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The role of forest protected
areas in the landscape
A draft paper for the Council on Foreign
Relations
November 1999
Nigel Dudley, Adrian Phillips and Sue Stolton
Aim: the following paper attempts to sketch out a conceptual framework for categorisation of management objectives for the world’s forests, suggesting a continuum of uses that stretches from strict protection to intensive, industrial-scale activity.
Background: The Council on Foreign Relations is carrying out a study into the implications of currents trends towards intensification of timber production, particularly with respect to forest conservation goals. This paper, one of a series of five, looks at the implications for forest protected areas, with particular emphasis on the suitability of current IUCN categories of protected area and the question of how much forest land could be assigned to protected areas in the future.
A brief essay such as this can provide only a very preliminary vision of the type of forest estate that we might expect, or hope to see in the future. It is put together not as a comprehensive prescription, but as a first step towards finding some common language – particularly with respect to the vexed question of what is, and is not a forest protected area or a protected forest area. Broad-scale approaches to questions of land use can help provide some necessary consistency, albeit with the recognition that flexibility is also essential to reflect local conditions, needs and aspirations.
Many of the issues we summarise are still the subjects of intense debate. The proposals laid out below are based around the principles of sustainability and of full awareness and accommodation of the needs of all stakeholders. The precise form that some land management takes – for example exactly what is meant by intensive forest management – lies outside our current remit.
Intensification of timber production and changing priorities in forest management
There is evidence that commercial timber production is becoming concentrated onto a smaller land area, as a result of plantation development and intensive forest management, and that this trend is set to continue. The latest estimates suggest that there are 61 million hectares of plantations in temperate and boreal forests and 81 million hectares in the tropics[1]. In both regions, plantations make up about 4 per cent of the total area under trees. The rate of plantation establishment is likely to increase further due to a number of factors, including declining production from natural forests, market forces and the potential investments in carbon sequestration. Many countries with large plantation estates will have virtually doubled their plantation area between 1995 and 2000.
The long-term implications of this remain
uncertain. Currently, there are still many problems facing plantations in some
parts of the world, including concerns about their social and environmental
impacts. Research suggests that the effectiveness of these plantations is very
variable; for example over 60 per cent of plantations in Africa and Asia have
been assessed by the consultancy Jaako Poyry as “unsuitable for commercial wood
production” due to low productivity, poor management and poor species selection[2].
Because intensive, commercial plantations are a new phenomenon, with at most
two or three rotations having taken place, their future performance can still
only be speculated about, although a recent study
carried out for the UK Department for International Development was optimistic
about future soil fertility[3].
Notwithstanding these important questions, the balance of evidence suggests
that the majority of timber production from forests will probably continue to
be concentrated onto a smaller area. The concept paper for the current study
suggests that “commercial scale timber production will be concentrated in one
quarter or less of the global forest area by the year 2050”[4].
This trend is already well advanced according to recent research by the WWF
Forests and Trade Initiative[5],
although it should also be noted that the area being cut continues to increase
in many countries.
Increasing intensification could in theory release more forest for alternative uses. In an ideal world, what should such forest lands be used for? If timber production is concentrated on a quarter of the forest, should three-quarters be in some form of protected area?
Forest protected areas
Forests that are designated as protected areas should all aim to meet the basic IUCN definition of a protected area[6], where a forest protected areas is:
An area of forest
especially dedicated to the protection and maintenance of biological diversity,
and of natural and associated cultural resources, and managed through legal or
other effective means.
The definition embraces
the “universe” of protected areas. All categories must fall within this
definition, although in practice the precise purposes for which protected areas
are managed differ considerably. Along
with more traditional conservation aims, for example, protected areas can also
embrace the maintenance of cultural and traditional attributes, education,
scientific research and tourism and recreation.
Within this over-arching definition, protected areas are therefore further subdivided into six categories:
-
Category Ia: Strict
nature reserve/wilderness protection area managed mainly for science or
wilderness protection - an area of land and/or sea possessing some
outstanding or representative ecosystems, geological or physiological features
and/or species, available primarily for scientific research and/or
environmental monitoring
-
Category Ib: Wilderness
area: protected area managed mainly for wilderness protection - large area
of unmodified or slightly modified land and/or sea, retaining its natural
characteristics and influence, without permanent or significant habitation,
which is protected and managed to preserve its natural condition
-
Category II: National
park: protected area managed mainly for ecosystem protection and recreation
- natural area of land and/or sea designated to (a) protect the ecological
integrity of one or more ecosystems for present and future generations, (b)
exclude exploitation or occupation inimical to the purposes of designation of
the area and (c) provide a foundation for spiritual, scientific, educational,
recreational and visitor opportunities, all of which must be environmentally
and culturally compatible
-
Category III: Natural
monument: protected area managed mainly for conservation of specific natural
features - area containing specific natural or natural/cultural feature(s)
of outstanding or unique value because of their inherent rarity,
representativeness or aesthetic qualities or cultural significance
-
Category IV: Habitat/Species
Management Area: protected area managed mainly for conservation through
management intervention - area of land and/or sea subject to active
intervention for management purposes so as to ensure the maintenance of
habitats to meet the requirements of specific species
-
Category V: Protected
Landscape/Seascape: protected area managed mainly for landscape/seascape
conservation or recreation - area of land, with coast or sea as
appropriate, where the interaction of people and nature over time has produced
an area of distinct character with significant aesthetic, ecological and/or
cultural value, and often with high biological diversity. Safeguarding the
integrity of this traditional interaction is vital to the protection,
maintenance and evolution of such an area.
-
Category VI: Managed
Resource Protected Area: protected area managed mainly for the sustainable use
of natural resources - area containing predominantly unmodified natural
systems, managed to ensure long-term protection and maintenance of biological
diversity, while also providing a sustainable flow of natural products and
services to meet community needs
The basis of the
categorisation is by primary management objective and assignment to a category
is not a commentary on management effectiveness. The categories system is
international, although national names for protected areas may vary. While all
categories are important, they imply a gradation of human intervention.
In recent years, the emphasis of protected area management has been broadened and extended to reflect the wider uses – and to some extent the priorities imposed from outside – that are driving protected area management.
Officially recognised protected areas now include “extractive reserves” (category VI under the WCPA definition), where a proportion of the protected area is used for sustainable forms of production, and landscape protected areas (category V) where biodiversity is embedded as one element in a working, usually traditional, landscape.
Protected areas such as
rubber tappers’ reserves in the Amazon (Category VI) and some national parks in
Europe (Category V) are very different from the traditional concept of a
strictly protected nature reserve. However, each category has clear guidelines
that separate the land from other more conventionally managed areas[7].
The key point is that the area must be managed so that the long-term protection
and maintenance of its biodiversity is assured. A clear distinction still
exists between protected areas and other land; this has recently been
emphasised anew by WCPA:
WCPA believes that large-scale
commercial activities such as clearcutting, plantation establishment and other
forms of industrial management, unrestrained tourism and other major
infrastructure projects are not compatible with any protected area designations[8].
Nonetheless, the
boundaries of “protected” and “non-protected” forests are sometimes in danger
of becoming blurred. As the areas listed in the United Nations List of Protected Areas are categorised by
governments, the criteria for qualification inevitably vary between states
(even though they are guided by the IUCN management categories). There is
consequently continuing disagreement about exactly when an area can be
classified as a “protected area”[9].
“Forest protected areas” and “protected forest
areas”
Typifying the debates about definitions is disagreement
about the term for describing protected areas within forests. WCPA prefers
“forest protected area” over “protected forest area” because the former places
the emphasis on the “protected area” while the latter could also refer to some
of the broader land-use categories referred to below.
To some extent, this confusion may be due to the fact that governments, feeling under pressure to create more protected areas, are “squeezing” as much land into protected area categories as possible. Whether this is the best approach to a truly sustainable forest management policy is open to question.
Other forest land
In the WWF/IUCN Forests for Life[10] strategy, three broad forest classifications are identified: forest protected areas, multiple-use forest, and intensively managed forests and plantations. Even if commercial timber production is concentrated onto a smaller area than at present, the remaining forest will continue to be subject to a range of pressures, such as food production, hunting, recreation, fuel-wood collection and large and small-scale mining.
Many of these uses are legitimate, but not
compatible with protected areas. Stretching the
definition of a protected area to encompass, for example, industrial activity
simply undermines the value of the concept of protected areas as a whole
without necessarily making compensatory gains in forest management and
conservation.
It is suggested that a
better approach would be to develop some further classifications of forest
management – forest management categories
– to stand beside the various categories of protected areas, thus forming a continuum of uses from strict protected
areas to intensively managed plantations.
Deciding on the proportion of each type of forest
management within a particular area would then form the basis of developing a
truly sustainable approach to forest management within the landscape.
Forest management categories
While precise
definitions of land-use are difficult and risk over-simplification, it is
possible to distinguish some broad categories, and an initial attempt is made
below. An overall definition of a forest management category might be
An area of
forest and associated lands primarily managed for resource protection and
sustainable use.
-
Five categories
are suggested, running from areas that are managed for general resource
protection but fall outside convention protected areas, to land managed for
industrial and intensive forestry. In all
of them, any associated biodiversity conservation is a secondary aim.
Such categories should,
in time, be developed along the same lines as those relating to protected
areas, i.e. including a definition, objectives of management,
guidance
for selection and organisational responsibility. The
current suggestions are summaries of what should eventually be more fully
worked out descriptions, complete with examples and explanatory case studies.
Such a typology could be one outcome of the current research being co-ordinated
by the Council on Foreign Relations.
- A: Managed for resource protection – an area of forest which is protected in order to provide a range of environmental services, such as soil and watershed protection, avalanche control and buffers against fire and flood. B: Managed for community benefit – an area of forest and associated lands which is used primarily to meet community needs such wood gathering, non-timber forest products, farming, artisanal mining and small settlements, including subsistence needs and small-scale trading.
- C: Reserved for future use – an area of forest that is reserved for potential future resource needs
-
D: Managed for multiple use – a landscape area, usually including forests
agricultural land and settlements that is as a whole sustainably managed for a
range of both community and
industrial uses.
-
E: Managed for industrial and intensive forestry – an area of forest which is managed primarily
for sustainable resource production such as production and management of
timber, non-timber forest products, agriculture, mining and energy.
These categories may have implications for the ways in which governments interpret the existing protected area categories. It may be, for example, that some of the areas classified as category V protected areas should be more accurately classified as category A above.
Within all these categories, a range of uses and actions will be important. The importance of these will vary with the category. In the following table, an initial attempt is made to identify the types of actions in the various categories of protected areas and forest management.
Proposed forest categories
|
Objectives |
Protected
Area Management Categories |
Forest
Management Categories |
|
|||||||||||
|
|
Ia |
Ib |
II |
III |
IV |
V |
VI |
A |
B |
C |
D |
E |
||
|
|
Strict nature reserve/ wild’ness protection |
Wilder-ness area |
National park |
Natural monum’t |
Habitat/ Species Management Area |
Protected Land-scape/ Seascape |
Managed Resource Protected Area |
Managed for resource protection |
Managed for commun-ity benefit |
Reserved for future use |
Managed for multiple use |
Managed for industrial
/intensive forestry |
||
|
Scientific research |
1 |
3 |
2 |
2 |
2 |
2 |
3 |
/ |
3 |
2 |
3 |
/ |
||
|
Wilderness protection |
2 |
1 |
2 |
3 |
3 |
/ |
2 |
/ |
/ |
2 |
/ |
/ |
||
|
Preserve species and genetic diversity |
1 |
2 |
1 |
1 |
1 |
2 |
1 |
3 |
2 |
2 |
3 |
3 |
||
|
Maintain environmental services |
2 |
1 |
1 |
/ |
1 |
2 |
1 |
1 |
2 |
2 |
2 |
3 |
||
|
Protection of natural/cultural features |
/ |
/ |
2 |
1 |
3 |
1 |
3 |
3 |
2 |
3 |
3 |
3 |
||
|
Tourism and recreation |
/ |
2 |
1 |
1 |
3 |
1 |
3 |
3 |
3 |
3 |
2 |
/ |
||
|
Education |
/ |
/ |
2 |
2 |
2 |
2 |
3 |
/ |
3 |
/ |
3 |
/ |
||
|
Sustainable use of natural ecosystems |
/ |
3 |
3 |
/ |
2 |
2 |
1 |
2 |
2 |
2 |
3 |
/ |
||
|
Maintain cultural/traditional attributes |
/ |
/ |
/ |
/ |
/ |
1 |
2 |
3 |
1 |
3 |
2 |
/ |
||
|
Subsistence/local scale |
/ |
/ |
/ |
/ |
3 |
2 |
1 |
3 |
1 |
2 |
1 |
/ |
||
|
Long-term resource protection |
/ |
/ |
/ |
/ |
/ |
/ |
2 |
2 |
3 |
1 |
3 |
/ |
||
|
Commercial/industrial |
/ |
/ |
/ |
/ |
/ |
/ |
/ |
/ |
/ |
/ |
2 |
1 |
||
|
Infrastructure/ transport |
/ |
/ |
/ |
/ |
/ |
3 |
3 |
/ |
2 |
3 |
2 |
2 |
||
|
Defence |
/ |
/ |
/ |
/ |
/ |
3 |
/ |
3 |
/ |
3 |
2 |
/ |
||
1 = primary objective (outlined in black)
2 = secondary objective
3 = acceptable objective
/ = objective not applicable
The grey
box = the main attributes of the six IUCN protected area categories and
is reproduced directly from Guidelines
for Protected Area Management Categories, CNPPA with the assistance of
WCMC, IUCN, Gland, Switzerland
Category E coloured dark grey = the proportion (around 25 per cent) of
the forest estate that will be dedicated to intensive forest management.
The white area = other categories of forest use outside
protected areas and intensive forest management
Protected area categories and forest management area categories are thus on a continuum from strict protection to virtual dedication to timber production. An approximate transition is shown in the diagram below, where the categories are plotted against the degree of disturbance (there is no attempt to represent this as an accurate scale).
|
Disturbance |
Protected Area Category |
Forest Management
Category |
|
|