site to support the implementation of the Guidelines. To support the implementation of the
Guidelines, a section of the KBA website dedicated to Business and KBAs provides additional information thatcan make each of the Guidelines more actionable. It includes links to existing resources and examples fromfield projects. A Questions & Answers section also supports quick access to common questions and concerns.
The information will be regularly updated and supplemented by new examples from business in using theguidelines, building in particular on the experience acquired by the KBA Partners in using the Guidelines.

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Guidelines on Business and KBAs: Managing Risk to Biodiversity

Project-level Guidelines
The KBA Partners recommend the application of the mitigation hierarchy (see Box 4) to any project with direct,
indirect, or cumulative impacts on biodiversity. Furthermore, to support the effective implementation of thevarious steps in the mitigation hierarchy, the KBA Partners recommend the adoption of additional measures
specifically aimed at ensuring the global persistence of biodiversity in line with the purpose of the KBA Standard,
which is to locate and highlight sites that make significant contributions to the global persistence of biodiversity.

Box 4. The Mitigation Hierarchy
The mitigation hierarchy is a framework for addressing project impacts, defined as:
1. Avoidance: measures taken to avoid creating impacts from the outset, such as careful spatialor temporal placement of elements of infrastructure in order to completely avoid impacts on
certain components of biodiversity.
2. Minimisation: measures taken to reduce the duration, intensity, and/or extent of impacts,
including, as appropriate, direct, indirect, and cumulative impacts (including from climatechange), that cannot be completely avoided, as far as is practically feasible.
3. Rehabilitation/restoration: measures taken to rehabilitate degraded ecosystems or restore
cleared ecosystems following exposure to impacts that cannot be completely avoided and/or
minimised.
4. Offset: measures taken to compensate for any residual significant, adverse impacts that cannot
be avoided, minimised, and/or rehabilitated or restored, in order to achieve no net loss or a net
gain of biodiversity. Offsets can take the form of positive management interventions, such as
restoration of degraded habitat or arrested degradation, or averted risk through protection ofareas where there is imminent or projected loss of biodiversity. Offsets should only be consideredafter following the first three steps of the mitigation hierarchy to further reduce residual impacts.
Source: Glossary (2012), Business and Biodiversity Offset Programme

1

Project biodiversity baseline. Potential residual impacts of a project are determined against
a baseline representing the pre-project condition of the biodiversity element(s) for which thesite qualifies as a KBA (including the supporting ecological context).
How can the World Database of Key Biodiversity AreasTM help?
The World Database of Key Biodiversity AreasTM can be used to
identify the trigger biodiversity element(s) that need to be assessed aspart of the baseline studies. In addition, information on existing threats
would also help in completing the study.

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Guidelines on Business and KBAs: Managing Risk to Biodiversity

2

Priority to avoidance. All forms of avoidance are prioritised (see Box 4), including notproceeding with project development where it is likely that negative impacts on the biodiversity
elements triggering the identification of the KBA will occur, or relocating the project to othersites, prioritising, where relevant, already degraded areas. As established by IUCN Members, certain
activities should be avoided in KBAs, including environmentally damaging industrial activities andinfrastructure (WCC-2016-Rec-102), oil palm plantations (WCC-2016-Res-061), and activities thatwould lead to the loss of primary forest (WCC-2016-Res-045).
How can the World Database of Key Biodiversity AreasTM help?
The identification of sensitive areas during screening processes andbaseline surveys is of critical importance. The World Database of Key
Biodiversity AreasTM can be used to show where existing or future
project sites, operations, and supply chains are located in relation to
KBAs. The World Database of Key Biodiversity AreasTM can also help
indicate the relative importance of the site for the persistence of thetrigger elements (for example, if the site is home to a high percentageof the global population of a species). Furthermore, measures andplans may be designed to minimise impacts on KBAs in or neara concession or across a supply chain by focusing on specificbiodiversity elements for which that KBA was identified.

3

Implementation of early minimisation. For the biodiversity element(s) for which the KBA
has been identified, minimisation measures are adopted as early as possible, even before thedisturbance occurs.
How can the World Database of Key Biodiversity AreasTM help?
The World Database of Key Biodiversity AreasTM can help identify
existing threats to the biodiversity trigger elements that could be
worsened by the project’s impacts. Furthermore, information on
the behaviour and ecology of the trigger elements can help identify
effective minimisation measures.

4

Limits to impact restoration. Where it is not possible to avoid and minimise all impacts,
the feasibility of ecological restoration is determined, with particular consideration given to thebiodiversity elements for which the site is identified as a KBA (as documented in the World
Database of Key Biodiversity AreasTM), and restoration is conducted where it is ecologicallyfeasible. A precautionary approach to ecological restoration should be applied, particularly when
predicting restoration success as part of residual impact estimates. Empirical expert advice and best
available scientific evidence is essential to determine the feasibility and effectiveness of restoration plans.
Furthermore, it is recommended that the limits to offsets established by the IUCN Policy on Biodiversity
Offsets (see Box 5) should also apply to the restoration of the project’s impact, and that the restoration
potential, including in the light of climate change, is demonstrated before project activities commence.
How can the World Database of Key Biodiversity AreasTM help?
The World Database of Key Biodiversity AreasTM can be used to
identify which habitat types occur in the KBA, to help focus additional
research on restoration success for those habitat types in other KBAs
and sites.

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Guidelines on Business and KBAs: Managing Risk to Biodiversity

5

Limits to biodiversity offsets. Offsets to address unavoidable residual impacts in KBAs
should follow the IUCN Policy on Biodiversity Offsets. In addition to the limits to biodiversity
offsets articulated in the IUCN Policy (see Box 5), and given the importance of KBAs for the
global persistence of biodiversity, the following additional guidelines are suggested when
the residual impacts affect the biodiversity element(s) triggering the identification of the KBA:
•

•
•

•

Offsets for residual impacts in KBAs should achieve Net Gain on the trigger element(s)affected by the project, such that the element(s) is highly likely to persist in the light ofclimate change and governance instability.
Offset gains should be achieved before impacts occur, or, where offset gains may taketime to achieve, offsets should be initiated with clear financing before impacts occur.
Offsets should not be used where residual impacts on biodiversity are likely to leadto a site no longer meeting the KBA criteria for any of its trigger elements, except in
exceptional circumstances when the offset will demonstrably generate significant gains
in the global persistence of each of these elements that exceeds the loss caused by
the residual impact.
The development and offset should both have obtained the free, prior, and informed
consent of any impacted local communities.

How can the World Database of Key Biodiversity AreasTM help?
The World Database of Key Biodiversity Areas can help in theidentification of potential offsets by offering information on the
population size or geographic extent of the trigger elements at
the impacted KBA and other KBAs, and the threats facing thoseelements.

Box 5. Limits to biodiversity offsets, according to the IUCN Policy on
Biodiversity Offsets
The IUCN Policy on Biodiversity Offsets states that ‘In certain circumstances residual impacts on
biodiversity (after completing the avoidance, minimisation and rehabilitation steps of the mitigation
hierarchy) cannot be offset. Additionally, there are some components of biodiversity for which impacts
could theoretically be offset, but with a high risk of failure. Under these circumstances, biodiversity offsets
are not appropriate, and this means that the project as designed should not proceed.’
The policy then lists the minimum circumstances in which offsets should not be considered. Particularly
relevant to the case of KBAs are situations where:••

8

impacts are likely to lead to a high risk of driving one or more previously non-threatened species
and/or ecosystems into the IUCN Red List Categories of Vulnerable, Endangered, CriticallyEndangered, Extinct in the Wild, or Extinct; or driving one or more previously threatened species
and/or ecosystems into IUCN Red List Categories of higher threat; orthe values that will be lost are specific to a particular place, and therefore cannot be foundelsewhere and adequately protected or re-created.

Guidelines on Business and KBAs: Managing Risk to Biodiversity

6

Biodiversity impact monitoring. In implementing the monitoring plan, it is crucial that:
•

•

•

•

the biodiversity elements that have triggered the KBA identification are included in themonitoring plan (even if these elements have not been highlighted as areas of concern
in the impact assessment);
the business monitoring system is aligned with and contributes to the KBA-widemonitoring efforts, if present, and, where KBAs are in or near indigenous peoples’or local communities’ lands and territories, community-based monitoring of KBAs is
supported;the data collected during the monitoring activities are made available to the KBA
Partners and included in the KBA database, consistent with the Red List Policy on
sensitive data access; andthe results of the monitoring are publicly disclosed, with considerations for confidential
information.
How can the World Database of Key Biodiversity AreasTM help?
The World Database of Key Biodiversity AreasTM can be used to
identify those biodiversity elements, that should be regularly monitored
and provides information on the population size or geographic extent
of trigger elements prior to project impacts.

78
9Long-term financing of the mitigation measures. Sustainable and sufficient financing forthe implementation of all the mitigation measures5 resulting from business operations in KBAs
throughout the project life cycle is secured from the outset of the operations.

Responsibilities in case of divestment. The ongoing actions and commitments are passed
on to new owners in case of divestment.

Participation and consultation. Those institutions, organisations, communities, and people
involved in the identification of the KBA should be consulted. Furthermore, decision-making
processes should be transparent.

10

Responsibility for existing operations. Additional conservation actions that will leadto conservation benefits for the biodiversity element(s) triggering the KBA identification
should be implemented to make up for the impacts generated by operations that started
before the identification of the KBA or before these guidelines were issued. Impacts
linked to extensions of the project and future operations should be managed according to the mitigation
hierarchy and Guidelines 1 to 9.

5 For specific recommendations related to financing of offsets, see the IUCN Offset Policy. https://portals.iucn.org/library/sites/library/files/resrecfiles/
WCC_2016_RES_059_EN.pdf

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Guidelines on Business and KBAs: Managing Risk to Biodiversity

Corporate-level Guidelines
The KBA Partners recommend the following additional Guidelines at the corporate/group level:

11

Reporting on KBAs as part of the company’s environmental performance. KBAs
can inform and support reporting in accordance with the Global Reporting Initiative, inparticular GRI 304 on Biodiversity (one of the topic-specific Standards in the 300 series- Environmental topics).
How can the World Database of Key Biodiversity AreasTM help?
Comparing a map of the company’s projects and conservation
initiatives against the distribution of KBAs is the basis for a more
powerful report on biodiversity. In particular:
a. Disclosure 304-1 Operational sites owned, leased,managed in, or adjacent to, protected areas andareas of high biodiversity value outside protectedareas: The reporting organisation could highlight which
operational sites are in or adjacent to KBAs.
b. Disclosure 304-2 Significant impacts of activities,
products, and services on biodiversity: The reportingorganisation could organise its narrative about its impacts
by type of areas, highlighting when these impacts occur
in KBAs.
c. Disclosure 304-3 Habitats protected or restored:
The reporting organisation could highlight which of thehabitats protected or restored are in KBAs.

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Additional conservation actions. Often, businesses seek to invest in conservationinterventions for features above and beyond those impacted by their own activities. This
could be because there is geographic proximity between the company and the KBA, forexample, or some connection between the company and the biodiversity elements forwhich a given KBA is important. Actions to safeguard the biodiversity for which a given KBA is important
therefore provide a highly desirable focus for such corporate social responsibility.
How can the World Database of Key Biodiversity AreasTM help?
The World Database of Key Biodiversity AreasTM provides spatial dataon the location of KBAs (which could be compared to, for instance,
the locations of a business’s headquarters, key points in its supply
chain, or its major markets) and tabular data on the biodiversity forwhich the site is important (which could be searched for, say, species
represented in a business’s name or logo). Once KBAs where abusiness is interested in focusing such corporate social responsibility
have been identified, the documentation of conservation actions‘ongoing’ or ‘required’ at each of these KBAs can guide what kind ofactions would be most appropriate for such investment.

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Guidelines on Business and KBAs: Managing Risk to Biodiversity

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KBAs as targets for offsetting impacts elsewhere. Selecting KBAs as recipients ofoffsets to compensate residual impacts in non-KBA sites could possibly lead to investingin an area with an opportunity for greater conservation impact than the one affected by
the project for which the offset is envisaged. This would open an opportunity for the business to invest
in offsets that would achieve better conservation outcomes, effectively ‘trading up’ the net outcomes.
However, such ‘trading up’ should not cross national boundaries where doing so is legally, politically, or
socially unacceptable.
How can the World Database of Key Biodiversity AreasTM help?
The World Database of Key Biodiversity AreasTM can provide
information on potential offset locations in KBAs that provide asimilar or even more significant contribution to the global persistenceof biodiversity elements than the area that is impacted by a given
development (not occurring in a KBA).

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Sharing biodiversity data. The business can play a critical role in supporting the World
Database of Key Biodiversity AreasTM by sharing relevant data with the KBA Partners,
consistent with the Red List Policy on sensitive data access. In particular, the datacollected during Environmental Impact Assessment processes, baseline studies, andmonitoring activities can add great richness to the database.

Compliance with certification schemes and financial institutions’ safeguard
policies. Reviewing the presence of a business’ operations in KBAs will help assess
compliance with voluntary sustainability standards and financial institutions’ safeguard
policies, which often require consideration of impacts on areas of high biodiversity value,such as KBAs.
How can the World Database of Key Biodiversity AreasTM help?
The World Database of Key Biodiversity AreasTM can provide relevant
input for the identification of critical habitats, which is required by mostfinancial institutions’ safeguard policies, and of High Conservation
Value Areas, which are often included in sustainability standards forcertification processes.

11Guidelines on Business and KBAs: Managing Risk to Biodiversity

RESOURCESA Cross-Sector Guide for Implementing the Mitigation Hierarchy (2015), Cross Sector Biodiversity Initiative.
http://www.csbi.org.uk/wp-content/uploads/2015/09/CSBI-Mitigation-Hierarchy-Guide-Sept-2015-1.pdf
BBOP Standard on Biodiversity Offsets and associated material.
http://bbop.forest-trends.org/pages/guidelines
Biodiversity for Business: A guide to using knowledge products delivered through IUCN (2014), IUCN.
https://portals.iucn.org/library/sites/library/files/documents/2014-004.pdf
Biodiversity offsets technical study paper (2014), IUCN.
https://portals.iucn.org/library/sites/library/files/documents/2014-044.pdf
CSBI Timeline Tool (2013), Cross Sector Biodiversity Initiative.
http://www.csbi.org.uk/wp-content/uploads/2015/12/csbi_timeline_tool_jan_2014.pdf
Free, Prior and Informed Consent Guide for RSPO members (2015), RSPO.
http://www.rspo.org/news-and-events/announcements/free-prior-and-informed-consent-guide-for-rspomembers-2015-endorsed#
A Global Standard for the Identification of Key Biodiversity Areas (2016), IUCN.
https://portals.iucn.org/union/sites/union/files/doc/a_global_standard_for_the_identification_of_key_
biodiversity_areas_final_web.pdf
Good Practices for the Collection of Biodiversity Baseline Data (2015), Cross Sector Biodiversity Initiative.
http://www.csbi.org.uk/wp-content/uploads/2015/07/Biodiversity_Baseline_JULY_4a-2.pdf
Guidelines for the appropriate use of the IUCN Red List for business (2016), IUCN.
https://cmsdocs.s3.amazonaws.com/keydocuments/Guidelines_for_Appropriate_Use_of_IUCN_Red_List_
for_Business_ver1.pdf
How to do. Seeking free, prior and informed consent in IFAD investment projects (2015), IFAD.
https://www.ifad.org/documents/10180/beec86e1-270d-45a1-8786-4b749c9db733
IUCN Policy on Biodiversity Offsets (2016), IUCN.
https://portals.iucn.org/library/sites/library/files/resrecfiles/WCC_2016_RES_059_EN.pdf
IUCN Review protocol for biodiversity net gain (2017), IUCN.
https://portals.iucn.org/library/sites/library/files/documents/2017-033_0.pdf
Performance Standard 6 Biodiversity Conservation and Sustainable Management of Living Natural
Resources (2012), International Finance Corporation (IFC).
http://www.ifc.org/wps/wcm/connect/bff0a28049a790d6b835faa8c6a8312a/PS6_English_2012.
pdf?MOD=AJPERES
Strengthening implementation of the mitigation hierarchy: managing biodiversity risk for conservation
gains (2015), Cambridge Conservation Initiative – Collaborative Fund Project Report compiled by: BirdLife
International, UNEP-WCMC, RSPB, FFI, and the University of Cambridge.
http://www.birdlife.org/sites/default/files/attachments/cci_report_-_managing_risk_for_conservation_gains_-_
final_-_june_9th_2015.pdf
Technical conditions for positive outcomes from biodiversity offsets: an input paper for the IUCN TechnicalStudy Group on Biodiversity Offsets (2014), IUCN.
https://portals.iucn.org/library/sites/library/files/documents/2014-027.pdf

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