ISBN 978-4-905304-86-9

ANNEX
Vol. 6
Environmental Safeguards
TAKUYA FURUKAWA, MAKOTO EHARA & KIMIKO OKABE

Research achievement of the 4th mid-term plan 12 (Forest Management Technology-11)

Preface
The basic concept of REDD-plus is to provide economic incentives such as funding andcredits to developing countries for REDD activities (reducing emissions from deforestationand forest degradation) and “plus” activities (reducing CO2 emissions and CO2 levels in
the atmosphere by carbon sequestration). Thus, to estimate changes in the amount ofcarbon stored in forests, monitoring using a scientific approach is essential. Additionally,
the international community has agreed on promoting and supporting “safeguards” toprevent possible adverse impacts on the environment and society resulting from REDD-plus
activities.
The REDD Research and Development Center published an easy-to-understandtechnical manual “REDD-plus Cookbook” in 2012. This manual provides basic knowledge
and techniques required for REDD-plus with the main focus on forest carbon monitoring
methods. REDD-plus Cookbook is intended for policy makers working on the introduction of
REDD-plus and practitioners and experts working for the planning of REDD-plus activities.
Items of necessary knowledge and techniques required for REDD-plus are compiled in units
called “recipe.” As for the REDD-plus safeguards, additional study materials published by the
REDD+ Safeguards Research Consortium in 2016 are also available. “Guidebook for REDD+
safeguards” (in Japanese) covers the background, basic concepts, and steps required toaddress and respect REDD-plus safeguards, and “REDD+ Safeguard Approaches 2014”provides practical examples from forest conservation projects around the world. Althoughthese materials are useful to understand the basic knowledge required for REDD-plus,
detailed instructions useful for on-site activities were not necessarily covered. Thus, we
decided to elaborate on hands-on knowledge on “social” and “environmental” aspectsof safeguards as part of a series of technical manuals called the “REDD-plus Cookbook
Annex.” In this particular annex, fundamental concepts to address and respect safeguards
are explained. This manual is intended to be used as a textbook for capacity building, andwe recommend that it be read in conjunction with the Cookbook, the “Guidebook for REDD+
Safeguards”, and the “REDD+ Safeguards Approaches 2014.”
We hope this manual will contribute to the promotion of REDD-plus worldwide.
March, 2018
The REDD Research and Development Center
Forestry and Forest Products Research Institute
Forest Research and Management Organization

Contents
1 Outline

1

1.1 Purpose of Cookbook Annex Vol. 6

1

1.2 Recipes covered by REDD-plus Cookbook

1

1.3 What are REDD-plus safeguards?

1

1.4 REDD-plus safeguards under the Cancun Agreement

2

2 Components of environmental safeguards

3

2.1 Conservation of biodiversity

4

2.2. Special consideration to natural forests

5

2.3 Conservation of ecosystem services

5

2.4 Enhancement of social and environmental benefits

7

3 Addressing environmental safeguards

8

3.1 Identifying conservation targets

8

3.1.1 Identifying important species

8

3.1.2 Identifying important ecosystems and/or landscapes

10

3.1.3 Identifying important ecosystem services

11

3.2 Avoiding negative impacts

13

3.3 Enhancing positive impacts

15

4. Monitoring of environmental safeguards

17

References

20

Conventions and International Agreements

23

Notes

23

REDD-plus COOKBOOK ANNEX

1 Outline
1.1 Purpose of Cookbook Annex Vol. 6
The REDD-plus Cookbook compiled in 2012 by the Forestry and Forest Products
Research Institute is an easy-to-understand technical manual on basic knowledge andtechniques required for REDD-plus. This REDD-plus Cookbook Annex Vol. 6 explains
REDD-plus safeguards by focusing on environmental aspects, such as biodiversity andecosystem services, which are roughly outlined in the Cookbook. It also covers necessary
considerations when developing and implementing REDD-plus, taking differences innational circumstances into consideration. Although (prospective) project proponents of
REDD-plus are the primary target readers of this manual, we hope that students and NGOsinterested in biodiversity conservation in the tropics will find it useful as well.
1.2 Recipes covered by REDD-plus Cookbook
This annex complements the explanations on safeguards outlined in REDD-plus Cookbook.
Recipes covered by REDD-plus Cookbook are shown in [ ] for reference. Detailed information
on safeguards is provided in “Guidebook for REDD+ Safeguards” (Forestry Agency of Japan
2016; in Japanese; http://www.maff.go.jp/j/kokusai/kokkyo/yosan/pdf/sg_guide.pdf), which thisannex will also complement.
1.3 What are REDD-plus safeguards?
The basic concept of safeguards was first proposed at the Declaration on Human
Environment adopted by the United Nations (UN) Conference on the Human Environment held
in Stockholm, Sweden, in 1972 and then developed as the bases for investment in the WorldBank and other organizations since the 1980s (Davis et al. 2013). The fundamental principles
are to “conserve the effects of measures” and to “do no harm,” but safeguards also include
expectations to further contribute to various social and environmental aspects of REDDplus. REDD-plus safeguards are often classified into two categories: social safeguards andenvironmental safeguards. The Cookbook provides four categories: forest governance, social,environmental (including related social aspects), and climate [See Recipe-P03, page 38-39].
<Key points of REDD-plus safeguards>• Safeguards are requirements to be met when implementing REDD-plus activities to prevent
negative social and environmental impacts and reduce any risks that can undermine climatechange mitigation measures.
• U nder the UN Framework Convention on Climate Change (UNFCCC), countries are
required to promote and support the safeguards throughout the implementation of REDDplus activities and provide a summary of information. National circumstances should be1Vol. 6 Environmental Safeguards

considered when determining the specific contents of the information, criteria, and indicatorsfor identifying the achievements.
• Information on effective approaches and methods of setting objectives for safeguards is
expected to be updated based on analyses of REDD-plus activities in the near future.
1.4 REDD-plus safeguards under the Cancun Agreement
The 16th Session of the Conference of the Parties (COP16) of UNFCCC held in Cancun,
Mexico, in 2010 was an important turning point for REDD-plus. The seven items of REDDplus safeguards that should be taken into consideration when implementing REDD-plus (seebelow) were identified in the so-called the Cancun Agreement. Since then, these safeguards
have been perceived as the fundamental requirements when implementing REDD-plus at
the national level [See Recipe-P03, page 38-39].
The seven safeguards identified in the Cancun Agreement (Cancun Safeguards) (1/CP.16,
Paragraph 2 of Appendix I) are as follows:(a) T hat actions complement or are consistent with the objectives of national forest
programmes and relevant international conventions and agreements;(b) Transparent and effective national forest governance structures, taking into accountnational legislation and sovereignty;(c) Respect for the knowledge and rights of indigenous peoples and members of local
communities, by taking into account relevant international obligations, national
circumstances, and laws, and noting that the United Nations General Assembly has
adopted the United Nations Declaration on the Rights of Indigenous Peoples [UNDRIP];(d) The full and effective participation of relevant stakeholders, in particular indigenous peoples
and local communities, in the actions referred to in paragraphs 70 and 72 of this decision1;(e) T hat actions are consistent with the conservation of natural forests and biologicaldiversity, ensuring that the actions referred to in paragraph 70 of this decision are
not used for the conversion of natural forests, but are instead used to incentivize theprotection and conservation of natural forests and their ecosystem services, and toenhance other social and environmental benefits2;(f ) Actions to address the risks of reversals;(g) Actions to reduce displacement of emissions.
1 Activities for reducing emissions from deforestation and forest degradation, as well as conservation,
sustainable management of forests, and enhancement of forest carbon stocks.
2 “Taking into account the need for sustainable livelihoods of indigenous peoples and local communities
and their interdependence on forests in most countries, reflected in the United Nations Declaration on
the Rights of Indigenous Peoples, as well as the International Mother Earth Day.” (1/CP.16, Footnote ofParagraph 2(e), Appendix I)

2

REDD-plus COOKBOOK ANNEX

2 Components of environmental safeguards
The primary objective of REDD-plus is to reduce emissions through forest conservationand sustainable forest management in developing countries. However, since the concept
was first proposed at UNFCCC, REDD-plus has also been expected to promote theconservation of biodiversity-rich tropical forests. This expectation is represented byitem (e) of the Cancun Agreement, which is also called environmental safeguards. The
statement requests countries to respect and address the conservation of biodiversity
and ecosystem services when implementing REDD-plus activities. Note that countries
are requested to enhance not only environmental benefits but also social benefits, as
represented by the term “social and environmental benefits” (See 2.4 for enhancementof benefits). Furthermore, the footnote of item (e) states that sustainable livelihood ofindigenous peoples and members of local communities should be considered in the context
of environmental safeguards (See REDD-plus Cookbook ANNEX Vol. 3 (Furukawa et al.
2017) for instructions on social safeguards). This particular manual focuses on item (e) of
the Cancun Agreement (Table 1) [See Recipe-P03, page 39-40].
Table 1. Categorization of Safeguards in the Cookbook and the focus of this annex
Cancun Safeguards Item
(a)
(b)
(c)
(d)
(e)
(f)
(g)

Category
Forest governanceSocial safeguards
Environmental and social safeguards
Climate change* This annex covers the green item only.

Safeguard items related to social and climate (c, d, f, and g) ask parties to avoid negative
impacts and reduce risks, whereas item (e) further encourages to enhance positive impacts.
The wording of item (e) is complicated reflecting the process of international negotiations,but the key components are 1) conservation of biodiversity, 2) special consideration for
natural forests, 3) conservation of ecosystem services, and 4) enhancement of socialand environmental benefits. Although multiple pathways exist to enhance social benefits
comprehensively, this manual will focus on social benefits achieved through conservationand enhancement of ecosystem services given the close link with biodiversity.

3Vol. 6 Environmental Safeguards

2.1 Conservation of biodiversity
The Convention on Biological Diversity (CBD) defines biodiversity as the variability amongliving organisms from all sources, including diversity within species, between species
and of ecosystems (CBD Article 2). Biodiversity is critical for sustaining the functioningof ecosystems and bringing various benefits to human society. However, biodiversity iscurrently at stake due to increasing pressures from human activities.
REDD-plus targets forests in developing countries, particularly in the tropics, where
biodiversity is exceptionally rich. However, tropical biodiversity has been rapidly declining
due to habitat loss, forest degradation, and excessive hunting and harvesting of biologicalresources (Bradshaw et al. 2009). Therefore, REDD-plus is expected not to impair thevalue of biodiversity but to further promote its conservation. The CBD invites countries toconsider the following points when implementing REDD-plus (Annex to Decision XI/19).
Adverse impacts on biodiversity to be avoided (excerpted from Article 4, Annex toDecision XI/19):• The conversion of natural forests to plantations and other land uses of low biodiversity
value and low resilience;• Displacement of deforestation and forest degradation to areas of lower carbon value andhigh biodiversity value;• Increased pressure on non-forest ecosystems with high biodiversity value;• Afforestation in areas of high biodiversity value.
Approaches to enhance biodiversity conservation and ecosystem services (excerpted
from Article 17(d), Annex to Decision XI/19):• Converting only land of low biodiversity value or ecosystems largely composed of nonnative species, and preferably degraded ecosystems;• Prioritizing, whenever feasible, local and acclimated native tree species when selecting
species for planting;• Avoiding [the use of] invasive alien species;• S trategically locating af forestation activities within the landscape to enhanceconnectivity and increase the provision of ecosystem services within forest areas.
Conservation of biodiversity is strengthened when it is planned based on multifacetedand spatially broad information, such as the location of important habitats, ecosystems withconservation priority, and landscape configuration and connectivity. Such information is usually
incorporated and reflected in regional or local biodiversity conservation programs, and item

4

REDD-plus COOKBOOK ANNEX(e) of Cancun Safeguards notes the importance of REDD-plus actions to be “consistent” withthem. When consistency is not ensured, the effectiveness of both REDD-plus and biodiversity
conservation measures might be weakened or impaired. Specific programs of interest are the
National and/or Regional Biodiversity Strategy and Action Plans (NBSAPs/RBSAPs) formulated
under the initiation of the CBD. Other international agreements and programs, such as theWorld Heritage Convention, the Convention on International Trade in Endangered Species ofWild Fauna and Flora (CITES), the Ramsar Convention, and UNESCO’s Man and the Biosphere(MAB) Programme might also have regulations, programs or guidance relevant to REDD-plus
activities. National and subnational programs and regulations related to land protection and land
use should also be checked. Conservation activities led by local stakeholders, such as NGOs,
indigenous peoples, and members of local communities, should also be considered.
2.2. Special consideration to natural forests
Reflecting the high level of interest by the international community, the term “natural forest”
appears three times in safeguard item (e). Natural forest is defined as “A forest composed ofindigenous trees and not classified as forest plantation,” so it is clearly distinguished from forest
plantation, i.e., “A forest established by planting or/and seeding in the process of afforestation
or reforestation” (FAO 2000). Monocultural plantation may be high in carbon absorption overa short period. However, biodiversity is generally significantly lower in forest plantations thanin natural forests (Gibson et al. 2011). During the initial negotiations in UNFCCC, one concern
was that if REDD-plus focused only on forest carbon, conversion of natural forests to fastgrowing forest plantations might be accelerated to increase the short-term gain in carbon
stocks. Furthermore, if the qualitative change in forests is ignored, conversion of natural forests
to profitable forest plantations might be overlooked. Therefore, safeguard item (e) emphasizes
to protect and conserve natural forests without converting them to plantations.
Natural forests include primary forests that have no clear visible indications of humanactivities and secondary forests that have naturally regenerated after disturbance (FAO 2000).
Intact forests that are almost unaffected by human activities are increasingly becoming rareworldwide (Potapov et al. 2017). Such forests are homes of species that are unable to survive insecondary forests or forests that have experienced selective cutting (Barlow et al. 2007; Gibson
et al. 2011). Therefore, REDD-plus has a large potential to promote biodiversity conservation by
preferentially protecting and conserving natural forests with almost no human activities.
2.3 Conservation of ecosystem services
Ecosystem services are the benefits supplied to human societies by ecosystems. Ecosystemservices are supported by biodiversity, and they are generally grouped into provisioning5Vol. 6 Environmental Safeguards

services, regulating services, cultural services, and supporting services, which all help improve1

human well-being in various ways (Fig. 1; MA 2005).
CONSTITUENTS OF WELL-BEINGECOSYSTEM SERVICES

Security
Personal safety
Secure resource access
Security from disaster

Provisioning
Food
Fresh water
Wood and fiber
Fuel…
Supporting
Nutrient cycling
Soil formation
Primary production…

Basic material for good life
Adequate livelihood
Sufficient nutritious food
Shelter
Access to goods

Regulating
Climate regulation
Flood regulation
Disease Regulation
Water purification…

HealthStrength
Feeling wellAccess to clean air and water

Cultural
Aesthetic
Spiritual
Educational
Recreational…

Good social relations
Social cohesion
Mutual respect
Ability to help others

LIFE ON EARTH - BIODIVERSITY
ARROW’S COLOR
Potential for mediation bysocioeconomic factors

Freedom of choice
and action
Opportunity to beable to achieve
what an individual
values doing andbeing

ARROW’S WIDTH
Intensity of linkage between ecosystemservices and human well-being

Low

Weak

MediumMediumHigh

StrongFig. 1 Links between ecosystem services and human well-being (MA 2005)

Synergy (relations in which the enhancement of a service also improves the state of otherservices) or trade-off (relations in which the enhancement of a service in exchange impairs
other services) might occur between ecosystem services or between ecosystem services
and biodiversity. In particular, different types of trade-offs that are mutually not exclusive
exist: spatial trade-offs (i.e., benefits here and costs there), temporal trade-offs (i.e., benefits
now and costs later), and beneficiary trade-offs (i.e., some win and others lose) (TEEB 2010).
Forests provide various ecosystem services to human society, and REDD-plus focuseson its climate regulation service (CO2 absorption and storage). For example, if REDDplus actions prioritize the conservation of forests high in carbon stock, biodiversity, andwatershed protection function (i.e., synergistic relationship), various ecosystem services canbe conserved simultaneously. Meanwhile, if REDD-plus activities restrict the use of forest(i.e., provisioning services), there might be a trade-off between the beneficiaries of emissions
reductions distributed worldwide and the local communities whose livelihood depends on forest
resources. To address this trade-off, the local communities might deserve livelihood support orcompensation for having restricted their rights so that any cost burdens are mitigated.

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REDD-plus COOKBOOK ANNEX

2.4 Enhancement of social and environmental benefits
Benefits are something useful and valuable to individuals and societies, and they are notlimited to products or services that can be priced. Ecosystem services are benefits people
obtain from ecosystems (MA 2005), and the benefits people enjoy also affect their wellbeing (Fig. 1). When assessing benefits, the cost required to obtain benefits should betaken into consideration (TEEB 2010).
REDD-plus is a financial mechanism for “carbon benefits” by reducing carbon emissions. As
mentioned earlier, forests are closely related to “social and environmental benefits” including
but not limited to ecosystem services. REDD-plus is expected to enhance these “social andenvironmental benefits” (also called “non-carbon benefits” or “co-benefits”) along with carbon
benefits. The definition of social and environmental benefits lacks consensus, but they likely
include benefits derived from the conservation of biodiversity, natural forests, and ecosystemservices, and positive social impacts to stakeholders including indigenous peoples andmembers of local communities. Thus, social benefits are closely related to respecting andaddressing items (c) and (d) of Cancun safeguards (i.e., respect for the knowledge and rights ofindigenous peoples and members of local communities, as well as full and effective participationof stakeholders), which are commonly known as social safeguards. Respecting the tenure rights
of forest-dependent local communities and their participation in the decision-making process offorest management would lead to an improvement and increased security of their livelihoods.
(See REDD-plus Cookbook ANNEX Vol. 3 Social safeguards (Furukawa et al. 2017) for details).
The social and environmental benefits that REDD-plus can provide are diverse, andvarious ways are used to strengthen them. When we perceive human well-being as a form ofcomprehensive benefit, REDD-plus has great potential to bring benefits to people through threeig. 2

non-exclusive approaches: “opportunities” including jobs, payments, and education; “security,”
which encompasses ecosystem services and the rights to landownership and resource use,and “empowerment” related to participation in decision making (Fig. 2; Lawlor et al. 2013).
REDD-plus
Opportunities• Jobs• Payments• Education• Infrastructure

Security• Landownership andmanagement rights• Access and use rights• Carbon rights• Health• Ecosystem services for water
food and health security

Empowerment• Participation in decisionmaking regarding to local
land-use anddevelopment• Building social capital toparticipate more
effectively

Human welfare
and well-being
Fig. 2 Three approaches to improve human well-being through REDD-plus (Lawlor et al. 2013)7

Vol. 6 Environmental Safeguards

3. Addressing environmental safeguards
To respect and address environmental safeguards when implementing REDD-plus
activities, one must 1) identify conservation targets found in areas that REDD-plus activities
may affect, 2) assess potential impacts of REDD-plus, especially negative impacts thatshould be avoided, and 3) consider whether appropriate conservation and/or enhancement
measures are planned and implemented.
3.1 Identifying conservation targets
To address environmental safeguards in REDD-plus, elements that are important forconserving biodiversity and ecosystem services should be identified3 in the target areas
where REDD-plus activities are carried out, and in other areas that might be indirectly
affected by REDD-plus activities (e.g., displacement of emissions4). Among the components
of environmental safeguards, natural forests can be specifically defined, but elements of
biodiversity and ecosystem services may vary depending on the sites. Given the difficulty for
individual project proponents to measure the variability within species (i.e., genetic diversity),
assessing biodiversity from or above the species level to the ecosystem/landscape scale isfeasible in the context of REDD-plus.
3.1.1 Identifying important species
The conservation priority of a species should be judged based on multiple factors such as
its extinction risk, level of endemism, cultural value, and resource value (See section 3.1.3 forvalues as culture and resources). Species inhabiting both forests and non-forest ecosystems
should be considered if there is a possibility of being affected by REDD-plus activities. Species
to be considered will most likely be limited to plants, vertebrates, and insects due to limited
information on identification keys, distribution, and general ecology of most species in othertaxa. For taxonomic groups that are difficult to identify to species (especially for plants andinsects), higher taxon, such as genus or family can be used based on the information available.

3 Social and Environmental Principles and Criteria (SEPC), REDD+ Social and Environmental Standards(REDD+ SES), Climate Community and Biodiversity Standards (CCBS), and Strategic Environmental
and Social Assessment (SESA), which are the four major REDD-plus safeguard guidelines usedworldwide, encourage the identification of areas to be preferentially conserved for biodiversity andecosystem services (Ehara et al. 2013).
4 Increase in emissions as a result of emission activities being displaced from areas targeted by REDDplus to areas that are not.

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REDD-plus COOKBOOK ANNEX

The National and/or Regional Biodiversity Strategy and Action Plans (NBSAPs/RBSAPs)
and related local conservation programs often provide lists of the important species thatshould be conserved. By referring to them, project proponents might be able to identify
species of conservation targets that may live in or near the project site. Other usefulsources of information include the IUCN Red List of Threatened Species5, which lists theworld’s endangered species and their distributions for some taxa. More detailed information
might be available if a national or regional Red Data Book or Red List of endangered
species is compiled. In particular, effective conservation measures can be planned if
information on population size or location of breeding site of important species is available.
When identifying the target species, one should check whether the species is regulated
in the Appendix to the Convention on International Trade in Endangered Species of Wild
Fauna and Flora (CITES) or protected by the laws in the host country. Many species
with economical and cultural values, especially those regulated under the CITES,
are overexpolited by illegal hunting and harvesting. Therefore, information of species
distributions must be handled with the utmost care (Box 1).
Box 1: Handling of information on endangered species
Scientific information on the ecology of endangered and/or rare species is useful fordeveloping effective conservation measures or for operating ecotourism in an ecologicallyappropriate manner. However, disclosing the information on species location or habitat
description to the public requires care: poachers or illegal harvesters might show up andwipe out the local population, or nature enthusiasts might accelerate habitat destruction(Lindenmayer and Scheele 2017). Species that are most targeted are those hunted orcollected for high economic or cultural values, such as high-value timber species, orchids,
animals with ivories or horns, or those consumed as rare delicacy, traditional medicine, oras pets and specimens. International crime networks are believed to be involved in someof these transactions. Appendix to CITES or the laws of the host country often provide listsof species that need to be handled with utmost care. However, such regulations might lag
behind the local situation, so project proponents should pay attention to any emerging threats
through various information channels including interviews with the locals. The search resultsof the name of the species on the internet would probably be a good indicator of whether the
species is highly prized and threatened by enthusiasts (Auliya et al. 2016). Project proponents
should avoild the careless disclosure of location information of species at risk, even thoughsuch data are intended to contribute to the conservation of biodiversity in the host country.
5 IUCN (International Union for Conservation of Nature and Natural Resources) Red List of Threatened
Species: http://www.iucnredlist.org/

9Vol. 6 Environmental Safeguards

3.1.2 Identifying important ecosystems and/or landscapes
An ecosystem includes not only organisms but also their surrounding physical environment
as a system. It is composed of hierarchical components such as genes, species, populations,and communities. At a broader spatial scale, multiple ecosystems form a landscape. For acomprehensive biodiversity conservation and the sustainability of ecosystem functioning
including provisioning of ecosystem services, there is growing recognition of the importanceof ecosystem-based management (UNEP 2009). Thus, REDD-plus is expected to recognize
important ecosystems and landscapes for biodiversity conservation (For the viewpoint fromecosystem services, see section 3.1.3).
Natural forest is the most emphasized ecosystem to conserve under REDD-plus. The
distribution and area of natural forests need to be monitored while being distinguishedfrom planted forests to demonstrate that no conversion has occurred. Natural forests withpristine features and minimal human impacts are particularly high in conservation value,
and REDD-plus can enhance biodiversity conservation by protecting such natural forests.
Forests with little human disturbance are characterized by few pioneer species and many
shade-tolerant species, and data from ground-based carbon monitoring might be useful
to identify the location and characteristics of such forests (Imai et al. 2014). Non-forest
ecosystems with little human activities distributed within the range affected by REDD-plus
activities should also be identified as well.
Ecosystems and landscapes that provide feeding grounds and habitat for important
species are also candidates of conservation targets. Protecting forests that have lost
species of conservation interest due to poaching and other illegal activities is a failureof ecosystem conservation and is called “empty forest syndrome” (Redford 1992).
Conservation success cannot be achieved unless both species and ecosystem conservation
are taken into consideration. Thus, whether species of conservation importance are foundin the target area and in which ecosystems, and where their distributions overlap, should bedetermined. Breeding grounds are areas that require special consideration.
Protected areas are important conservation targets whose conservation values havebeen identified through pre-existing conservation schemes. In addition to protected areas(e.g., national parks and wildlife reserves) designated by the host country, those thatare registered under international conservation networks such as the World Heritage
Convention, the Ramsar Convention and the UNESCO’s MAB, and areas protected by local
stakeholders should also be identified. If such protected areas have conservation plans,
useful information on the species and areas of conservation importance, areas restricted tohuman activities, and locally adapted conservation measures might be available.
Areas of conservation interest can also be identified through landscape-level analyses. For

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REDD-plus COOKBOOK ANNEX

example, intact forests that are not fragmented by anthropogenic land use such as roads andbuilt-up areas are becoming increasingly rare worldwide (Potapov et al. 2017). Landscapelevel analyses are also useful for identifying contiguous ecosystems that play a critical role inlocal biodiversity conservation and areas that improve the connectivity of ecosystems.
3.1.3 Identifying important ecosystem services
Among the four categories of ecosystem services, provisioning, regulating, and cultural
services are subject to conservation as they are directly related to human well-being,
whereas supporting services are necessarily not because they are the basic functionsof ecosystems that support other services (Fig. 1). When identifying ecosystem servicesof conservation interest, opinions from stakeholders including indigenous peoples andmembers of local communities should be considered through interviews and consultations
to enhance social and environmental benefits.
Important provisioning services can be identified by interviewing local peoples whouse, consume, and/or sell resources obtained from the surrounding landscape. The typeof resources they collect, the location of collection including prohibited areas, and thecharacteristics of people who use them are important information that can be obtained
through household interviews (Miah et al. 2012; Kimura et al. 2014; Ehara et al. 2015).
However, what people consider to be valuable in the forest areas is often difficult torecognize and measure (Sheil and Wunder 2002; Kaimowitz and Sheil 2007). Thus,
one should understand the socioeconomic background and surrounding environmentof vulnerable groups in the community, particularly those sensitive to changes in thesurrounding environment, and the services they depend on (especially food, fuel, medicine,and materials) (Schoneveld et al. 2011; Mandondo et al. 2013; Ehara et al. 2016). From theperspective of social safeguards, understanding the relationship between stakeholders’rights related to land and forest use and each provisioning services is crucial, with special
attention to the rights of indigenous peoples and members of local communities.
Regulating services are difficult to measure directly, and the beneficiaries, who tend to
be distributed in relatively wide areas, are often hard to identify. Thus, the critical areas forthe conservation of regulating services should be identified using knowledge derived fromscientific literature. For example, vegetation in the riparian zone and on steep slopes is acandidate of conservation targets for the general functions of soil and water conservationand preventing landslides.
Field-based interviews to local stakeholders should be conducted to identify conservation
targets of cultural services due to their large regional variation. Specifically, the forests usedor protected by indigenous peoples and local communities over generations, such as grave11Vol. 6 Environmental Safeguards

forests, spiritual forests, shrine and temple forests, and sites prohibiting human entry should
be included. In addition to these forests and sites, scenic spots designated by host countries
and landscapes attracting people for sightseeing will also be targets of conservation.
In the previous sections, key approaches to identifying conser vation targets of
biodiversity, ecosystem, and ecosystem services from the perspective of REDD-plus
environmental safeguards have been explained. In early REDD-plus projects, a framework
known as High Conservation Value (HCV) was utilized to identify conservation targets, inwhich both biodiversity and community objectives were incorporated (Box 2).
Box 2: Framework for High Conservation Value (HCV)
Forestry-related voluntary certification schemes, such as the Climate, Community andBiodiversity Standards (CCBS) and the Forest Stewardship Council (FSC), use a framework
known as High Conservation Value (HCV) to identify the conservation targets (CCBA 2013;
Forest Stewardship Council 2015). HCVs consist of six categories: HCV1–HCV3 (biodiversity
components), and HCV4–HCV6 (elements of ecosystem services important for local
communities) (Table 2; Brown et al. 2013). In particular, HCV identifies the areas with highconservation value as the target to conserve. In addition, when identifying HCV4–HCV6,
opinions of indigenous peoples and members of local communities are required to be taken
into account.
Table 2 Elements and contents of High Conservation Value (HCV)
Category

Notes and examples
Areas with high concentrations of biological diversity:

HCV1 Species diversity
Biodiversity

protected areas, habitats of rare, endangered and/or
endemic species, including temporal importance (e.g.,
breeding areas, feeding grounds, and migration routes)

HCV2

Intact forest landscapes and large landscape-levelLandscape-level ecosystems
natural ecosystems and mosaics that contain viable
and habitats
populations of the great majority of a species

HCV3

Rare, threatened, or endangered−
ecosystems

Local communities

HCV4 Ecosystem services

Basic ecosystem services including protection of water
catchments and control of erosion of vulnerable soils andslopesHCV5 Community needs

Sites and resources fundamental for satisfying the basic
necessities of indigenous peoples and local communities(for livelihoods, health, nutrition, water, etc.)

HCV6 Cultural values

Sites, resources, habitats and landscapes of cultural,archaeological or historical significance, and/or thosethat are critical for the traditional cultural identity ofindigenous peoples and local communities

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REDD-plus COOKBOOK ANNEX

3.2 Avoiding negative impacts
The basic concept of REDD-plus safeguards is to avoid negative impacts that might
be caused by REDD-plus activities. After identifying the conservation targets, potential
impacts of REDD-plus activities should be analyzed at the planning stage. If possible
negative impacts are identified, improvement measures, such as changing the plan oradding compensatory measures, should be adopted. Some project proponents may regard
safeguards as “burdens” of REDD-plus activities, but one must remember that any negative
impact to the environment or the community might lead to the failure of the entire project.
Therefore, safeguards should be addressed and respected from the initial stage of project
development.
When a REDD-plus project aims to reduce deforestation, measures to control the
expansion of land-use associated with forest conversion (to farmland or residential land)
are usually implemented. This type of REDD-plus activity usually leads to the conservationof forest biodiversity and ecosystem services. However, such positive effects might belimited unless the conservation of natural forests is ensured. In addition, when managing
the displacement of emissions, one must ensure that non-forest ecosystems (or low-carbon
forests) with high value of biodiversity and ecosystem services are not converted to otherland-use.
In a REDD-plus project aimed at reducing forest degradation, the reduction in forest
carbon stocks is often prevented by restricting forest use. As with deforestation measures,
reducing forest degradation is considered to act positively for the conservation of forest
biodiversity and ecosystem services. However, if the use of provisioning services, suchas timber, fuel, and other forest resources, is prohibited, local people using them might be
adversely affected by the project. Therefore, compensation and/or support for livelihood
equivalent to the loss caused by the implementation of the REDD-plus project is needed for
those affected. The use of provisioning services is closely related to the rights to land andforest use. Special attention should be paid to the customary rights of indigenous peoples
and members of local communities, which are not always recognized in the host country’s
legal system and not reflected in local resource management programs. (See Furukawa etal. (2017) for further reading on respecting the knowledge and rights of indigenous peoples
and local communities).
Afforestation and reforestation activities are not necessarily the focus of REDD-plus ingeneral, but related activities (e.g., small-scale tree planting, assisted natural regeneration,and restoration) have been implemented in early projects to enhance carbon stocks,
restore forest ecosystems and biological corridors, and/or introduce useful tree species forlivelihood support. When implementing such activities related to tree planting, converting13Vol. 6 Environmental Safeguards

natural forests into tree plantations is not allowed in REDD-plus. Alien species might beselected for planting due to established reforestation technology and low adoption costs,
but the use of highly invasive species that might threaten natural ecosystems, disturb
water balance, or alter natural fire regimes should be avoided. In particular, voluntary
certifications strongly recommend the use of native species for biodiversity conservation;
if alien species are used, one should demonstrate that the benefits are larger than thenegative ecological impacts (CCBA 2013).
Other types of activities might also be conducted in a REDD-plus project, and carefulconsideration is required as their possible negative impacts will vary depending on thecircumstances. Some international safeguard standards ask to demonstrate that theuse and disposal of chemicals (e.g., fertilizer, herbicide, and insecticide) and materials
used for the activities are appropriate (CCBA 2013). If, for example, forest patrolling by
local communities is planned for the conservation of forest carbon and biodiversity, thecommunity would be negatively affected if appropriate expenses of patrolling including
labor cost are not paid (which applies to all community-based participatory activities).
Diverse measures can be adopted to address negative impacts under REDD-plus
environmental safeguards, and they should be considered in close relationship with social
safeguards, especially for matters involving indigenous peoples and members of local
communities.

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REDD-plus COOKBOOK ANNEX

3.3 Enhancing positive impacts
Unlike other items of the Cancun safeguards, environmental safeguards encourage
the enhancement of social and environmental benefits. Avoiding negative impacts while
enhancing positive impacts in REDD-plus may seem demanding. However, REDD-plus
has the potential to achieve both carbon and non-carbon benefits simultaneously. The
enhancement of social and environmental benefits might also be an integral element forthe success of a project to receive support from local stakeholders and strengthen project
legitimacy. Furthermore, projects are increasingly evaluated or even rated based onwhether it can deliver net positive impacts, in which the with-project scenario is comparedagainst the business-as-usual or without-project scenario (Box 3).
To promote additional benefits of REDD-plus, threats to the identified conservation
targets must first be understood, and measures in conjunction with REDD-plus activities
should be planned. For example, agriculture, logging, and hunting were consideredthreats to biodiversity in early forest carbon projects (Panfil and Harvey 2016). Amongthese threats, agriculture and logging are drivers of deforestation and forest degradation,
respectively (Hosonuma et al. 2012). Thus, carbon benefits and biodiversity conservation
might be achieved simultaneously in REDD-plus projects targeting these drivers. Many
projects have claimed to contribute to biodiversity conservation by conserving species
habitats through REDD-plus (Panfil and Harvey 2016). Likewise, conservation of forestrelated ecosystem services is one of the benefits that REDD-plus can achieve relatively
easily.
Additional benefits might be greatly promoted with minimal modification of theplanned REDD-plus activities. For example, if patrolling of illegal cutting is planned as acountermeasure of forest degradation, watching out for poaching and other illegal forest
use would also enhance the conservation of rare animals and plants while conserving
forest carbon. Adding livelihood support for local communities through ecotourism
development to such patrolling activities might be one potential option to further enhancesocial benefits. Furthermore, if small-scale tree planting (e.g., distributing seedlings ofgarden trees and boundary trees along the edge of croplands or rangelands) to reduce
forest degradation is planned, considering the needs of local communities (such as fuel,food, medicine, and materials) when selecting tree species would enhance social benefitsof project activities. Environmental benefits can also be promoted by preferentially using
native species, choosing trees that provide food to other animals, and planting in areas that
increase habitat connectivity (Thompson et al. 2014).

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Vol. 6 Environmental Safeguards

Box 3: Net positive impacts and additionality
Enhanced positive impacts in some elements can be offset by negative impacts inothers caused by the project if the negative impacts are left unaddressed. Therefore,
some international safeguard standards require not only avoiding negative impacts of the
project activities but also demonstrating that the activities deliver net positive impacts6.
Voluntary certification schemes such as the CCBS expect convincing explanation of how
the project will bring the impacts on the environment and society (CCBA 2013). This task isachieved by comparing the with-project scenario against the business-as-usual (BAU) or
the without-project scenario and demonstrating that the net positive impact would not haveSocial or Biodiversity
Conditions

been gained without the project (which is known as “additionality”) (CCBA 2013) (Fig. 3).

Project
start date

Expected
impactstime

Fig. 3 Concept of net positive impacts achieved through the project’s additionality(Richards and Panfil 2011)

The idea of assessing net positive social impacts of a REDD-plus project by comparing
with the BAU scenario shown in Fig. 3 is close to the concept of time-series evaluationthat has developed in evaluation research (e.g., see Rossi et al. 1999). However, Caplow
et al. (2011) reported that robust evaluations using counterfactual scenarios are rarein avoided deforestation projects prior to the introduction of REDD-plus. In addition,
constructing BAU scenarios is a challenge for REDD-plus projects because the datacollection for scenario analysis is often conducted after project initiation (Pasgaard 2013).

6 Among REDD-plus safeguard standards and tools available worldwide, some of them (e.g., CCBS) require
applying methods to demonstrate a net positive effect, and some do not (Ehara et al. 2013).

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REDD-plus COOKBOOK ANNEX

4. Monitoring of environmental safeguards
In general, the objectives of monitoring are to assess whether the activities are producing
the intended effects as originally planned and to update and improve the next actions basedon the results. Monitoring is a crucial process for the adaptive management of REDD-plus
projects and environmental safeguards. To conduct effective monitoring of environmental
safeguards, project proponents should understand what information is needed for
implementing safeguards throughout the project. In addition, project proponents must
report how safeguards have been respected and addressed and disclose the monitoring
results regardless of which financial scheme of REDD-plus they use. Monitoring of naturalforests is already a requirement in many REDD-plus frameworks.
Monitoring should be effective and efficient given the often limited project finance.
Effectiveness can be achieved by analyzing how the project will bring impact and achieve
the targeted effects. In particular, safeguard monitoring should check whether project
activities are bringing positive rather than negative impacts to the identified conservation
targets as planned. Before project implementation, potential negative impacts of the projecton the identified conservation targets should be analyzed and the project design should be
modified and improved in advance to avoid negative impacts. Additionally, project activities
are expected to be modified or added accordingly to bring positive effects on the identified
targets of biodiversity, ecosystem services, and local communities. In both cases, therelationship among the “targets” affected by the “impacts” (effects) of the “activity” should
be clarified during the project development phase, and these three components are goodcandidates of monitoring indicators of environmental safeguards (Fig. 4).
The relationship between project activities and conservation targets can be further
analyzed in detail in a framework called “Theory of change” (Fig. 5; Richards and Panfil2011). Under this framework, the planned activities bring initial “outputs,” which thenbecome tangible “outcomes,” such as, changes in people’s behavior. Finally, the targeted
final objectives of the activities (“impacts”) are achieved. Effective monitoring can beachieved by setting relevant indicators for each step. This framework of analyzing theimpacts of a project in a step-wise manner is also useful for planning effective project
activities.
Among the conservation targets, those that may be negatively affected should bemonitored. Even if the plan had been improved to avoid negative impacts, the target that
could have been negatively affected in the original plan needs to be monitored to assess
whether the improvement measures are functioning. If unexpected negative impacts
become apparent on targets that were not intended to be monitored, improvement measures

17

4

5

Vol. 6 Environmental Safeguards(a) Original plan
Activity１(b) Revised plan
Target A

Activity１ʼ

Target A

Target B
Activity２

Target B

Target C

Negative
impactActivity２ʼ

Avoidednegative impact

Target C

Positive
impactFig. 4 Relationship between the targets affected by project activities
In this hypothetical example, Activity 1 was found to have negative impacts on Targets A and B, but
Activity 2 had no negative or positive impacts on any of the targets in the original plan (a). To avoid
negative impacts and bring positive effects, Activity 1 was modified to Activity 1’ so that the negative
impacts on Targets A and B were avoided, and Activity 2 was modified to Activity 2’ to enhance positive
impacts on Target C. In this case, one should monitor whether Targets A and B were not negatively
affected by Activity 1’, and whether Activity 2’ brought expected positive impacts on C.

Measures against illegal logging＋
Measures against illegal hunting

Reduce pressure on forest resources＋
Support for alternative livelihoods• Forest patrol• Removal of illegal hunting traps

Activity• Lectures and training courses• Provision of farming tools and materials• # of arrested illegal users• # of removed traps

Output• # of trainees attending• # of households using new tools/materials• Rate of recidivism of illegal users• Amount of illegal bushmeat on the market

Outcome• # of households adopting alternative
livelihood activities• Increase in income by alternative livelihoods• Decline of illegal logging/hunting• Increase in wildlife population

Impact• Decrease in poverty rate
• Decreased pressure on forest resources

Fig. 5 Concept of “Theory of change” and examples of monitoring indicators
Countermeasures against poaching implemented along with illegal logging measures (left); livelihood
support implemented as part of measures to reduce pressure from forest use (right).

should be taken immediately and monitoring should be added. Project proponents should
remember that evaluation of positive and negative impacts is often performed more strictly
under voluntary certification schemes (Box 3). When extracting monitoring indicators basedon the concept of “Theory of change” for negative project impacts, focus should be given to18

REDD-plus COOKBOOK ANNEX

the “impact” as the aim is to monitor “no negative impact”.
Efficient data collection is indispensable for sustained monitoring. Determining themonitoring indicators for project activities and their outputs should be relatively easy.
Considering whether data collection can be carried out as part of the project activities isalso important. For example, monitoring cost may be reduced by recording the number ofobserved wild animals, including traces of feces and footprints, during forest patrolling.
Utilizing data collected for carbon monitoring is another way to reduce cost. For example,
changes in the distributions and areas of natural forests and other natural ecosystems canbe assessed using remote sensing data that was obtained to monitor forest carbon stocks
and drivers of deforestation and forest degradation. In addition, data from ground-basedcarbon monitoring can be used to analyze the distribution and characteristics of forests
with low human impacts and their qualitative change (Imai et al. 2014).
Meanwhile, collected data might have limited use without ensuring the reliability ofdata. When monitoring temporal changes in a conservation target, use of the data thatare periodically recorded via a comparable method at the same observation point isrecommended. Monitoring should be conducted using an appropriate survey method andtime (e.g., season and day/night) depending on the target, and advice must be sought fromexperts when necessary. When local communities or non-experts participate in monitoring,appropriate training for necessary monitoring skills should be provided to all participants.
To improve project activities through monitoring, project governance structure including
the responsibility of data collection and analysis and the decision-making process foradaptive management should be defined. Monitoring results also need to be reported
and disclosed in accordance with the guidance of the financial scheme of REDD-plus
the project uses. Monitoring results should be disclosed to the local communities using
local languages and appropriate means. Project proponents should also keep in mind thatparticipation of local stakeholders can be enhanced by sharing monitoring data and jointly
planning the monitoring design, especially with indigenous peoples and local communities(See Furukawa et.al (2017) for details on participation).

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Vol. 6 Environmental Safeguards

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REDD-plus COOKBOOK ANNEX

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Notes
This annex includes a revision of a part of the “Guidebook for REDD+ Safeguards” (inJapanese) published in March 2016 by the Forestry Agency of Japan.

23

Authors	Takuya Furukawa, Makoto Ehara, Kimiko Okabe (Forestry and Forest
Products Research Institute)
Editors
Tamotsu Sato & Masayoshi Takahashi
Version
1.01enCitation
This document may be cited as:	Furukawa T, Ehara M, Okabe K (2018) REDD-plus Cookbook Annex.
Vol. 6 Environmental Sageguards. REDD Research and Development
Center, Forestry and Forest Products Research Institute Japan, 23pp.