|
The Montréal Process
Liaison Office
Canadian Forest Service
Ottawa, Canada
April 2000
Canadian
Cataloguing in Publication Data
Working
Group on Criteria and Indicators for the Conservation
and Sustainable Management of Temperate and Boreal Forests
Montréal
Process Year 2000 Progress Report - Progress and Innovation
in Implementing Criteria and Indicators for the Conservation
and Sustainable Management of Temperate and Boreal Forests
Issued
also in French under the title:
Le processus de Montréal Rapport de l'an 2000
- Progrès et innovations dans la mise en ouvre
des critères et des indicateurs pour la conservation
et l'aménagement durable des forêts tempérées
et des forêts boréales
Issued
also in Spanish under the title:
El Proceso de Montreal Informe del año 2000 -
Progreso e innovación en la implementación
de criterios e indicadores para la conservación
y el manejo sustentable de los bosques templados y boreales
At head
of title: The Montréal Process
ISBN: 0-662-28794-0
Cat. No.: FO42-238/2-2000E
1. Forest
conservation - Congresses.
2. Forest management - Congresses.
3. Taiga ecology - Congresses.
4. Sustainable forestry - Congresses.
I. Canadian Forest Service.
II. Title.
III. The Montréal Process.
SD411.W67
2000 333.75'6
The Montréal
Process Liaison Office
8th Floor, 580 Booth Street
Ottawa, ON
K1A 0E4
Tel: 1-613-947-9061
Fax: 1-613-947-9038
Report
also available in PDF Format (2.33 MB)

TABLE
OF CONTENTS
INTRODUCTION
BACKGROUND
VIGNETTE
ON ARGENTINA
VIGNETTE ON AUSTRALIA
VIGNETTE ON CANADA
VIGNETTE ON CHILE
VIGNETTE ON CHINA
VIGNETTE ON JAPAN
VIGNETTE ON KOREA
VIGNETTE ON MEXICO
VIGNETTE ON NEW ZEALAND
VIGNETTE ON RUSSIA
VIGNETTE ON UNITED STATES
VIGNETTE ON URUGUAY
DISCUSSION
APPENDIX
A
Montréal Process Criteria and Indicators
of the Conservation
and Sustainable Management of Temperate and Boreal Forests
|
Top |

INTRODUCTION
This
Year 2000 Report on the Montréal Process has
been prepared for presentation at the Eighth Session
of the United Nations Commission on Sustainable Development
(UNCSD), to be held in April 2000 in New York, USA,
and at the XXI World Congress of the International
Union of Forestry Research Organizations (IUFRO),
to be held in August 2000 in Kuala Lumpur, Malaysia.
The
report, which incorporates input from individual countries,
highlights accomplishments in implementing the criteria
and indicators of the Montréal Process, including
capacity-building, data collection, forest management,
institutional and regulatory policy development, and
technical co-operation. Countries have prepared "vignettes"
which describe experiences and provide examples of
progress and innovation in implementing criteria and
indicators and related policy initiatives to promote
sustainable forest management (SFM).
After
a brief introductory chapter, a short history of the
Montréal Process is included. This is followed
by presentation of the vignettes on participating
countries. The report continues with a discussion
concerning the strengths and added values provided
by working within the framework of the Montréal
Process, and concludes with a statement concerning
future actions to be taken by the Montréal
Process Working Group. The list of Montréal
Process criteria and indicators is attached to the
report (Appendix A).
| Table
of Contents | Top |

BACKGROUND
In
1993 Canada convened an International Seminar of Experts
on Sustainable Development of Boreal and Temperate
Forests. This meeting, held in Montréal, was
sponsored by the Conference on Security and Co-operation
in Europe (CSCE), now the Organisation for Security
and Co-operation in Europe (OSCE). The seminar focused
specifically on criteria and indicators and provided
a conceptual basis for subsequent regional and international
work.
The
Montréal meeting represented a response to
the United Nations Conference on Environment and Development
(UNCED) which was held in Rio de Janeiro in June 1992.
The conference had focused world attention on the
importance of sustainable forest management as a key
component of sustainable development, defined as meeting
the needs of today without hurting the ability of
future generations to meet their needs.
Following
the CSCE seminar, the Ministerial Conference on the
Protection of Forests in Europe elected to work as
a region under a pre-existing initiative. Canada then
took the lead in launching an initiative among non-European
countries having boreal and temperate forests. The
objective of this initiative was to develop and encourage
implementation of internationally agreed-on national-level
criteria and indicators for sustainable forest management.
In Geneva in 1994 the Working Group on Criteria and
Indicators for the Conservation and Sustainable Management
of Temperate and Boreal Forests was formed; this is
now known as the Montréal Process.
Twelve
countries are involved in the Montréal Process
Working Group - Argentina, Australia, Canada, Chile,
China, Japan, Republic of Korea, Mexico, New Zealand,
Russian Federation, United States of America and Uruguay.
These countries together represent about 60 per cent
of world's forests, about 90 per cent of the world's
temperate and boreal forests, 45 per cent of world
trade in wood and wood products, and 35 per cent of
the world's population.
Between
June 1994 and February 1995, the Montréal Process
countries met five times to pursue the development
of a comprehensive set of criteria and indicators.
At the Sixth Meeting, in Santiago, Chile, in February
1995, the 10 original participating countries endorsed
a statement of political commitment known as the Santiago
Declaration, together with a comprehensive set
of criteria and indicators for use by policy makers,
practitioners, and the general public (see Appendix
A). Subsequently the declaration was endorsed by Argentina
and Uruguay who have become members of the Montréal
Process. Since its inception, the Liaison Office for
the Process has been hosted by the Canadian Forest
Service. The office, located in Ottawa, provides various
services including document preparation and distribution,
process co-ordination and various clearing-house functions.
Over
the past five years a number of publications have
been issued by the Montréal Process. The first
report, issued in May 1996 and entitled Status
of Data and Ability to Report on the Montréal
Process Criteria and Indicators, summarised the
responses to a questionnaire, which had been designed
to assess the availability of data and to identify
the ability of countries to report on the criteria
and indicators. Subsequently, in February 1997, a
progress report on implementation of the Process was
released. This report included brief vignettes for
10 of the countries; these vignettes provide information
on the unique experiences of each country, the great
variation from country to country and the special
challenges or issues faced by individual countries.
A
First Approximation Report of the Montréal
Process was issued in August 1997. This report
reviewed the history of the Montréal Process
and its criteria and indicators and provided a summary
of more recent Montréal Process activities,
including early implementation. Advice concerning
the preparation of the report was provided by the
Technical Advisory Committee (TAC). The report was
primarily devoted to member-country responses to a
call for updated information on the status of data
assembly and on key issues associated with implementation
of the Process. The survey revealed that there was
a reporting rate of 87 per cent for all indicators,
that data were being collected for 68 per cent of
the indicators, and that specific detail was being
provided for 39 per cent of the indicators. It was
revealed, however, that there were gaps in the ability
to report for 50 per cent of the indicators. These
country reports are the key to future reports in that
they provide baseline information and highlight the
gaps in the available national data for each indicator.
A technical
report prepared by the TAC is currently under review
by the Montréal Process Working Group. A brief
explanation or rationale, definitions of key terms
and suggested measurement approaches are included
for each indicator. The measurement approaches suggested
do not necessarily represent the latest available
techniques, but focus on useful and cost-effective
techniques. Possible techniques are included for all
indicators, even when measurement approaches may be
difficult to implement fully in the short term.
Criteria and Indicators
Criteria
and indicators are tools for characterising the state
of a nation's forests and for providing information
on how forest lands and uses are changing. This information
is vital in formulating policies that promote sustainable
forest management and can be used to assess national
trends. Information on trends is an essential step
in measuring progress toward the goal of sustainable
forest management.
Comparisons
of periodic national reports on the various indicators
will assist the public and decision-makers to identify
the current status and trends in most aspects of forests.
Over time, they will document the changes and outcomes
that result from forest management.
Specifically,
the seven criteria identified in the Montréal
Process are the essential components of the sustainable
management of forests. They include vital functions
and attributes (biodiversity, productivity, forest
health, carbon sequestration, and soil and water protection),
socio-economic benefits (timber, recreation and cultural
values), and the laws and regulations that constitute
the forest policy framework. The criteria and indicators
provide a framework for answering the fundamental
question, "What is important about forests?"
The Montréal Process indicators provide ways
to assess or describe a criterion. Many indicators
are quantitative, whereas others are qualitative or
descriptive. All indicators provide information about
the present conditions of forests and their use and,
over time, will establish the direction of change
in these variables. It is also recognised that whereas
many of the indicators can be readily measured, others
will involve the gathering of new and additional data,
a new program of systematic sampling, or even basic
research.
Together,
the seven criteria and the 67 indicators of the Montréal
Process reflect an ecosystem-based approach to sustainable
forest management and the need to serve human communities.
The criteria and indicators are not static; they will
be reviewed and refined continuously to reflect new
research, advances in technology, increased capability
to measure indicators and an improved understanding
of what constitutes appropriate assessment indicators.
| Table
of Contents | Top |

VIGNETTE
ON ARGENTINA
Criterion
1: Conservation of Biological Diversity
A major
inventory of forest plantations began in November
1997 and will be completed in May 2000. Partial information,
including range and extension of forest species, total
wood volume and species age, has been elaborated on
provincial maps at a scale of 1:100 000. Total areas
of forest by province are given in Table 1, with a
map of provinces in Figure 1.
Also,
a geographic information system, based on the indicators
noted in the previous sentence and on the interpretation
of satellite images, has been developed. The inventory
is being carried out by the Forest Development Project,
under the direction of the Secretariat of Agriculture,
Livestock, Fisheries and Food (IBRD).
Figure
1. Provinces of Argentina
 |
| Table
1. Planted forests by province |
| Provinces |
Planted
forest area
(ha)
|
|
Buenos
Aires
|
144
537
|
|
Catamarca
|
15
|
|
Córdoba
|
41
470
|
|
Corrientes
|
187
967
|
|
Chaco
|
1
620
|
|
Chubut
|
5
063
|
|
Entre
Ríos
|
86
962
|
|
Formosa
|
389
|
|
Jujuy
|
18
986
|
|
La
Pampa
|
2
701
|
|
La
Rioja
|
|
|
Mendoza
|
14
500
|
|
Misiones
|
197
000
|
|
Neuquén
|
41
094
|
|
Río
Negro
|
20
712
|
|
Salta
|
3
479
|
|
San
Juan
|
4
524
|
|
San
Luis
|
483
|
|
Santa
Cruz
|
2
139
|
|
Santa
Fe
|
30
414
|
|
Santiago
del Estero
|
3
833
|
|
Tierra
del Fuego
|
0
|
|
Tucumán
|
4
999
|
|
Total
|
812
887
|
|
Table
2. Native forest by region
Natural regions
(forested) |
Natural forest
area
(ha) |
Percentage
|
| Parque
Chaqueño (Chaco parkland) |
25
750 000 |
68.9
|
| Selva
tucumano-boliviana (Tucumán-Bolivia forest) |
2
490 000 |
6.7
|
| Selva
misionera (Misiones forest) |
2
060 000 |
5.5
|
| Bosques
subantárticos (Subantarctic woodland) |
1
970 000 |
5.3
|
| Monte
occidental (Western mountains) |
1
880 000 |
5.0
|
| Bosque
pampeano (La Pampa woodland) |
1
790 000 |
4.8
|
| Parque
mesopotámico (Inter-river parkland) |
1
440 000 |
3.8
|
| Total
|
37
380 000 |
100
|
The
Environment Secretariat is preparing the native forest
inventory.
Forest
types in Argentina, which totalled 60 300 000 hectares
in 1970, and now total 37 380 000, have been
classified into seven categories: Selva Misionera,
Selva Tucumano-boliviana, Parque Chaqueño,
Parque Mesopotámico, Bosque Pampeano, Monte
Occidental, y Bosques Subantárticos. Forested
areas by region are listed in Table 2 with a map of
regions shown in Figure 2.
There
are many categories of protected areas in Argentina.
The largest are natural environment conservation areas,
which cover 13 695 183 hectares. Also,
224 reserved areas have been established to protect
landscapes and other land use under the provincial
and national natural parks laws.
National
Forest Reserves have been designated in 34 sites covering
2 590 301 hectares to conserve natural ecosystems.
Criterion
2: Maintenance of the Productive Capacity of Forest
Ecosystems
The
greatest progress has been made on plantations. Forest
plantations, in 1992, totalled 20 000 hectares per
year, and currently total 120 000 hectares per year.
Forest policy has emphasised the expansion of commercial
forests, to decrease the deterioration of native forest
biomass. According to estimates for the next 10 years,
commercial forest lands will occupy about 2 000 000
hectares.
Figure
2. Natural regions of Argentina

Criterion
3: Maintenance of Forest Ecosystem Health and Vitality
The
National Agrifood Health and Quality Service, which
participates in the Forest Agricultural Health Program
is undertaking research on the pine-tree boring wasp
(Sirex noctilio). At the same time, the program has
signed an inter-institutional agreement with the Paraná
Delta Producers' Council.
Additionally,
in November 1991, a permanent Working Group on Forest
Agricultural Health was created under the South Cone
Plant Health Committee established by Argentina, Brazil,
Chile, Uruguay and Paraguay. The priority objectives
of this group are to analyse forest health questions
in the region, to coordinate actions, to exchange
experiences advising the directive committee.
Criterion
4: Conservation and Maintenance of Soil and Water Resources
The
Secretariat of Agriculture, Livestock, Fisheries and
Food, through the Forest Development Project (SAGPyA/IBRD),
has completed a study on desertification in Patagonia.
One of the study's conclusions was the importance
of forestation in erosion control. The study was carried
out by DHV consultants BV (Holland) - SCC Swedforest
International AB (Sweden), with experts from the National
Agricultural Technology Institute and the Faculty
of Agronomy of Buenos Aires University.
Criterion
5: Maintenance of Forest Contribution to Global Carbon
Cycles
The
native forest area in Argentina is estimated at about
37 000 000 hectares, and with an annual growth rate
of 3 cubic metres per hectare, is increasing in volume
at a rate of 105 000 000 cubic metres per year.
Likewise, the forest plantations, which cover 1 000
000 hectares and have an average annual growth rate
of 15 cubic metres per hectare, are increasing in
volume at about 15 000 000 cubic metres per year.
Accordingly, with silvicultural practices, Argentina
has capacity to realise carbon absorption (Tables
3 and 4).
Table
3. Carbon sequestered by plantation forests (per hectare)
| Species |
Commercial
annual growth rate (m3/ha)
|
Adjustment
for roots and branches |
Carbon
pool (t/m3)
|
Total
carbon
(t/ha) |
| Araucaria
|
18
|
1.4
|
0.26
|
6.6
|
| Pinus elliotii
|
25
|
1.4
|
0.26
|
9.1
|
| P. taeda |
28
|
1.4
|
0.26
|
10.2
|
| P. caribaea
|
33
|
1.4
|
0.26
|
12.0
|
| Eucalyptus
|
35
|
1.4
|
0.6
|
12.7
|
| Populus |
35-40
|
1.4
|
0.26
|
12.7
|
Table
4. Net carbon in forests at the end of first rotation
| Prior
use |
C
released in conversion
(t) (2)
|
C captured in
forest
(t/year) (3)
|
Net C/ha of new
plantation (3)-(2)=(4)
|
| |
|
Max
|
Min
|
Max
|
Min
|
| Agricultural
crops |
0
|
12.7
|
6.6
|
381
|
198
|
| Pastures
|
0
|
12.7
|
6.6
|
381
|
198
|
| Abandoned
agricultural lands with regrowth |
50 |
12.7 |
6.6 |
331 |
148 |
| Delta
wetlands (9 years) |
0
|
12.7
|
6.6
|
114
|
59
|
Criterion
6: Maintenance and Enhancement of Long-Term Multiple
Socio-economic Benefits to Meet the Needs of Societies
The
Secretariat of Agriculture, Livestock, Fisheries and
Food, under the Ministry of Economy and Public Services
and Works, is responsible for execution of the Forest
Development Project.
The
principal benefits foreseen by the project will include
the following:
- A more efficient
political-regulatory framework to develop ecological
potential, in sites highly suitable for forestry
but marginal for other activities
- Direct emphasis
on increased productivity
- Prioritisation of
effort for regions showing economic and ecological
advantages
- Quality improvements
in wood to be harvested and diversification of manufacturing
alternatives
- Recovery of fragile
or deteriorated zones, helping to diminish the pressure
on natural forests
- Strengthening of
peripheral research, information and extension services
- Greater participation
of the private sector, in production as well as
in services
- Creation and implementation
of options to improve family incomes of small producers
- Enhanced technical
and administrative forest capability in the public
sector
- Training of technical
and managerial staff in private and public areas
Criterion
7: Legal, Institutional and Economic Framework for Forest
Conservation and Sustainable Management
Basically,
the legal framework is composed of the legislation
listed in Table 5:
Table
5. Legal framework for forest conservation and sustainable
management
|
Sector
|
Conservation
law
|
|
Protected
areas
|
Law
22351 and decree regulation 637
|
|
Protected
areas
|
Decree
1979/78
|
|
Flora
|
Law
13273
|
|
Flora
|
Law
23973
|
|
Fauna
|
Law
22421/81 and regulation 691/81
|
|
Land
|
Law
22428 and regulation 681/81
|
|
Water
|
Law
2797/91
|
|
Water
|
Law
20481 and regulation 1886/83
|
|
Water
|
Law
23615
|
|
Water
|
Decree
2125/78
|
|
Water
|
Decree
776/92
|
|
Atmosphere
|
Law
20282
|
|
Atmosphere
|
Law
24040
|
|
Pesticides
and fertilisers
|
Laws
3489, 18073, 18796, 18323, 20026, 20316, 20418,
20466 and 22289
|
Furthermore,
Argentina is part of several international conventions
on conservation and protection of the natural resources
(Table 6).
Table
6. Participation in international conventions
|
Subject
|
Agreement
|
Year
of ratification
|
|
Biodiversity
|
Protection
of wildlife
|
1946
|
|
Biodiversity
|
Ramsar
|
1971
|
|
Biodiversity
|
CITES
|
1973.
Law 22344/ 80
|
|
Biodiversity
|
Conservation
of migratory fauna (Bonn)
|
1979.
Law 23818
|
|
Biodiversity
|
Biodiversity
(Río de Janeiro)
|
1992
|
|
Atmosphere
|
Protection
of ozone (Vienna)
|
1985
Law 23724
|
|
Atmosphere
|
Montréal
Protocol
|
1987
|
|
Atmosphere
|
Climate
Change Framework
|
1994
|
|
Health
of vegetation
|
----------------------------
|
Various
|
The
policy and legislative framework for forests has
considered the following objectives in the Cultivated
Forest Investment Law (Nº 25.080/99) and the Decree
(Nº 133/99):
- Protection of natural
forests, prohibiting their use except where management
plans to promote active management have been approved
- Expansion of the
forest base through forest plantations, using appropriate
species on land with medium to low agricultural
productivity, with an approved sustainable management
plan.
| Table
of Contents | Top |

VIGNETTE
ON AUSTRALIA
Summary
This
report highlights developments since 1997, when Australia's
First Approximation Report (FAR) was produced. Australia
finalised A framework of regional (sub-national)
level criteria and indicators of sustainable forest
management in Australia in 1998, after a two-year
consultative process between government agencies at
Commonwealth (Federal), State and Territory levels,
and stakeholders. The framework was endorsed by forestry
and environment Ministers at all levels and was released
publicly in August 1998. The framework is based on
the internationally accepted national-level criteria
and indicators of the Montréal Process. It
provides a co-ordinated approach to monitoring trends
in forest conditions and to the sustainability of
Australia's forest management practices at a sub-national
level. This will enable data to be aggregated for
use at the national level. A phased approach to implementation
of indicators has been agreed on, giving States and
Territories flexibility regarding implementation.
To
support this work, Australia is undertaking a number
of research and development projects that aim to deliver
practical, cost-effective and sensitive indicators.
As outlined in the FAR, several key challenges exist
for Australia, including collection of data from non-commercial
forests on public land and from the large majority
of privately managed forests. Given that these tenures
constitute about 90 per cent of Australia's forest
estate of 157 million hectares, this amounts to a
significant issue.
Development
of a Framework of Criteria and Indicators for Use at
Sub-national Level
In
July 1996, Australia's Ministerial Council on Forestry,
Fisheries and Aquaculture (MCFFA) requested that a
framework of regional-level criteria and indicators
be developed. The MCFFA's Standing Committee on Forestry
(SCF) and the Australian and New Zealand Environment
and Conservation Council's (ANZECC) Standing Committee
on Conservation (SCC) agreed to establish the Montréal
Process Implementation Group for Australia (MIG),
a Commonwealth-State body, to develop the framework
of regional criteria and indicators. The MIG process
has included stakeholder meetings, expert workshops,
seminars and a period for public comment. Stakeholders
and experts provided input on the adequacy of the
indicators to capture key attributes of sustainable
forest management (SFM) at a regional (sub-national)
scale and for Australian conditions. Advice was also
provided on research needs.
The
MIG process confirmed that the seven Montréal
Process criteria are relevant to all land tenures
and all forest types in Australia. However, consistent
with Australia's National Forest Policy Statement,
the application and importance of the criteria and
their respective indicators will vary among tenures
and broad forest types.
Of
the 67 Montréal Process (national) indicators,
30 have been accepted as regional-level indicators
and 10 have been classed as not relevant at a regional
level. Twenty-five national-level indicators have
been reworded to reflect regional issues more accurately,
and two indicators have been amalgamated with related
indicators. Twelve new or interim indicators have
been developed for use at the regional level. In summary,
the regional framework also has 67 indicators.
There
has been agreement in Australia that it is not possible,
practical or cost-effective to fully implement and
monitor all indicators in the framework at this time.
Therefore, the framework identifies three sub-sets
of indicators:
- Category A, which
can be measured immediately for most forests
- Category B, which
require further work on methods or resourcing before
indicators can be implemented
- Category C, where
significant research and development is required
to develop practical, sensitive and cost-effective
implementation (see Table 7).
Table
7. Phased implementation of indicators
|
Category
A- Largely implementable now
|
Category
B- Require some development
|
Category
C- Require longer-term R&D
|
|
1.1.a
Extent of area by forest type and tenure. (Amended
to include 1.1.c)
1.1.b Area of forest type by growth stage
distribution by tenure. (amended to include
1.1.d)
1.2.a A list of forest dwelling species.
1.2.b The status (threatened, rare, vulnerable,
endangered, or extinct) of forest dwelling species
at risk of not maintaining viable breeding populations,
as determined by legislation or scientific assessment.
2.1.a Area of forest land and net area
of forest land available for timber production.
2.1.d Annual removal of wood products
compared to the sustainable volume.
2.1.f Area and per centage of plantation
established that meets effective stocking one
year after planting.
2.1.g Area and per centage of harvested
area of native forest effectively regenerated.
3.1.a Area and per centage of forest
affected by processes or agents that may change
ecosystem health and vitality. (A narrative
as interim)
4.1.a (Interim) Area and per centage
of forest land systematically assessed for soil
erosion hazard, and for which site-varying scientifically-based
measures to protect soil and water values are
implemented.
6.2.c Number of visits per annum.
6.5.a Direct and indirect employment
in the forest sector and forest sector employment
as a proportion of total employment. (Direct)
7.1 (Narrative) Extent
to which the legal framework (laws, regulations,
guidelines) supports the conservation and sustainable
management of forests.
7.2 (Narrative) Extent
to which the institutional framework supports
the conservation and sustainable management
of forests.
7.4 (Narrative) Capacity to measure
and monitor changes in the conservation and
sustainable management of forests.
7.5 (Narrative) Capacity
to conduct and apply research and development
aimed at improving forest management and delivery
of forest goods and services.
|
1.1.e
Fragmentation of forest types.
5.1.a Total forest ecosystem biomass
and carbon pool, and if appropriate, subtotals
by forest type, age class, and successional
stages.
6.1.a Value and volume of wood and wood
products production, including value added through
downstream processing.
6.3.a Value of investment, including
investment in forest growing, forest health
and management, planted forests, wood processing,
recreation and tourism.
6.4.a(i) (priority areas) Area and per
centage of forest lands in defined tenures,
management regimes and zonings which are formally
managed in a manner that protects Indigenous
peoples' cultural, social, religious and spiritual
values, including non-consumptive appreciation
of country.
6.4.a(ii) Proportion of places of non-Indigenous
cultural values in forests formally managed
to protect these values.
6.5.a Direct and indirect employment
in the forest sector and forest sector employment
as a proportion of total employment. (Indirect)
6.6.a Extent to which the management
framework maintains and enhances Indigenous
values including customary, traditional and
native title use by Indigenous peoples and for
Indigenous participation in forest management.
|
1.2.c
Population levels of representative species
from diverse habitats monitored across their
range.
1.3.a Amount of genetic variation within
and between populations of representative forest
dwelling species.
3.1.a Area and per centage of forest
affected by processes or agents that may change
ecosystem health and vitality.
3.1.c Area and per centage of forest
land with diminished or improved biological,
physical and chemical components indicative
of changes in fundamental ecological processes.
4.1.c Per centage of stream kilometres
in forested catchments in which stream flow
and timing have significantly deviated from
the historic range of variation.
4.1.d Area and per centage of forest
land with significantly diminished soil organic
matter or changes in other soil chemical properties
or both.
4.1.d (Interim) The total quantity of
organic carbon in the forest floor (components
< 25 mm in diameter) and the surface 30 cm
of soil.
4.1.e Area and per centage of forest
land with significant compaction or change in
soil physical properties resulting from human
activities.
4.1.f Per centage of water bodies in
forest areas (e.g., stream kilometres, lake
hectares) with significant variance of biological
diversity from the historic range of variability.
6.1.b Value and quantities of production
of non-wood forest products.
6.2.b Number, range and use of recreation
and tourism activities available in a given
region.
6.5.c(i) Viability and adaptability to
changing social and economic conditions of forest
dependent communities.
6.5.c(ii) Viability and adaptability
of forest dependent Indigenous communities.
|
| Total:
12 indicators and 4 sub-criteria |
Total:
8 indicators |
Total:
13 indicators |
Research
and development work is being funded for these indicators.
As this research is completed, the indicators will
be reviewed to establish the feasibility of their
inclusion in Category A. The three categories cover
all seven Montréal Process criteria, and provide
a strategy for phased implementation.
The
remaining 20 indicators are not seen as having a high
priority for regional implementation, or for research
and development, over the short to medium term. However,
they may be important in particular regions and could
be adopted where needed.
Although
Australia is committed to monitoring and reporting
against the regional framework of criteria and indicators,
there is no expectation of uniform implementation
of indicators across the nation. It is also worth
noting that the framework is not legally binding,
nor is it a compliance document or an operations manual.
The
ability of agencies, industry, forest owners and growers,
and the broader community to contribute to monitoring
will vary.
Links
with Other Domestic and International Activities
There
are important linkages between the implementation
of the framework and work being undertaken on other
key initiatives, including Australia's Regional Forest
Agreement process, the National Forest Inventory,
State of the Forest and State of the Environment reporting,
greenhouse activities, and international reporting.
Not only does the framework provide a common approach
to monitoring, with the specific purpose of progressively
improving forest management on all land tenures, it
endeavours to avoid duplication in forest-related
data collection. The framework will allow aggregation
of data from the regional level to a State and national
level in a transparent and credible way in both Regional
Forest Agreements (RFAs) and non-RFA regions.
Regional
Forest Agreements
A key
element of the approach adopted in Australia's National
Forest Policy Statement involves RFAs between the
Commonwealth and State governments, which are being
developed following comprehensive studies of forest
values and consultation with stakeholders. The agreements
will seek to conserve the full suite of environmental
and heritage values that forests can provide for current
and future generations by ensuring that the forest
conservation reserve system is comprehensive, adequate
and representative, and through the complementary
management of forests outside reserves. Secure access
to wood resources will be provided through these agreements,
enabling continued development of internationally
competitive and ecologically sustainable industries.
The RFAs cover over 25 million hectares (approximately
16 per cent of the forest estate). To date, all signed
RFAs have included references to identification of
sustainability indicators based on the regional framework.
Considerable progress has been made in New South Wales
and Tasmania on identification of indicators for monitoring.
Although preliminary resource assessment has been
undertaken on private native forests in most RFA areas,
only Tasmania has included both the private and the
public forest in their final resource analysis.
National
Forest Inventory
The
National Forest Inventory (NFI) was established in
1988 by the Commonwealth, State and Territory governments
to co-ordinate the gathering and use of forest information
nationally. Ministerial Councils have tasked the NFI
with the production of five-yearly State of the Forest
reports based on the regional framework.
State
of the Forests and State of the Environment Reporting
Ministerial
Councils have also agreed that the preparation of
national State of the Forest reports be aligned with
all other national and international reporting requirements.
This means that the State of the Environment and Montréal
Process reporting will be based on data collected
for the regional framework.
Greenhouse
As
part of Australia's National Greenhouse Strategy,
a number of activities are being undertaken that will
improve knowledge of the contribution forests make
to carbon fluxes and sinks. A Co-operative Research
Centre for Greenhouse Accounting was established in
1999 and will undertake research aimed at increasing
certainty in measurement and predictions of stocks
and fluxes of carbon in Australian vegetation at both
continental and project scales. Information gathered
will be directly related to Criterion 5 of the regional
framework. A National Carbon Accounting System is
being developed within the Australian Greenhouse Office
that provides a comprehensive framework for reporting
storage and emissions of carbon dioxide and other
greenhouse gases in the Australian landscape. These
two initiatives will provide a basis for State and
national agencies reporting under Criterion 5.
Certification
and Labelling
Australia
acknowledges that the Montréal Process criteria
and indicators have no automatic link to certification
and labelling. Certification and labelling schemes
could draw on information and methods employed in
this assessment of SFM (including relevant criteria
and indicators). An Australian Forestry Standard is
being developed, as a basis for voluntary certification,
by Australian Commonwealth, State and Territory forestry
ministers. The standard will be developed through
a process that actively solicits and transparently
considers the views of a wide range of stakeholders.
Such an approach would seek to combine environmental
performance elements that address the Montréal
Process criteria and systems elements drawn from ISO
14001. Australia will also be seeking to co-operate
with Montréal Process countries and other interested
countries to explore an internationally co-operative
approach to certification and labelling.
International
Reporting
As
mentioned previously, data collected for the regional
framework will be used for international reporting
to the Montréal Process. The criteria are equivalent
and the indicators are largely the same. Australia
has contributed to the Global Forest Resources Assessment
2000 Programme by responding to the assessment enquiry
in 1998-99 and also by participating in the development
of a Global Ecological Zone Map.
International
Co-operation
Australia
has been active in international co-operation on criteria
and indicators. Australia and China have jointly organised
two workshops, the first of which was held in Fuzhou,
China, in December 1997 and investigated China's national-level
indicators. The second was held in Melbourne following
the Conference of International Union of Forestry
Research Organizations in August 1998 and aimed to
accelerate progress on implementation of criteria
and indicators through capacity and confidence building.
Highlights
of Work being Undertaken at State and Territory Level
In
New South Wales, the State Forests Service (NSW SF)
commenced implementation of criteria and indicators
for sustainability in 1997 prior to completion of
the regional framework. The initial 17 indicators
selected by NSW SF after extensive consultation fitted
under the Montréal Process criteria and were
reported on in the first Environmental and Social
Values Report of 1997-98. From 1999 onward, the Category
A indicators are being incorporated into the State
Forests sustainability monitoring process. Discussions
are in progress with other agencies to co-ordinate
implementation of criteria and indicators on other
tenures.
In
Victoria, the RFAs specify that a set of sustainability
indicators will be established to monitor forest changes
and that these will be consistent with the Montréal
Process criteria and indicators. Research and development
programmes have been reconfigured to address the need
to monitor against indicators. With respect to native
forests, Victoria has identified a number of Montréal
Process indicators considered relevant to its forests,
for which information can be provided now and after
further research and development. The private forests
sector in Victoria is assessing options for implementation.
Queensland
expects to utilise indicators in its RFA process.
The Department of Natural Resources has undertaken
substantial work in developing these indicators and
is developing an implementation strategy for Category
A indicators. A three-tier monitoring strategy is
being advanced which involves long-term reference
sites, permanent plots and temporary plots. Queensland
has initiated and is further developing research and
monitoring projects for Category B and C indicators.
Queensland is considering expanding the forest monitoring
plots to regions outside the RFA area, and to include
privately owned forests and reserve systems.
Western
Australia will focus on Category A indicators. Limited
data are available for forested lands that are not
managed by the Department of Conservation and Land
Management, that is, land vested in or owned by other
government agencies or local government and private
and leasehold land. The initial focus will be on the
RFA area. Future work is likely to address the temperate
and tropical areas. Partnerships with other agencies
and organisations will be required.
Tasmania
is unique in that the whole state is an RFA area.
Tasmania, together with stakeholders and the Commonwealth,
intends to identify a set of indicators that will
be used for monitoring the RFA by December 1999.
In
those State and Territories where RFAs are not being
pursued, the focus on implementation of indicators
is variable. The South Australian forest management
agency, ForestrySA, manages a sizeable plantation
estate with only a relatively small area of multiple
use forest. The state has recognised the importance
of advancing implementation of indicators for the
entire forest sector in South Australia.
Interestingly,
it is production forest agencies that have been leading
the way on implementation. A continuing effort is
required to ensure that all forest management agencies
are engaged in the process and that innovative mechanisms
for engaging industry, private forest owners and growers,
academia, research bodies and the community are developed.
It
is essential that the linkages among the above activities
are strengthened and duplication avoided, if not eliminated.
Research
and Development
As
mentioned above, to assist with the implementation
of the framework of regional indicators, research
is being undertaken into the development and implementation
of cost-effective and practical indicators of SFM.
The Forest and Wood Products Research and Development
Corporation manages the funds on behalf of Agriculture,
Fisheries and Forestry - Australia (AFFA). Brief details
of the projects are provided in Table 8.
Tables
9 to 13 provide core data on some Category A indicators.
Table
8. Forest sustainability indicator research and development
projects
|
Title
of project (related indicator)
|
Progress
and key contact
|
|
Direct
and indirect employment in the forest sector
and forest sector employment as a proportion
of total employment (6.5a).
|
Concluded
- The Final Report, including recommendations,
will be available by mid-1999.
Contact: John Dargavel, Australian National
University
Phone: 61(0)2 6249 2118 Fax: 61 (0) 2 6249 0312
|
|
Soil-based
information for developing sustainable plantation
forestry in Australia (4.1d, 4.1e).
|
This
project is an extension of a current project
investigating plantation sustainability indicators
and is not due to commence until October 1999.
Contact: Russell Haines, Queensland Forest Research
Institute
Phone: 61 (0) 7 3896 9703 Fax: 61 (0) 7 3896
9848
|
|
Evaluation
of key soil indicators of sustainability in
Australian mediterranean forests (4.1d, 4.1e)
.
|
In
progress.
Contact: John McGrath, Western Australia Conservation
and Land Management
Phone: 61 (0) 8 9334 0303 Fax: 61 (0) 8 9334
0326
|
|
Evaluation
of soil organic matter as a meaningful indicator
of important soil properties and processes in
native forest ecosystems (4.1d, 4.1e).
|
In
progress. Soil samples collected from trial
sites for laboratory analysis.
Contact: Jurgen Bauhus, Australian National
University
Phone: 61 (0) 2 6249 2748 Fax: 61 (0) 2 6249
0746
|
|
Procedures
for the measurement of changes in soil physical
properties following logging of wet Eucalyptus
obliqua forest, and the subsequent effect
on site productivity (4.1e).
|
In
progress.
Contact: Bill Neilsen, Forestry Tasmania
Phone: 61 (0) 3 6233 8225 Fax: 61 (0) 3 6233
8292
|
|
Effect
of forest harvesting on soil physical properties:
developing and evaluating meaningful soil indicators
of sustainable forest management in South Eastern
Australia (4.1d).
|
In
progress.
Contact: Stephen Lacey, State Forests Service
of New South Wales
Phone: 61 (0) 2 9872 0111 Fax: 61 (0) 2 9871
6941
|
|
Development
and implementation of landscape metrics for
reporting forest fragmentation at field and
landscape levels (1.1e).
|
In
progress.
Contact: Phil Norman, Queensland Department
of Natural Resources
Phone: 61 (0) 7 3896 9830 Fax: 61 (0) 7 3896
9858
|
|
Identification
of species and functional groups that give early
warning of major environmental change (1.2c).
|
In
progress.
Contact: Rod Kavanagh, State Forests Service
of New South Wales
Phone: 61 (0) 2 9872 0160 Fax: 61 (0) 2 9871
6941
|
|
Development
of indicators of genetic diversity in managed
native forests (1.3a, 3.1c, 1.1e, 1.2c).
|
Scoping
study concluded, consideration being given to
follow-up work.
Contact: Gavin Moran, CSIRO Forestry and Forest
Products
Phone: 61 (0) 2 6281 8211 Fax: 61 (0) 2 6281
8312
|
|
Regeneration
success measures and monitoring methods for
sustainable forest management in native forest
(2.1g).
|
In
progress.
Contact: John Kellas, Centre for Forest Tree
Technology - Victoria
Phone: 61 (0) 3 9450 8666 Fax: 61 (0) 3 9450
8644
|
|
Testing
and refinement of AUSRIVAS for the detection,
assessment and interpretation of changes in
stream diversity associated with forestry operations
(4.1f).
|
In
progress.
Contact: Bill Neilsen, Forestry Tasmania
Phone: 61 (0) 3 6233 8225 Fax: 61 (0) 3 6233
8292
|
|
Development
of an agreed framework for consultation and
for input of indigenous knowledge pertinent
to the Montréal indicators for ecologically
sustainable forest management at a regional
level (6.6a).
|
In
progress.
Contact: Alan Black, Edith Cowan University
- Western Australia
Phone: 61 (0) 8 9400 5844 Fax: 61 (0) 8 9400
5866
|
|
Indicators
of changes in fundamental ecological processes
in forests based on crown condition, landscape
function analysis and biotic indicators (3.1c).
|
Scoping
study report submitted - new proposal being
considered.
Contact: Ken Old, CSIRO Forestry and Forest
Products
Phone: 61 (0) 2 6281 8211 Fax: 61 (0) 2 6281
8312
|
Table
9. Tenure of major native forest types
[Indicator 1.1.a - extent of area by forest type and
tenure (incorporates indicator 1.1.c)]
| |
Tenure
area (thousand ha)
|
|
Forest
type
|
Private
|
Leasehold
|
Conserved
|
Other
|
Multiple-use
|
No
data
|
Australia
(thousand ha)
|
|
Eucalypt
|
33
178
|
50
681
|
14
961
|
13
940
|
10
728
|
974
|
124
463
|
Tall
|
1
372
|
583
|
1
469
|
110
|
3
006
|
4
|
6
543
|
Medium
|
28
640
|
35
121
|
9
232
|
10
178
|
7
391
|
888
|
91
450
|
Low
|
988
|
12
056
|
658
|
787
|
139
|
72
|
14
700
|
Mallee
|
2
174
|
2
920
|
3
602
|
2
864
|
193
|
11
|
11
764
|
Unknown
|
5
|
(1)
|
0
|
(1)
|
(1)
|
0
|
6
|
|
Acacia
|
2
784
|
8
525
|
276
|
608
|
99
|
7
|
12
298
|
|
Melaleuca
|
949
|
2
560
|
424
|
86
|
45
|
29
|
4
093
|
|
Rainforest
|
1
017
|
414
|
812
|
220
|
1
093
|
26
|
3
583
|
|
Casuarina
|
81
|
919
|
39
|
6
|
6
|
(1)
|
1
052
|
|
Mangrove
|
422
|
118
|
231
|
146
|
1
|
126
|
1
045
|
|
Callitris
|
197
|
300
|
69
|
8
|
292
|
(1)
|
867
|
|
Other
|
3
390
|
2
586
|
770
|
582
|
1
086
|
22
|
8
435
|
|
Total
native forest
|
42,018
|
66,103
|
17,580
|
15,597
|
1,351
|
1,186
|
155,835
|
|
Plantation
softwood
|
931
|
|
Plantation
hardwood
|
291
|
|
Total
plantations
|
1
222
|
|
Total
forest
|
157
057
|
Area
less than one thousand hectares
Note: Column or row total may not add up due to
rounding
Source: National Forest Inventory 1998 and National
Plantation Inventory 1999 |
Table 10 Australia - Nature Conservation
Reserves, area by forest type and age
[Indicator 1.1.b - Area of forest type by growth
stage distribution by tenure (incorporates indicator
1.1.d)]
| |
By
age (thousand ha)
|
|
Forest type
|
Total forest area
|
Total
area for which age class is known
|
Establishment
1-10 years
|
Juvenile 11-30 years
|
Immature 31-100 yr
|
Mature 100-200 yr
|
Senescent > 200 yr
|
Two (mixed) aged
|
Three
or more aged
|
|
Rainforests
|
812
|
177.0
|
|
|
|
177
|
|
|
|
|
Tall
open eucalypt
|
1
435
|
184.9
|
0.1
|
5.2
|
19.4
|
95
|
|
19
|
46.2
|
|
Medium
open eucalypt
|
3
388
|
756.3
|
0.1
|
0.5
|
41.0
|
203
|
|
49
|
462.7
|
|
Low
open eucalypt
|
17
|
|
|
|
|
|
|
|
|
|
Tall
eucalypt
|
34
|
|
|
|
|
|
|
|
|
|
Medium
eucalypt
|
5
844
|
|
|
|
|
|
|
|
|
|
Low
eucalypt
|
641
|
|
|
|
|
|
|
|
|
|
Eucalypt
mallee
|
3
602
|
|
|
|
|
|
|
|
|
|
Callitris
|
69
|
|
|
|
|
|
|
|
|
|
Acacia
|
276
|
|
|
|
|
|
|
|
|
|
Other
|
1
463
|
31.0
|
|
|
|
|
|
|
31.0
|
|
Total
|
17,580
|
1,149.2
|
0.2
|
5.7
|
60.4
|
475
|
0
|
68
|
539.9
|
Notes:
1. For Nature Conservation Reserves, New
South Wales did not provide age-class information
by forest type, so the State's data is not included
in this national sum.
2. New South Wales reports on the six eucalypt
forest types combined, which total an area of
655 017 ha, composed of three age classes (75
980 ha of juvenile, 475 095 ha of senescent and
103 942 ha of immature and mature combined).
3. Tasmania merges all age class data for
mature and senescent and reports it under mature.
Source: National Forest Inventory 1998 |
Table
11 Australia - Multiple-use forests by forest type and
age
[Indicator 1.1.b - Area of forest type by growth stage
distribution by tenure (incorporates indicator 1.1.d)]
| |
By
age (thousand ha)
|
|
Forest type
|
Total
area for which ageclass is known
|
Establishment
1-10 years
|
Juvenile
11-30 years
|
Immature 31-100 yr
|
Mature 100-200 yr
|
Senescent > 200 yr
|
Two (mixed) aged
|
Three
or more aged
|
|
Rainforests
|
341
|
|
|
|
195
|
80
|
|
66
|
|
Tall
open eucalypt
|
1
984
|
73
|
150
|
273
|
378
|
364
|
133
|
614
|
|
Medium
open eucalypt
|
2
971
|
22
|
150
|
147
|
647
|
266
|
171
|
1
568
|
|
Low
open eucalypt
|
|
|
|
|
|
|
|
|
|
Tall
eucalypt
|
|
|
|
|
|
|
|
|
|
Medium
eucalypt
|
1
360
|
|
|
|
|
546
|
|
814
|
|
Low
eucalypt
|
|
|
|
|
|
|
|
|
|
Eucalypt
mallee
|
|
|
|
|
|
|
|
|
|
Callitris
|
225
|
|
|
|
|
|
|
225
|
|
Acacia
|
|
|
|
|
|
|
|
|
|
Other
|
74
|
|
|
|
|
|
|
74
|
|
Total
|
6
955
|
95
|
300
|
420
|
1
219
|
1
256
|
304
|
3
361
|
Note:
State definitions of forest types may differ from
each other and from the national definitions,
potentially resulting in different categorisations.
Source: National Forest Inventory 1998 |
Table
12 Number of species known to occur in Australian forests
[Indicator 1.2.a - A list of forest dwelling species]
|
Species
known to occur in forests
|
Number
of species
|
|
Mammals
|
317
|
|
Birds
|
561
|
|
Reptiles
|
219
|
|
Amphibians
|
126
|
|
Fish
|
16
|
|
Higher
plants
|
13
622
|
|
Rare
or threatened vertebrates
|
81
|
| Source:
National Forest Inventory 1998 |
Table
13 Area of native forest under multiple-use forest tenure
available for harvesting, by State and Territory
[Indicator 2.1.a - Area of forest land and net area
of forest land available for timber production](1)
| |
Total
multiple-use forested
(thousand ha) (2)
|
Per
centage forested
of
total multiple-use(3)
|
Total
multiple-use area
(thousand ha) (4)
|
|
Australian
Capital Territory
|
5
|
20.2
|
23
|
|
New
South Wales
|
3
095
|
81.1
|
3
814
|
|
Northern
Territory
|
-
|
-
|
-
|
|
Queensland
|
3
983
|
91.7
|
4
346
|
|
South
Australia (3)
|
27
|
21.0
|
126
|
|
Tasmania
|
1
285
|
79.0
|
1
627
|
|
Victoria
|
3
346
|
90.2
|
3
710
|
|
Western
Australia
|
1
612
|
82.1
|
1
962
|
|
Australia
|
13
351
|
85.5
|
15
608
|
Notes:
(1) Does not include timber production
data from private and other tenures
(2) Forested portion of multiple-use forests.
Per centages relate to exact figures, not the
rounded figures given in this table
(3) Includes unforested areas
(4) No harvesting of publicly owned native
forest takes place in South Australia.
Column or row total may not add up due to rounding.
Source: National Forest Inventory 1998. |
Future
Activity
Australia
recognises that the implementation of criteria and
indicators will require significant effort in the
future. The key challenges are to address a number
of major impediments, including the following:
- Lack of consistency
and different methods of data collection and format
among States
- Poor or no data
from non-commercial forests on public land and from
essentially all forests on privately managed land
- Lack of knowledge
and commitment to criteria and indicators by private
forest growers and lessees
- Lack of integration
of RFA data into indicator format
- Amount of research
and development required to implement some of the
indicators
- Scarcity of resources
for removing these impediments and advancing progressing
implementation.
However,
even with these impediments, Australia considers that
significant progress has been made since 1997. In
particular, there is better co-ordination across activities
at both the State or Territory and national levels,
as well as recognition that duplication needs to be
removed.
Australia's
regional framework is, and will continue to be, viewed
as a dynamic document that can reflect variables such
as changes in community expectations and improvement
in knowledge. One of the key tasks for the future,
in the implementation of indicators at a regional
level, is the need to develop objectives, targets
and standards in accordance with management requirements
and objectives against which trends in indicators
can be measured.
In
terms of reporting, the following commitments will
utilise data collected for the regional framework
of indicators:
- Category A indicators
(regular national reporting with first scheduled
for 2000)
- National State of
the Environment Report (2001), supported by State
and Territory level reports
- State of the Forests
Report (2003)
- Montréal
Process Report (2003)
Internationally,
Australia continues to participate in the Montréal
Process Working Group and its Technical Advisory Committee.
We believe opportunities exist for sharing experiences
with other countries both within the Montréal
Process and more broadly, and will continue to promote
such co-operation.
Further
information is available at the following web sites:
http://www.affa.gov.au/ffid/sir/criteria/
http://www.fwprdc.org.au
References
- Australian Bureau
of Statistics. 1995. Australia Year Book.
AGPS, Canberra
- Commonwealth of Australia
1997, Australia's First Approximation Report to
the Montréal Process - June 1997, Montréal
Process Implementation Group, Australia
- National Forest Inventory
1998, Australia's State of the Forests Report 1998,
Bureau of Rural Sciences, Canberra
- National Plantation
Inventory 1999, National Plantation Inventory 1999
- The Tabular Report, Bureau of Rural Sciences,
Canberra (only available through the website: www.brs.gov.au/nfi/activities/npi/interim.html
)
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VIGNETTE
ON CANADA
Canada's
Forests
Canada
is known for the abundance of its natural resources
and, in particular, the vastness of its forests-nearly
half the nation's land area. Our forests are part
of our heritage and national identity, and are viewed
as a legacy to be sustained and passed on. These living,
life-supporting ecosystems provide Canadians with
ecological and environmental services, as well as
economic and social benefits ranging from the material
to the spiritual.
Canada
is unusual among forest nations in that most of its
forests are publicly owned and are overseen by governments.
Seventy-one per cent of the forests are under provincial
jurisdiction, 23 per cent are under federal jurisdiction
(some managed by or in co-operation with the territorial
governments), and the remaining 6 per cent are in
the hands of an estimated 425 000 private landowners.
Under
the Canadian Constitution, the provinces retain responsibility
for forest management, and each province has its own
legislation, regulations, standards and programs through
which it allocates harvesting rights and management
responsibilities for the public forest. In the Northwest
Territories the responsibility for forest management
has been transferred from the federal to the territorial
governments and a similar transfer is being negotiated
with the Yukon Territory. In recognition of the broad
spectrum of forest users, governmental agencies seek
public views and work closely with forest industries,
Aboriginal groups and environmental organisations
to incorporate recreational, social, wildlife and
economic values into forest management planning and
decision-making.
In
ecological terms, there are eight forest regions in
Canada, ranging from the tall towering coastal rainforests
in British Columbia to the sparse, slow-growing forests
at the Arctic tree line. Each region has a distinct
distribution of plant and animal species; an estimated
180 species of trees occur in different parts of the
country. Canada can also be described as having 15
terrestrial ecozones, 194 ecoregions, and more than
a thousand ecodistricts.
The
forests were once viewed primarily as sources of timber,
and forestry was based on the economics of harvesting.
Today, forest management also includes economic, environmental,
social and cultural considerations. To find flexible
and balanced ways of integrating these factors - a
challenging task given the complexity and size of
the resource and the diverse interests of the forest
community - Canada is continually re-examining and
adjusting its policies and engaging its collective
ingenuity to sustainably manage its forests. Criteria
and indicator (C&I) initiatives, at both the national
and international levels, are key components of Canada's
efforts to measure and report on sustainable forest
management (SFM).
Measuring
Sustainable Forest Management at the National Level
With
the global shift in approach from sustained yield
to SFM, Canada has faced a variety of new demands:
- The need to broaden
traditional forest policies and practices to integrate
many non-timber, as well as timber, values
- The need to develop
a better understanding of how forest systems work
from ecological, social and economic perspectives
- The need to encourage
co-operation and partnerships among a broad range
of forest users
- The need to define
a set of forest values for the nation to adopt,
sustain and enhance.
In
addition to its participation in the Montréal
Process, Canada has taken a number of steps domestically
to promote SFM. In early 1992 - a few months prior
to the UN Conference on Environment and Development
and after two years of national consultations - Canada's
forest community and the public agreed that science-based
C&I were an important tool in achieving SFM. This
agreement was subsequently reflected in the National
Forest Strategy, Sustainable Forests: A Canadian
Commitment (1992-1998), which included 96 action
items to guide forest management.
In
1993, the Canadian Council of Forest Ministers (CCFM)
began an initiative to measure and report on forest
values that Canadians consider important, and in 1995,
after year-long consultations, the council adopted
a national framework of C&I. This framework reflects
an approach to forest management that recognises forests
as ecosystems providing a wide range of environmental,
economic and social benefits to Canadians.
CCFM
C&I Framework
The
intention of the CCFM in developing the C&I framework
was to:
- Clarify the meaning
of SFM and provide a framework for describing and
assessing it at a national level
- Provide a reference
point for the development of policies on the conservation,
management and sustainable development of forests
- Contribute a scientific
and policy basis for the clarification of issues
related to environment and trade, including product
certification
- Provide concepts
and terms to facilitate domestic and international
dialogue on SFM
- Improve the information
available to the public and decision-makers.
An
analysis of the CCFM C&I framework and the Montréal
Process framework has indicated that the two systems
are compatible, with approximately 80 per cent similarity.
Although the CCFM indicators reflect the particular
features of Canada's forests, the CCFM criteria are
consistent with the first six criteria of the Montréal
Process. Some of the indicators under criteria 5 and
6 of the CCFM framework are similar to those found
under the seventh criterion of the Montréal
Process (legal, institutional and economic framework
for forest conservation and sustainable management).
In
1997, on behalf of the CCFM, a network of forest experts
from the provinces and territories, industry organisations,
non-governmental organisations, academic institutions
and professional forestry associations prepared a
detailed document that described Canada's capacity
to report on each of the 83 indicators. That document
was entitled Criteria and Indicators of Sustainable
Forest Management in Canada, Technical Report.
To communicate the network's findings to a broader
audience, a more concise and less technical version
of the report also was released, entitled Criteria
and Indicators of Sustainable Forest Management in
Canada, Progress to Date. Preparation of these
two reports led to a better understanding of Canada's
strengths and weaknesses with respect to our capacity
to measure forest sustainability.
In
1998, Canada renewed its commitment to sustainable
forests in the National Forest Strategy (1998-2003).
In particular, the new Strategy addresses the need
to develop objective measures for testing and demonstrating
sustainability under the national framework of C&I,
and it commits to action plans for regular reporting
on Canada's progress toward SFM. (Canada will report
on its progress in April 2000, at the United Nations
Commission on Sustainable Development in New York
City.)
Implementing
Criteria and Indicators at the Sub-national Level
Under
the National Forest Strategy, several provinces have
adopted provincial sets of C&I, and many are preparing
to incorporate them into their forest management planning.
In addition, some provinces have taken steps to integrate
C&I into their forest legislation, while others
are considering that possibility. Quebec, for example,
amended its Forest Act to include the six criteria
from the CCFM C&I framework and has developed
a framework of 60 indicators (many of which are similar
to those of the CCFM) which it expects to implement
over a three-year period. Ontario, too, has drafted
a comprehensive set of indicators for use at the provincial
level in evaluating and reporting on forest sustainability.
In both of these provinces, the C&I have been
integrated into forest legislation and policies.
In
Newfoundland and Labrador, the government is drafting
a 20-year forestry development plan that will contain
specific references to a provincial set of C&I,
and it is considering having the indicators integrated
into legislation.
In
addition, Saskatchewan is developing indicators for
forest ecosystem health that are derived mainly from
the Montréal Process. And New Brunswick has
taken a slightly different approach, developing a
vision document for its forests that provides a framework
for forest management and sets out policy goals, as
well as explicit standards and objectives to be used
in the development of forest management plans on Crown
Timber Licences.
Developing
and Testing Criteria and Indicators at the Local Level
Canada's
Model Forest programme was established in 1992 by
Natural Resources Canada-Canadian Forest Service to
develop and demonstrate innovative approaches to SFM.
At the core of each model forest is a partnership
of people who collaborate in working toward their
shared objective of SFM within the social, economic
and ecological conditions of their own forest area.
(Together, the network of 11 model forests represents
the diversity and complexity of the major forest regions
of Canada.)
An
important focus for each model forest in Phase II
of the programme (1997-2002) was the establishment
of processes for the development, testing, application
and monitoring of local-level indicators of SFM, based
on the CCFM C&I framework. The guidelines for
the indicators' development required that they be
based on appropriate scientific attributes; be easily
and readily measured; demonstrate the best management
practices available; be adaptive, replicable by others
and relevant on a temporal basis (reflecting links
between changes in economic, social and environmental
circumstances); and be able to show trends in behaviour
and attitudes.
The
suites of local-level indicators can be used by each
of the model forests to describe its progress toward
SFM. In addition, a network-wide initiative is enabling
the model forests to share their experiences, expertise
and information and help each other achieve their
own suites of local-level indicators. As of 31 March,
1999, each model forest had developed a set of indicators.
Although some sites are in the process of refining
their initial master set, several are beginning to
develop protocols for monitoring and reporting the
indicators.
This
approach to developing suites of local-level indicators
has been adopted by various industries and provincial
governments. Currently, Newfoundland, Manitoba and
Alberta are using and supporting the model forest
process to develop regional and provincial indicators.
Also, partner industries at Manitoba Model Forest,
Fundy Model Forest and Foothills Model Forest are
adopting these approaches for their forest management
planning and are linking the indicators to their certification
requirements.
New
Rules and Regulations
Across
the country, new forest laws based on the principles
of sustainability and stricter enforcement of policies
and guidelines indicate that steps are being taken
by an increasing number of provinces and territories
in response to the demands of SFM. For example, in
recent years, many provinces have passed legislation
or introduced regulations governing forestry operations
on Crown land.
British
Columbia, for instance, has opted to address most
of the aspects covered under the C&I through legislation,
administration and research. Alberta has developed
a framework that reflects the public's desire to maintain
its access to the wide range of benefits provided
by sustainable forest ecosystems. In addition, a number
of provinces have announced incentives to encourage
the sustainability of private woodlots through tax
rebates, financing for silvicultural activities and
education.
Government
agencies across Canada have, without exception, adopted
a consultative approach to developing forest policy.
They routinely seek public views and work closely
with industries, Aboriginal groups and environmental
groups to incorporate recreational, social, wildlife
and economic values into forest management planning
and decision-making.
New
Data Collection Systems
In
establishing and reporting on the CCFM C&I framework,
Canada has faced challenges in developing new approaches
to data collection and management (particularly for
non-timber values), in developing tools to measure
social values and in expanding its knowledge of forest
ecosystems. With respect to new approaches to data
collection and management, a number of initiatives
have evolved in response to C&I demands.
A new
National Forest Inventory is being proposed that will
be consistent nationally, describe all classes of
ownership, provide changes and trend estimates, be
compatible with ecological classification and allow
spatial and temporal reporting on multiple resource
attributes. For the past decade, the forest inventory
for Canada has been prepared by rolling up data from
provincial inventories, based on definitions that
were not always compatible. Approximately 30 per cent
of the indicators in the CCFM framework will be addressed
in the national inventory. In addition, some non-timber
values will be incorporated, such as the number of
forest-dependent species.
To
complement the new inventory, a National Forest Information
System has also been proposed, as a national system
for integrating and linking information on Canada's
forests. In addition, the Canadian Forest Service
is working with the Canadian Space Agency on a joint
project called Earth Observation for Sustainable Development
(EOSD). The project is designed to monitor the sustainable
development of Canada's forests and provide core information
requirements. It is estimated that the reporting requirements
of 25 of the 83 indicators could potentially be satisfied
through this remote sensing project.
Future
Reporting
The
pursuit of SFM is a dynamic and evolving process.
Criteria and indicators are based on the best information
available and, as such, they are subject to continual
revision and improvement. For example, several years
have passed since the CCFM C&I framework was developed,
and during that period, the capacities of information
systems have increased, the approaches to forest inventories
have changed and the availability of data for some
indicators has improved. Also, advances in science
have increased our understanding of systems and have
influenced our concept of SFM and our ability to measure
our progress toward that objective.
It
is in this light that the CCFM has approved a review
of the 83 indicators currently included in the C&I
framework. In addition, the Council has used the experience
and knowledge gained from the preparation of Canada's
first report to develop and approve an implementation
plan for reporting in 2000.
The
Task Force charged with preparing the implementation
plan has identified a core set of 49 indicators, which
they derived from the original 83 indicators by conserving
those consistent with ones found in other C&I
processes, combining similar indicators, and focusing
on indicators applicable at the national level. (In
fact, close to 70 indicators from the original framework
will be reported on in 2000.)
To
carry out the implementation plan and facilitate production
of the 2000 report, the Task Force established working
Internet and FTP sites. By providing templates for
data submission and compilation, these sites have
served to standardise the submission of data and information.
In addition, by linking the 75 technical contacts
across the country who provide the information for
the report with the 22 writers who compile the national
perspectives for the indicators, the sites have also
stimulated discussion regarding definitions and reporting
strategies, and have promoted the sharing of information
and ideas. The working web site also will be used
to identify sources of information and to archive
information for future reporting.
References
- Buchanan, K., and
M. McKennirey. 1996. Criteria and Indicators for
Sustainable Forest Management, Comparison of Montréal
Process and CCFM Frameworks. Can. For. Ser., Unpublished
Rep. 11 p.
- Goodenough, D. G.,
A. S. Bhogal, R., R. Fournier, R. J. Hall, J. Iisaka,
D. Leckie, J. E. Luther, S. Magnussen, O. Niemann,
and W. M. Strome. 1998. Earth Observation for Sustainable
Development of Forests (EOSD), Proc. 20th Canadian
Symposium on Remote Sensing, Calgary, Alberta. p.
57-60.
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VIGNETTE
ON CHILE
Introduction
Chile
is situated in the southwest part of South America,
extending southward to the Antarctic continent and
westward as far as Easter Island. On the South American
continent, it stretches from 17 degrees 30 minutes
latitude south to the Diego Ramirez islands at 56
degrees 30 minutes latitude south. The country has
a continental surface area of 75.4 million hectares,
of which 15.6 million hectares are classified as forests
(20.8 per cent) as recorded in the 1998 Natural Vegetation
Survey.
As
a result of this geographical scope, there is a wide
variety of climatic types, prominent among them desert,
steppe, Mediterranean, warm rainy temperate, rainy
maritime, cold steppe, tundra and polar climates.
With this geographical scope, the variety in latitude
and altitude makes it possible to find in Chile a
diversity of plant formations. Studies including one
by Gajardo in 1994 have determined that there are
eight vegetation regions and 21 vegetational subregions.
Chile
is divided into 13 political-administrative Regions,
nine of which contain temperate forest resources and
tree plantations. The four northernmost regions are
extremely arid and have scanty woodland areas that
do not contain temperate forests.
The
Ministry of Agriculture is responsible for the development
of policies for promotion of the country's agriculture,
livestock and forests. The Ministry performs its forest
management and conservation functions in accordance
with its legal authority and with a number of provisions
that enable it to operate through Services or Agencies.
These are dependent on the national government, but
they are administratively and geographically decentralised.
In this respect, the Forest Service (CONAF) is an
agency that belongs to the Ministry of Agriculture.
Its institutional mission is "To guarantee for
society the sustainable use of forest ecosystems and
the efficient management of the National System of
State-Protected Areas (SNASPE), for the purpose of
contributing to the improvement of quality of life
for present and future generations."
The
forest resources existing in Chile consist of native
forests, planted forests and a mixture of both, with
a total surface area of 15 647 894 hectares (Natural
Vegetation Survey, CONAF-CONAMA, 1998) (Figure 3).
Figure
3. Composition of Chile's forest
National
Initiatives that Promote the Montréal Process
National
survey of native vegetational resources
Since
1997 Chile has had a National Survey of Native Vegetation
Resources and a land use information system, tools
that facilitate the monitoring of changes in forest
area and the construction of area-based indicators
which are present in the Montréal Process.
The
instrument makes it possible to do the following:
- Locate, determine
dimensions and to a certain degree, characterise
the forests and the various natural plant formations
existing in the country
- Set up a digital
database for expeditious handling and updating of
information on the natural plant formations and
planted forests existing in the country
- Monitor changes
in land use and update the pertinent information.
Inasmuch
as the objective of the Survey is an evaluation for
environmental and economic purposes, the definitions
used pertain to concepts based fundamentally on the
structure of ecosystems or communities more than on
concepts related to utilisation. This establishes
a high degree of compatibility with the Montréal
Process, whose Introduction states, in point
1.3, that "The forest management approach reflected
in the criteria and indicators is the management of
forests as ecosystems." This conceptual approach
of both instruments makes it possible to implement
the Montréal Process indicators with a high
degree of correlation.
It
is estimated that 28 of the total of 67 indicators
of the Montréal Process can be applied based
on the Survey. However, and in line with the "Design
of a System for Follow-up and Monitoring of the State
of Conservation of Native Formations" project,
the development of the indicators listed under Criterion
1 will be given priority (Table 14).
Table
14. Relation of Montréal Criterion 1 to Chile's
Survey
|
Montréal
Criteria and Indicators
|
Degree
to which the Survey and its updates serve the
purpose
|
|
Criterion
N° 1 Conservation of Biological Diversity
|
Partially
|
|
Ecosystems
diversity
- Area by forest
type in relation to total forest area
- Area by forest
type and by age class or succession stage
- Area by forest
type in Protected Areas
- Area by forest
type in Protected Areas and by age class or
succession stage
- Fragmentation
of forest types
|
Fully
Partially
Fully
Partially
Partially
|
|
Species
diversity
- Number of
forest - dependent species
- Conservation
status of forest - dependent species
|
Partially
Fully
|
|
Genetic
diversity
- Number of
forest - dependent species which occupy a
small part of their original distribution
range
- Population
levels of species representative of diverse
habitats, measured periodically and systematically
throughout their distribution range
|
Partially
Partially
|
The
indicators that can be fully measured or calculated
on the basis of information contained in the Survey
of Native Vegetational Resources will be available
in CONAF's Inquiry System, through a subsystem. Thus,
for instance, it will be possible to ask for indicator
(a) of Criterion 1 Conservation of Biological Diversity
- in other words, area by forest type in relation
to total forest area at the level of a protected area,
a commune, a province, a region or the entire country.
Furthermore,
it will be possible to measure the indicators listed
under Criterion 2 once the Forest Information System
is developed (Table 15). This is a system that will
integrate data from CONAF's Survey of Native Vegetation
from a National Survey of Planted Forests prepared
by the Forestry Institute (INFOR).
Table
15. Relation of Montréal Criterion 2 to Chile`s
Survey
|
Montréal
Criteria and Indicators
|
Degree
to which the Survey and its updates serve the
purpose
|
|
Criterion
N° 2 Maintenance of the productive capacity
of forest ecosystems
- Area of lands
suitable for forestry and net area of woodlands
available for timber production
- Area and
volume of plantations of native and exotic
species
|
Partially
Fully
Fully
|
At
present, changes in land use are monitored and the
information is updated. This will make it possible
to have a platform upon which to begin to construct
the proposed indicators.
Permanent
Working Group for Sustainable Management of Chile`s
Forests
In
1996, the Permanent Working Group for Sustainable
Management of Chile`s Forests (GMS) was formed, as
collaboration with a project prepared by the Forestry
Institute (INFOR). Also participating, as founding
members of the GMS, were the Forest Service (CONAF);
the Chilean Wood Manufacturers Association (CORMA),
an organisation made up of the country's main forest
companies; the National Commission for the Environment
(CONAMA); and the Ministry of Foreign Affairs. At
present, the group also includes university representatives,
environmental organisations, the forest engineers
association and the small farmers association. One
of the specifically defined courses of action is the
search for consensus regarding sustainable forest
management (SFM).
With
the aim of attaining this consensus, an instrument
was designed which consists of a set of assertions
that reflect, to a greater or lesser degree, what
the different players think of SFM.
Concepts
expressed in various international and national initiatives,
both public and private in nature, were used in the
preparation of this questionnaire, the Montréal
Process being one of the foundations supporting the
development of this tool.
The
work of this group has not yet finished, but nevertheless
the progress attained has already made it possible
to approach a level of agreement between the parties.
Application
of Criteria and Indicators at the Local Level
CONAF's
Environmental Studies Unit is developing a proposed
method for the common understanding and evaluation
of SFM, backed by the framework of criteria and indicators
of the Montréal Process.
The
idea is that, based on a criterion, one can arrive
at a performance objective or goal which, in accordance
with the standard or norm, can be incorporated into
the forest management plan for evaluation in the field.
In themselves, the criteria and indicators constitute
a key component of the cycle of continuous improvement
of SFM, inasmuch as they can be converted into practical
objectives and means of measuring performance, for
the purpose of incorporating them into forest planning,
operating decisions and monitoring systems.
The
method is designed to facilitate the operational application
of SFM concepts, and with this the designing, management
and evaluation of the sustainability of plans, programmes
and projects at national and sub-national levels (region,
province, commune or forest management unit).
At
present there are two projects, headed by government
agencies with the backing of international co-operation
organisations, whose follow-up and monitoring plans
include the use of some indicators derived from the
Process for the evaluation of SFM at the local level.
They are being developed for demonstration purposes,
and are:
- Conservation of
Chile`s Temperate Natural Forest, Environmental
Criteria for Sustainable Management, Application
to the Pilot Area: Malleco Forest Reserve, Tolhuaca
National Park, and their Peripheral Area (CONAF/National
Forest Office of France agreement), this project
involves an area of approximately 30 000 hectares
- Management Plan
for the Valdivia National Reserve, this is part
of a project on the Sustainable Management of Natural
Forests (CONAF/German Technical Co-operation Society,
GTZ, agreement), and involves an area of approximately
16 000 hectares.
Management
of National Forect Reserves
Innovations
are being introduced in management and harvesting
within the National Reserves. These innovations are
in line with the principles that will guide forest
development in the 21st Century, and are
based on the criteria of the Montréal Process.
They aim to offer present and future generations a
forest heritage that is biologically and ecologically
stable, highly productive, and of great adaptability
in the face of changes in the environment and in social
demands. The sustainable utilisation of natural resources
is promoted, combining production of goods and services
with the needs of the nearby peasant and indigenous
communities, as well as the demands of the increasingly
urban population of the country.
This
new forest management model will have the following
fundamental objectives:
- Sustainable production,
ensuring the permanent existence of well-managed
forests, adapted to the site
- Protection or recovery
of the biodiversity
- Social development
based on a participatory process including the communities
linked with the forest or forest activities
- Appreciation of
the natural forest by the national community.
Chiloe
Model Forest
Chile,
with its "Chiloe Model Forest," has been
part of the International Model Forest Network since
1998. The strategic vision of the Chiloe Model Forest
proposition is to increase utilisation of the natural
resources associated with forest ecosystems, maintaining
the ecological characteristics and processes of these
systems. Key components are the search for, development,
and implementation of, new and innovative approaches,
practices and technologies. These would be based on
the generation of a solid knowledge base on the dynamics
of the ecosystems involved and their characteristics,
functions and interrelations, as well as on the participation
and recognition of the interests and viewpoints of
all the social groups interested in the forests or
dependent upon them. Thus, combining scientific knowledge,
an ecological approach and a social approach, it is
possible to develop and apply a system of integrated
management of the natural resources, which is accepted
by all stakeholders.
Among
the objectives of the Chiloe Model Forest is that
of providing support in the development and application
of criteria and indicators. To this end, it has incorporated
into its negotiation and implementation of SFM, the
concepts developed by the Montréal Process.
A first
evaluation will be made to determine the degree of
fulfilment attained which will make it possible to
obtain feedback for the purpose of improving the project.
Forest
Contribution to Global Carbon Cycles
Chile
is a signatory country to the Framework Convention
on Climate Change (FCCC). There are many commitments
that are common to FCCC and the Montréal Process
criteria and indicators.
Regarding
Criterion 5, it is relevant to mention that there
is an important government-funded research project
aimed at developing methodologies to determine the
carbon status of planted and indigenous forests, considering
different species and forest types. The results of
this project will enable Chile to report on this criterion
by the year 2002-03.
Legal,
Institutional and Economic Framework
At
present, there are two legal initiatives being discussed
in Parliament. The first proposes a new institutional
framework, in order to enhance the capacity of the
governmental agencies to deal with the development
of the forest sector and particularly to promote the
sustainable management of indigenous and planted forests.
With this new institutional framework the forest sector
aims to acquire a higher rank within the Government
structure; the bill proposes the creation of an Under-secretary
of Forest Development and a Forest Service with new
mandates.
The
second legal initiative under discussion is aimed
at promoting the recovery and management of Chile`s
indigenous forests. This Act should be the main mechanism
to promote SFM.
Conclusions
The
application of the Montréal Process concepts
in Chile has not been free of difficulties. Nevertheless,
the progress since the signing of the "Santiago
Declaration" has been significant. Following
dissemination and discussion within the Forest Service
and with other players in Chile`s forest sector, this
process has served as a conceptual framework for developing
initiatives designed to further the sustainable management
of temperate forests in Chile.
The
experience arising from these and other initiatives
consistent with the Montréal Process will serve
to strengthen a harmonious development, which will
contribute to the sustainability of the country.
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VIGNETTE
ON CHINA
Summary
The
status quo of development and implementation
of criteria and indicators for sustainable forest
management in China has been reviewed. China is one
of the 12 member countries of the Montréal
process and has been participating in other international
initiatives. The Chinese Government has taken a series
of significant measures in promoting sustainable forest
management (SFM). The Forestry Action Plan for
China's Agenda 21, the Outline of China's Ecological
Development Programme, and the Action Plan
of Protection of Biodiversity in China have been
worked out, and relevant researches, capacity building
and extension have been carried out.
In
order to effectively implement SFM in China, a research
group to develop the criteria and indicators for such
management has been established. Research in experiment
and demonstration regions has been initiated to test
and further develop the criteria and indicators and
final versions will be formulated which could be operational
and meet the need at the various levels.
The
development of criteria and indicators for SFM is
an important step in implementing the Forestry
Action Plan for China's Agenda 21. The criteria
and indicators will be formulated on the basis of
specific Chinese conditions, and fully standarlized
components will be drawn from relevant criteria and
indicators, designed to be in line with those adopted
internationally, especially in the Montréal
Process. There are many constraints existing in the
formulation of criteria and indicators for SFM, and
arduous tasks will be faced to implement them in China.
Forests
in China
The
largest forests are in the northeast and inner Mongolian
provinces, the 10 southern provinces, and Sichuan
and Yunnan provinces. The Chinese Government attaches
great importance to forestry development. China has
the world's most extensive plantation estate, in excess
of 20 million hectares.
China
is one of the most species-diverse countries in the
world. There are about 32 800 flowering plant species,
of which 9 410 are woody species, comprising 40 per
cent of the world total. The forests and other vegetation
are home to about 499 species of mammals, 1 244 species
of birds, 391 species of reptiles, 280 species of
amphibians and millions of invertebrates. Furthermore,
this country is one of the three major centres of
origin of cultivated plants in the world, with a number
of related wild species. There are approximately 870
nature reserves covering more than 6 per cent of the
country's land area.
In
China, about 58.2 million hectares or 45.3 per cent
of the total forest cover are State owned and administered
by the State Forestry Administration, and 70.3 million
hectares or 54.7 per cent are owned by collectives,
although managed under the authority of forest laws
and monitored by the State Forestry Administration.
However, the growing stock of the collective-owned
forest resources is only 32.2 million cubic metres
or 30 per cent of the total growing stock in China,
compared with 70 per cent from State forest lands.
Forestry activities are labour intensive and the sector
is a large employer of both men and women, with more
than 2.5 million employees.
China
is a developing country with a population of more
than 1.26 billion, which accounts for about 20 per
cent of the world population. The country lacks forest
resources, with only 13.92 per cent forest cover and
3 to 4 per cent of the world's forest area. China's
forests can hardly meet the basic living needs of
its population, environmental conservation and improvement.
The pressure will be more and more intense with successive
increases in an already huge population and an increasing
standard of consumption per capita.
Criteria
and Indicators at the National Level in China
Sustainable
forest management had been developing as an important
issue of common concern when it emerged at the United
Nations Conference on Environment and Development
(UNCED) in 1992. As a follow-up action to UNCED, China's
Agenda 21 - A White Paper on China's Population, Environment
and Development into the 21st Century was drafted
by the Chinese Government as one of the key documents
to guide the country's long-term plan of social and
economic development. Sustainable forest management
gained great attention in terms of realising sustainable
development. Under the guidance of the principle of
sustainable development, the Forestry Action Plan
for China's Agenda 21 was worked out, and priority
project items of the Forestry Action Plan were formulated
by the former Ministry of Forestry. These were highlighted
as major documents presenting the components and the
objectives in the national Ninth Five-Year Plan and
the Plan for the year up to 2010. Recently, in 1999,
China's national program for ecological environment
improvement was worked out by the Chinese Government,
which is for long-term guidance and alignment with
the national economic and social development plan.
An
important aspect of implementing sustainable forest
management in China is to improve environmental services
and supplies of products of the forest ecosystems.
This is being done through the establishment of high
yield plantations, an ecological protection forest
system and restoration of degraded forest ecosystems.
Achieving this will require an increase in forest
resources and a reduced consumption from the natural
forests. Since 1978, large-scale protection forest
programmes have been implemented including the Three-North
(namely Northwest, Central-north, and Northeast) Shelterbelt
System, the Soil and Water Conservation Forests Along
the Upper and Middle Reaches of the Yangtze River,
the Coastal Shelterbelt System, the Taihang Mountain
Afforestation, the Farmland Shelterbelt Network in
Plains Areas, and the National Combat against Desertification.
So far, approximately 21.86 million hectares of protection
forests have been established. Remarkable achievements
have been made in these programmes, but there is a
wide gap remaining to be closed for the completion
and full functioning of the ecological protection
forest system and the realisation of SFM across China.
Therefore, as well as continuously implementing the
above-mentioned forestry programme, the following
new programme was started in early 1998, that is,
the Soil and Water Conservation Programme Along the
Upper Reaches of Yangtze River, the Soil and Water
Conservation Programme Along the Middle and Upper
Reaches of the Yellow River, and the Natural
Forest Conservation Programme in Key Natural Forest
Areas. These programmes are intended to improve the
ecological environment in these regions, better distribute
China's system of ecological forestry programme and
strengthen the capacity for implementing SFM.
The
development of criteria and indicators for sustainable
forest management is an important step in implementing
the UNCED "Forest Principle", Agenda 21
and the Forestry Action Plan for China's Agenda 21,
which is relevant to the protection of biological
diversity, climate change and prevention of desertification.
Criteria and indicators are the basis for constructing
the evaluation system for sustainable forest development,
and the standard and basis for evaluating and judging
forestry economic activities within the range of forestry
development. Formulating the standardized and operational
criteria and indicators for SFM is essential to improve
the application of sustainable forestry development
in China.
Under
the unified leadership of the State Forestry Administration,
formulation of criteria and indicators was put into
effect by Sustainable Forestry Research Centre, Chinese
Academy of Forestry. With involvement of experts from
various fields, a provisional Framework of Criteria
and Indicators for Sustainable Forest Management in
China has been worked out (Table 16), and it is
now under testing and further development. There are
8 criteria and 80 indicators in the set of China's
national-level criteria and indicators, of which 11
indicators are ready to be implemented, 55 require
some Research and Development, 9 require long-term
Research and Development and 5 are uncertain.
Table
16. Framework of National Level Criteria and Indicators
for Sustainable Forest Management in China
|
China's
Framework
|
Montréal
Process
|
|
Ref.
|
Criteria
and Indicators
|
Type*
|
Ref.
|
|
1
|
Conservation
of Biological Diversity
|
|
1
|
|
1.1
|
Ecosystem
diversity
|
|
1.1
|
|
1.1.1
|
Extent
of area by forest types relative to total forest
area |
A
|
1.1.a
|
|
1.1.2
|
Extent
of area by forest type and by age class or successional
stage |
B
|
1.1.b
|
|
1.1.3
|
Area
and per cent of plantation by broad/leaved species
and coniferous species |
B
|
NA
|
|
1.1.4
|
Extent
of area by forest type in protected area categories
as defined by IUCN or other classification systems |
B
|
1.1.c
|
|
1.1.5
|
Extent
of area by forest type in protected area categories
and by age class or successional stage |
D
|
NA
|
|
1.1.6
|
Fragmentation
of forest types |
C
|
1.1.d
|
|
1.2
|
Species
diversity |
|
|
|
1.2.1
|
Number
of forest-dependent species |
B
|
1.2.a
|
|
1.2.2
|
Status
of forest-dependent species at risk of not maintaining
viable breeding populations, as determined by
legislation or scientific assessment |
A
|
1.2.b
|
|
1.3
|
Genetic
diversity |
|
1.3
|
|
1.3.1
|
Number
of forest-dependent species that occupy a small
portion of their former range |
B
|
1.3.a
|
|
1.3.2
|
Population
levels of representative species from diverse
habitats monitored across their range |
C
|
1.3.b
|
|
2
|
Maintenance
of the Productive Capacity of Forest Ecosystems
|
|
2
|
|
2.1
|
Area
of forest land and net area of forest land available
for timber production |
A
|
2.a
|
|
2.2
|
Area
and total growing stock of different forest types |
B
|
NA
|
|
2.3
|
Ratio
of different types of forest land in the total
forest land |
A
|
NA
|
|
2.4
|
Total
growing stock of forests for timber |
B
|
2.b
|
|
2.5
|
Area
and growing stock of plantations |
B
|
2.c
|
|
2.6
|
Distribution
of area and stock of forest for wood production
by age-class |
B
|
NA
|
|
2.7
|
Annual
cutting of forest for timber not to exceed the
annual growth of forests |
A
|
cf.
2.d
|
|
NA
|
Annual
removal of wood products compared with the volume
determined to be sustainable |
N/A
|
2.d
|
|
2.8
|
Annual
removal of non-timber forest products (fur-bearers,
berries, mushrooms, game), compared with the levels
determined to be sustainable |
B
|
2.e
|
|
3
|
Maintenance
of Forest Ecosystem Health and Vitality
|
|
3
|
|
3.1
|
Area
and per cent of forest affected by process or
agents beyond the range of historic variation |
B
|
3.a
|
|
3.2
|
Area
and per cent of air polluted |
A
|
cf.
3.b
|
|
NA
|
Area
and per cent of forest land subject to levels
of specific air pollutants or ultraviolet B that
may cause negative impacts on the forest ecosystem |
N/A
|
3.b
|
|
3.3
|
Area
and per cent of forest land with diminished biological
components indicative of changes in fundamental
ecological process and/or ecological continuity |
B
|
3.c
|
|
4
|
Conservation
and Maintenance of Soil and Water Resources
|
|
4
|
|
4.1
|
Area
and per cent of forest land with significant soil
erosion |
B
|
4.a
|
|
4.2
|
Area
and per cent of cultivated land on slopes of more
than 25 degrees which has been turned back into
forest land |
B
|
NA
|
|
4.3
|
Area
and per cent of forest land for soil and water
conservation in those important regions |
B
|
cf.
4.b
|
|
NA
|
Area
and per cent of forest land managed primarily
for protective functions |
N/A
|
4.b
|
|
4.4
|
Per
cent of stream kilometers in forested catchment
in which stream flow and timing have significantly
deviated from the historic range of variation |
C
|
4.c
|
|
4.5
|
Range
of changes in physical and chemical properties
of streams in forested catchments |
C
|
cf.
4.f
&
4.g
|
|
NA
|
Per
cent of water bodies in forest areas with significant
variance of biological diversity from historic
range of variability |
N/A
|
4.f
|
|
NA
|
Per
cent of water bodies in forest areas with significant
variance from historic range of variability in
pH, dissolved oxygen, levels of chemical, sedimentation
or temperate change |
N/A
|
4.g
|
|
4.6
|
Controlled
area and control per centage of areas with soil
and water losses, intensity of which is very light |
B
|
NA
|
|
4.7
|
Controlled
area and control per centage of areas with soil
and water losses, intensity of which is light |
B
|
NA
|
|
4.8
|
Area
and per cent of cultivated land on slopes on which
maintenance and conservation of soil and water
resources have been taken into account according
to regulations of the government |
B
|
NA
|
|
4.9
|
Area
and per cent of forest of human origin which has
serious degradation of site index |
C
|
cf.
4.d
&
4.e
|
|
NA
|
Area
and per cent of forest land with significantly
diminished soil organic matter or changes in other
soil chemical properties, or both |
N/A
|
4.d
|
|
NA
|
Area
and per cent of forest land with significant compaction
or changes in soil physical properties resulting
from human activities |
N/A
|
4.e
|
|
4.10
|
Area
and per cent of broad-leaved forest in forests
of human origin |
A
|
NA
|
|
4.11
|
Area
and per cent of individual tree species |
A
|
NA
|
|
4.12
|
Area
and per cent of replanted forests of human origin |
D
|
NA
|
|
4.13
|
Area
and per cent of land on slopes on which maintenance
and conservation of soil and water resources have
been taken into account in silviculture according
to regulations of the government |
B
|
NA
|
|
4.14
|
Intensity,
area and per cent of protection of forest ground
vegetation |
B
|
NA
|
|
NA
|
Area
and per cent of forest land experiencing an accumulation
of persistent toxic substances |
N/A
|
4.h
|
|
5
|
Conservation
of Forest Contribution to Global Carbon Cycles
|
|
5
|
|
5.1
|
Area
of forests |
A
|
NA
|
|
5.2
|
Total
forest ecosystem biomass and carbon pool, and
if appropriate, by forest types, age class, and
successional stages |
B
|
5.a
|
|
5.3
|
Area
and consumption of forests for energy resources
and their contribution |
C
|
NA
|
|
5.4
|
Production
and consumption of forest products and their contribution |
C
|
5.c
|
|
5.5
|
Area
of cutting and its contribution |
B
|
NA
|
|
5.6
|
Absorption
of carbon by forest |
D
|
cf.
5.b
|
|
5.7
|
Carbon
emission by soil |
D
|
cf.
5.b
|
|
NA
|
Contribution
of forest ecosystems to the total global carbon
budget, including absorption and release of carbon |
N/A
|
5.b
|
|
5.8
|
Release
of CO2 and CH4 by peat |
D
|
NA
|
|
6
|
Maintenance
and Strengthening of Long-term Multiple Benefits
of Forests
|
|
6
|
|
6.1
|
Growing
and consumption, including employment |
N/A
|
6.1+6.5
|
|
6.1.1
|
Population
rate and economic rate |
A
|
NA
|
|
6.1.2
|
Supply
and consumption of wood and wood products, including
consumption per capita |
B
|
6.1.c
|
|
6.1.3
|
Upper
limitation for annual removal of wood, and the
area and location of forests available for timber
production and their changes by year |
B
|
NA
|
|
6.1.4
|
Supply
and demand of wood and non-wood products, including
their export and import |
C
|
NA
|
|
NA
|
Supply
and consumption or use of non-wood products |
N/A
|
6.1.f
|
|
6.1.5
|
Value
and volume of wood and wood or non-wood products
production, including value added through downstream
processing, and value of wood and non-wood products
production as per centage of GDP |
B
|
6.1.a+
6.1.b+
6.1.d
|
|
NA
|
Degree
of recycling of forest products |
N/A
|
6.1.e
|
|
6.1.6
|
Direct
and indirect employment in the forest sector and
forest sector employment as a proportion of total
employment |
B
|
6.5.a
|
|
6.1.7
|
Production
efficiency rate, average wage rates and injury
rates in major employment categories within the
forest sector |
B
|
cf.6.5.b
|
|
NA
|
Average
wage rates and injury rates in major employment
categories within the forest sector |
N/A
|
6.5.b
|
|
NA
|
Viability
and adaptability to changing economic conditions,
of forest-dependent communities, including indigenous
communities |
N/A
|
6.5.c
|
|
NA
|
Area
and per cent of forest land used for subsistence
purposes |
N/A
|
6.5.d
|
|
6.2
|
Investment
in forestry |
N/A
|
6.3
|
|
6.2.1
|
Value
of investment, including investment in forest
growing, forest health and management, planted
forests, wood processing, recreation and tourism |
B
|
6.3.a
|
|
6.2.2
|
Level
of expenditure on research and development, education,
and extension and use of new and improved technologies |
B
|
6.3.b+
6.3.c
|
|
6.2.3
|
Rates
of return on investment |
B
|
6.3.d
|
|
6.3
|
Forest
recreation and tourism, demands and assessment
of culture, social and spiritual |
N/A
|
6.2+
6.4
|
|
6.3.1
|
Value,
area and per cent of forest land managed for general
recreation and tourism, in relation to the total
area of forest land. Number and type of facilities
available for general recreation and tourism,
and number of visitor days attributed to recreation
and tourism, in relation to population and forest
area |
B
|
6.2.a+
6.2.b+
6.2.c
|
|
6.3.2
|
Area
and per cent of forest land managed in relation
to the total area of forest land to protect the
range of culture, social and spiritual needs and
values |
B
|
6.4.a
|
|
NA
|
Non-consumptive
use forest value |
N/A
|
6.4.b
|
|
7
|
Legal
and Policy Protection Systems
|
|
7.1-7.3
|
|
7.1
|
Legislation |
N/A
|
7.1
|
|
7.1.1
|
Forest
resource ownership |
B
|
7.1.a
|
|
7.1.2
|
Institution
for management of forest resources |
B
|
7.1.b+7.1.e.
7.2.b
|
|
NA
|
Forest
management to conserve special environmental,
cultural, social or scientific values, or a combination |
N/A
|
7.1.e
|
|
7.1.3
|
Encouraging
best practice codes for forest management |
B
|
7.1.d
|
|
7.1.4
|
Adopting
institution of document management in managing
forest resources |
B
|
NA
|
|
7.1.5
|
Strengthening
administrative regulations in forest management |
B
|
cf.
7.1.b
|
|
NA
|
Providing
opportunities for public participation in public
policy and decision-making related to forest and
public access to information |
N/A
|
7.1.c
|
|
7.2
|
Policy |
N/A
|
7.2
|
|
7.2.1
|
Public
participation in forestry |
B
|
7.2.a+
7.1.c
|
|
NA
|
Undertaking
and implementing periodic forest-related planning,
assessment, and policy review including cross-sectoral
planning and coordination |
N/A
|
7.2.b
|
|
7.2.2
|
Developing
and maintaining human resource skills |
B
|
7.2.c
|
|
7.2.3
|
Adjusting
the structure of forestry industry |
B
|
NA
|
|
7.2.4
|
Developing
and maintaining efficient physical infrastructure |
B
|
7.2.d
|
|
NA
|
Enforcing
laws, regulations and guidelines |
N/A
|
7.2.e
|
|
7.3
|
Economic
framework |
N/A
|
7.3
|
|
NA
|
Investment
and taxation policies and a regulatory environment
in order to meet long-term demands for forest
products and services |
N/A
|
7.3.a
|
|
7.3.1
|
Favorable
policy on forestry investment and taxation |
B
|
cf.
7.3.a
|
|
7.3.2
|
Adopting
policy collecting silviculture expenditure |
B
|
cf.
7.3.a
|
|
7.3.3
|
Establishing
forest ecological compensation system |
C
|
cf.
7.3.a
|
|
7.3.4
|
Strengthening
institution of forest funds |
B
|
cf.
7.3.a
|
|
7.3.5
|
Expanding
fund channel for forestry construction |
B
|
cf.
7.3.a
|
|
7.3.6
|
Absorbing
and exploitation of overseas funds to speed up
major project construction in forestry |
B
|
cf.
7.3.a
|
|
7.3.7
|
Speeding
up construction of institute for modern forestry
enterprise |
B
|
cf.
7.3.a
|
|
7.3.8
|
Establishing
fair trading on forest products gradually |
B
|
7.3.b
|
|
8
|
Information
and Technological Support Systems
|
|
7.4-7.5
|
|
8.1
|
Measurement
and monitoring |
N/A
|
7.4
|
|
8.1.1
|
Availability
and extent of up-to-date data, statistics and
other information important to measuring or describing
indicators associated with criteria 1 to 7 |
A
|
7.4.a
|
|
8.1.2
|
Scope,
frequency and statistical reliability of forest
inventories, assessments, monitoring and other
relevant information |
B
|
7.4.b
|
|
8.1.3
|
Compatibility
with other countries in measuring, monitoring
and reporting on indicators |
B
|
7.4.c
|
|
8.2
|
Research
and development |
N/A
|
7.5
|
|
8.2.1
|
Development
of scientific understanding of forest ecosystem
characteristics and function |
B
|
7.5.a
|
|
8.2.2
|
Development
of methodologies to measure and integrate environmental
and social costs and benefits into markets and
public policies, and to reflect forest-related
resource depletion or replenishment in national
accounting systems |
B
|
7.5.b
|
|
8.2.3
|
Evaluation
of the contribution of science and technology |
B
|
cf.7.5.c
|
|
8.2.4
|
Enhancement
of ability to predict impacts of human intervention
on forests |
B
|
7.5.d
|
|
8.2.5
|
Ability
to predict impacts on forests of possible climate
change |
B
|
7.5.e
|
*Indicator
type: A-implementation now; B-requiring some R&D;
C-requiring long-term R&D; D-uncertain
Criteria
and Indicators at the Sub-national Level in China
China
has developed its criteria and indicators at two sub-national
levels, the regional level and the forest management
unit (FMU) level. As China is a country with vast
territory and a rich diversity of forest types, the
sub-national criteria and indicators should be more
specific to the local situations, with appropriate
deletion or addition of indicators within the national
framework. Indicators that are not measurable at sub-national
levels should be not considered, although they are
important at the national level. Furthermore, to make
an effective evaluation at the national level, it
is necessary to weight each indicator at the sub-national
level according to the local objectives of forest
management.
Since
1997, the identification and testing of regional criteria
and indicators have been conducted in three representative
forest zones. The Yichun in Heilongjiang Province,
Fenyi in Jiangxi Province and Zhangye in Gansu Province
are representatives of the Northeast State Owned Forest
Zone, South Collective Owned Forest Zone, and Northwest
Dry Land Forest Zone, respectively. The development
and testing of criteria and indicators in these three
sites were funded by the UNDP, called CPR/96/109 Project
Capacity Building, Research and Extension for Sustainable
Forest Management. A number of experts, both national
and international, have been involved in this project.
The
draft sets of regional criteria and indicators, each
with eight criteria similar to the national level,
have been developed for the three representative forest
zones in China (Table 17). In total, the 60 indicators
for Fenyi in the Southeast of China are mainly related
to forest ownership, plantations, and cash tree plantations.
The 68 indicators for Zhangye in the Northwest concentrate
environmental and social issues (water resource conservation
forest, shelterbelt, and cash tree plantations). The
77 indicators defined for Yichun in the Northeast
focus mainly on the maintenance of forest productivity.
Table
17. Indicators at the regional (sub-national) level
in three typical forest zones of China
| |
|
Sub-national
level
|
| |
National
Level |
Fenyi,
Jiangxi |
Zhangye,
Gansu |
Yichun,
Heilogjiang |
|
C1,
Biodiversity
|
10
|
11
|
13
|
9
|
|
C2,
Productivity
|
8
|
9
|
8
|
12
|
|
C3,
Health and vitality
|
3
|
3
|
8
|
3
|
|
C4,
Soil and water
|
14
|
11
|
8
|
8
|
|
C5,
Carbon cycles
|
8
|
3
|
4
|
5
|
|
C6,
Multiple benefits
|
12
|
9
|
10
|
14
|
|
C7,
Legal and policy
|
17
|
10
|
10
|
18
|
|
C8,
Information and technology
|
8
|
4
|
7
|
8
|
|
TOTAL
|
80
|
60
|
68
|
77
|
Also,
the criteria and indicators have been developed and
tested at the forest management unit level in the
three representative sites, including selection of
the indicators, a feasibility study for data collection
and the process for reporting of criteria and indicators.
Most of the indicators at this level are developed
from criteria 1 to 4 (Table 18).
Table
18. Criteria and number of possible indicators at the
forest management unit level in three representative
forest zones of China
|
Criterion
|
C1
|
C2
|
C3
|
C4
|
C5
|
C6
|
C7
|
C8
|
TOTAL
|
|
Dagangshan,
Fenyi, Jiangxi
|
10
|
5
|
4
|
8
|
3
|
8
|
9
|
0
|
47
|
|
Xishui,
Zhangye, Gansu
|
8
|
3
|
2
|
5
|
3
|
4
|
3
|
0
|
28
|
|
Fenlin,
Yichun, Heilongjiang
|
8
|
10
|
1
|
4
|
1
|
7
|
7
|
0
|
38
|
Experiment
and Demonstration Network for Sustainable Forestry Development
in China
China's
experiment and demonstration areas
In
order to examine the approach to sustainable forestry
development and to implement a plan based on the Forestry
Action Plan for China's Agenda 21, the Chinese Government
initiated the establishment of an experiment and demonstration
area on sustainable forestry development. One of main
objectives is to give support to China's practice
and international discussion on SFM. Since 1997, eight
experiment and demonstration areas on sustainable
forestry development have been selected across the
ecozones of China (Table 19).
Table
19. Demonstration forest network for sustainable forest
management in China
|
Forest
zone
|
Location |
Years |
Issues
focused
|
| Northeast
State |
Yichun,
Heilongjiang
|
1997-
|
Protection
of Natural Forest |
| Forestry
Zone |
Muling,
Heilongjiang
|
1997-
|
Development
of large State forest bureaux |
| Three-North |
Zhangye,
Gansu
|
1997-
|
Management
of water conservation forest |
| Dryland
Forestry Zone |
Pingshan,
Hebei
|
1997-
|
Sustainable
mountainous area development |
| Collective
Forestry Zone |
Fenyi,
Jiangxi
|
1997-
|
Collective-owned
forest management |
| Collective
Forestry Zone |
Tonggu,
Jiangxi
|
1997-
|
Plantation
management |
| Collective
Forestry Zone |
Lin'an,
Zhejiang
|
1998-
|
Sustainable
mountainous area development |
| Collective
Forestry Zone |
Zhanjiang,
Guangdong
|
1997-
|
Forestry
and forest Industry |
Join
in activities of the International Model Forest Network
In
1996, China`s Forestry Department agreed to join in
the activities of the International Model Forest Network
at the invitation of Department of Natural Resources
of Canada. The construction of China`s Model Forest
Network was documented in a memorandum on forestry
co-operation between China and Canada.
China's
Model Forest Network has been established on the basis
of areas for National experiment and demonstration
on sustainable forestry development. Linan County
in Zhejiang Province was selected as the first model
forest in China. An international workshop on China's
model forests jointly supported by IMFNS, the Canadian
Forest Service and the Chinese Academy of Forestry,
was held in Linan from 29 March to 2 April 1999. The
workshop dealt with how to implement the Chinese Model
Forest Network, especially in the Linan Model Forest.
Some pioneer activities such as potential partnership
identification, farmers' training, and eco-tourism
planning and implementation have been conducted.
China's
Model Forest Network is participating in a series
of four regional workshops, held in Tokyo, Mie Prefecture
and Gunma Prefecture, on Model Forests for Field-level
Application of Sustainable Forest Management. In this
project, supported by Japan, Chinese experiences on
SFM at the operational level and on model forest building
were introduced at the workshop.
China
is one of the member countries of the Japan/FAO trust
funding project known as The Regional Project on Assistance
for the Implementation of the Model Forest Approach
for Sustainable Forest Management in the Asia-Pacific
Region. The project, which has been conducted since
January 2000 with China and three other countries
(Thailand, Myanmar and Philippines) as members, will
promote the model forest establishment in the Asia
- Pacific region.
Major
Constraints for Implementing Sustainable Forest Management
in China
China
also faces many constraints for implementing criteria
and indicators. Generally speaking, the main constraints
are a shortage of forest resources, serious ecological
and environmental degradation, high pressure from
|