Zimmermann Case study: The Kyrgryz forestry concept: policy changes for a multipurpose management of mountain forests in I.. Foreword: Linking mountain forests conservation with sustaina
Trang 2IUFRO Research Series
IUFRO Research Series
The International Union of Forestry Research Organizations (IUFRO), with its14,000 scientists from 700 member institutions in 100 countries, is organizedinto nearly 300 research units that annually hold approximately 60 confer-ences, workshops and other meetings The individual papers, proceedingsand other material arising from these units and meetings are often publishedbut in a wide array of different journals and other publications The object ofthe IUFRO Research Series is to offer a single, uniform outlet for high qualitypublications arising from major IUFRO meetings and other products ofIUFRO’s research units
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Trang 3language, allowing papers occasionally to be in other languages Guidelinesfor submitting and publishing material in this series are available from thePublisher, Books and Reference Works, CABI Publishing, CAB International,Wallingford, Oxon OX10 8DE, UK, and the IUFRO Secretariat, c/o FederalForest Research Centre, Seckendorff-Gudent-Weg 8, A-1131, Vienna, Austria.IUFRO Executive Board:
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R Guevara Moncada, Turrialba, Costa Rica
J Hong, Beijing, China
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India
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Titles Available:
1 Forest Dynamics in Heavily Polluted Regions
Edited by J.L Innes and J Oleksyn
2 Forest History: International Studies on Socioeconomic and Forest Ecosystem Change
Edited by M Agnoletti and S Anderson
3 Methods and Approaches in Forest History
Edited by M Agnoletti and S Anderson
4 Air Pollution and the Forests of Developing and Rapidly Industrializing Countries
Edited by J.L Innes and A.H Haron
5 Forests in Sustainable Mountain Development: a State of Knowledge Report for 2000
Edited by M.F Price and N Butt
Trang 4Forests in Sustainable Mountain
Development: a State of Knowledge Report for 2000
Task Force on Forests in Sustainable Mountain Development
SWISS AGENCY FOR DEVELOPMENT AND COOPERATION
SDC
THE ROYAL MINISTRY OF FOREIGN AFFAIRS
Trang 5CABI Publishing is a division of CAB International
USA Tel: +1 212 481 7018 Fax: +1 212 686 7993 Email: cabi-nao@cabi.org
© CAB International 2000 All rights reserved No part of this publication may
be reproduced in any form or by any means, electronically, mechanically, by photocopying, recording or otherwise, without the prior permission of the
copyright owners.
A catalogue record for this book is available from the British Library, London, UK.
Library of Congress Cataloging-in-Publication Data
Forests in sustainable mountain development : a state of knowledge report for 2000 / edited by M.F Price and N Butt.
p cm (IUFRO research series ; no 5) Includes bibliographical references (p ).
Typeset by AMA DataSet Ltd, UK
Printed and bound in the UK by Biddles Ltd, Guildford and King’s Lynn
Trang 6Contents
Foreword: Linking mountain forests conservation with sustainable
1 Mountain Forests: Location, Characteristics and Trends 1
V Kapos, J Rhind, M Edwards, M.F Price and C Ravilious
V Kremsa and S Varela
Case study: Mapping and monitoring biodiversity and
M Castro and M Kappelle
Case study: Monitoring of degraded mountain forests in
T Zawila-Niedzwiecki, M Iracka and E Wisniewska
Trang 71.2 Expansion of European mountain forests 19
P Piussi
Case study: Woodland expansion in the Welsh mountains 25
J.E.G Good, J.W Humphrey, D Clough and T.H Thomas
G Grabherr
Case study: Mountain forests, biodiversity and people
M Kappelle and M.E Juárez
N Ndam, J.R Healey, J Acworth and P.G Tchouto
D.L Peterson, S.J Prichard and D McKenzie
1.5 Restoration of Andean forests for conservation
F.O Sarmiento
M Beniston
1.7 Forest decline, air pollution and other anthropogenic
J.L Innes
H Kreutzmann and C Stadel
2.2 Impacts of population increase and economic change
S.J Scherr and S.R Templeton
Case study: Forests of the Usambara Mountains: historical
A.R.S Kaoneka, Y.M Ngaga and G.C Monela
Trang 82.3 Mountain women and their forests 103
Atul and Punam
J.D Gurung
P.S Ramakrishnan
Case study: Environmental perception and the sacred in the
V Castro
Case study: Sacred forests in the Sierra Nevada de Santa
G.E Rodríguez Navarro
3 Interdependencies between Mountain and Lowland
El Hadji M Sène
Case study: Creating common interests around Huascaran
Case study: Ecosystem services of forest gardens in Sri Lanka 153
F.L Sinclair and G Hitinayake
3.3 Sustainably balancing downstream and upstream benefits in
P.C Zingari
Case study: Urban sprawl and peri-urban mountain forests inGreece: conflict and co-existence in a quest for survival 161
P.C Xanthopoulos
Trang 94 Perceiving and Assuring the Multiple Functions of
A Zanzi Sulli
4.2 The importance of empirical research on public perceptions
and attitudes towards forests for participatory policy
W Zimmermann and F Schmithüsen
4.3 Traditional knowledge, Western science and environmental
A.J Thomson, M.N Jimmie, N.J Turner and D Mitchell
4.4 Approaches to multifunctionality in mountain forests 187
G Buttoud
Case study: Multifunctional use and sustainable management
G.K Solntsev and M.V Pridnya
4.5 Silvicultural problems in subalpine forests in the Alps 197
W Schönenberger
Case study: Multifunctionality in the Fiemme Valley,
S Cattoi, C Pollini and V Tosi
Case study: ‘Close-to-nature’ silviculture in the Italian Alps:
Trang 10Case study: Quantitative analysis of fragmented landscapepatterns resulting from timber harvesting practices in the
M Shiba
Case study: Designing sustainable mountain landscapes in
A.J Thomson and S.A Akenhead
Case study: Participatory photo-mapping in Nepal 218
R.A Mather
5 Multiple Functions from Mountain Forests I Mountain
H.R Heinimann
Case study: Renaturalization of coppices in the National Park
R Spinelli, R Spinelli and G Fabbri
Case study: Labour costs in the forests of the Alps and
Case study: Planting stock quality and establishment in the
N.J Ledgard and G.C Baker
Trang 11Case study: Choosing which trees to plant in the Ecuadorian
R.G.M Hofstede, W Jongsma, R Coppus, J.P Groenendijk and J Fehse
6 Multiple Functions from Mountain Forests II Agroforestry
6.1 Agroforestry in sustainable mountain development 270
K Atta-Krah and Tang Ya
Case study: Chagga agroforests on Mount Kilimanjaro,
E.C.M Fernandes
6.2 Improved agroforestry systems for steeplands in the
M.A McDonald, J.R Healey, P.A Stevens and P.V.D Prasad
Case study: Evaluation of trees indigenous to the montaneforest of the Blue Mountains of Jamaica for reforestation and
M.A McDonald and J.R Healey
Case study: Sustainable management of the Himalayan
R.M Singhal, V Kumar and P Kumar
J.E.M Arnold and M Ruiz Pérez
N Ndam and B Ewusi
Case study: Edible herbs and wildflowers in mountain areas of
D.K Lee and G.T Kim
Case study: Production of mountain mushrooms in Korea 310
Y.-C Youn
6.4 The potential of medicinal and aromatic plants for sustainable
T.B Shrestha and S Pokharel
Trang 12Case study: The potential of bamboo resources in mountainous
M Ruiz Pérez, F Maoyi, B Belcher and Y Xiaosheng
7 Multiple Functions from Mountain Forests III Diverse
S.F McCool and P.R Lachapelle
7.2 Recreation and landscape management impacts in
H Liniger and R Weingartner
7.8 Research, planning and implementation of watershed
H Schreier
Case study: The World Overview of Conservation Approaches
H Liniger
M Aldrich
Trang 138 Legislation, Policies and Economic Instruments 399
8.1 The role of forest and environmental legislation in sustainable
F Schmithüsen and W Zimmermann
Case study: The Kyrgryz forestry concept: policy changes for
a multipurpose management of mountain forests in
I Yunusova, A Chingojoiev and G Buttoud
Case study: Mountain forest policies in Austria 413
G Weiss
8.2 European mountain forest policies – a comparative analysis 415
A Ottitsch and G Weiss
R Beck and M Suda
Case study: Payments for watershed services in Costa Rica 428
J.C Calvo
K Thornber
9.1 Evaluation of organizational performance in mountain
Trang 149.4 Forests as common property in the Swiss Alps 459
I Kissling-Näf
9.5 Privatization of mountain forest land in countries in
D Pettenella
P Branney and M Hobley
10.2 Participatory monitoring and evaluation for collaborative
P Warren
Case study: Assessment of the wide range of forest productsthrough a simple participatory forest inventory 494
R aus der Beek
Trang 15Contributors
I.V Abrudan, Faculty of Silviculture and Forest Engineering, 1 Sorul
Beethoven, Brasov-2200, Romania
J Acworth, The Mount Cameroon Project, Limbe Botanic Garden, PO Box
437, Limbe, South West Province, Cameroon
S.A Akenhead, Facet Division Systems, Vancouver, British Columbia, Canada
M Aldrich, Forests for Life Programme, WWF International, Avenue du
Mont Blanc, 1196 Gland, Switzerland
J.E.M Arnold, 19 Hayward Road, Oxford OX2 8LN, UK
K Atta-Krah, Eastern and Central Africa Regional Programme, ICRAF, PO
Box 30677, Nairobi, Kenya
Atul, Department of Agroforestry and Environment, COA, Himachal Pradesh
Agricultural University, Palampur 176062, India
R aus der Beek, Ekantakuna, Jawalakhel, PO Box 113, Kathmandu, Nepal G.C Baker, Forest Research, Forestry Road, University of Canterbury, Ilam,
Christchurch, New Zealand
R Beck, Technical University of Munich, Am Hochanger 13, 85354
P Branney, 5 Little Road, Edinburgh EH16 6SH, UK
S.R Brechin, School of Natural Resources and Environment, The University
of Michigan, 430 E University Avenue, Ann Arbor, MI 48109, USA
Trang 16G Buttoud, Unité Économie et Politique Agricole et Forestiére, Institut
National de la Recherche Agronomique, 14 Rue Giradet, CS4216-54042, Nancy Cedex, France
J Calvo, Centro Cientifico Tropical, Apartado 8-3870, 1000, San José, Costa
Rica
J Campos, Jose Jaquin Campos, Natural Forest Management Unit, CATIE
7170, Turrialba, Costa Rica
M Castro, Proyecto ECOMAPAS, Institution Nacional de Biodiversidad
(INBio), PO Box 22-3100, Santo Domingo de Heredia, Costa Rica
V Castro, Departmento de Antropología, Facultad de Ceincias Sociales,
Universidad de Chile, Ignacio Carrera Pinto 1045, Nuñoa, Santiago,Chile
S Cattoi, Forest and Range Management Research Institute, 38050
Villazzano, Trento, Italy
A Chingojoiev, First-Deputy Director, State Forest Agency of the
Government of the Kyrgyz Republic, 276 Abdymomunov Street,Bishkek 720033, Kyrgyz Republic
D Clough, Chris Blandford Associates, Archway House, Station Road,
Chester CH1 3DW, UK
R Coppus, Department of Physical Geography and Soil Science, University
of Amsterdam, Nieuwe Prinsengracht 130, 1018 VZ Amsterdam, TheNetherlands
O Dubois, IIED, 3 Endsleigh Streeet, London WC1H 0DD, UK
M Edwards, WCMC, 219 Huntingdon Road, Cambridge CB3 0DL, UK
B Ewusi, The Mount Cameroon Project, Limbe Botanic Garden, PO Box 437,
Limbe, South West Province, Cameroon
G Fabbri, CNR-IRL, via Barazzuoli 23, I-50136 Firenze, Italy
L Fé d’Ostiani, FAO/TCOC, Viale delle Terme di Caracalla, 00100 Rome,
Italy
J Fehse, Department of Physical Geography and Soil Science, University of
Amsterdam, Nieuwe Prinsengracht 130, 1018 VZ Amsterdam, TheNetherlands
E.C.M Fernandes, Department of Crop and Soil Science, Cornell University,
624 Bradfield Hall, Ithaca, NY 14853, USA
J.E.G Good, Institute of Terrestrial Ecology, Bangor Research Unit,
University College of North Wales, Deiniol Road, Bangor, GwyneddLL57 2UP, UK
G Grabherr, Department of Vegetation Ecology and Conservation Biology,
University of Vienna, Althanstraße 14, A-1090 Vienna, Austria
H.M Gregerson, Department of Forest Resources, University of Minnesota,
St Paul, MN 55108, USA
J.P Groenendijk, Department of Physical Geography and Soil Science,
University of Amsterdam, Nieuwe Prinsengracht 130, 1018 VZAmsterdam, The Netherlands
Trang 17M.R Guariguata, Jose Jaquin Compos, Natural Forest Management Unit,
CATIE 7170, Turrialba, Costa Rica
J.D Gurung, International Center for Integrated Mountain Development
(ICIMOD), 4/80 Jawalakhel, PO Box 3226, Kathmandu, Nepal
J.R Healey, Agricultural and Forest Sciences, University of Wales, Bangor,
Gwynedd LL57 2DG, UK
H.R Heinimann, Swiss Federal Institute of Technology, Forest Engineering
Section, ETH-Zurich, CH-8092, Switzerland
G Hippoliti, Istitudo di Assestamento e Tecnologia Forestale, Via San
Bonaventura 13, 50145 Firenze, Italy
G Hitinayake, Department of Crop Science, University of Peradeniya,
Peradeniya, Sri Lanka
M Hobley, Glebe House, Thorncombe, Chard, Somerset TA20 4PP, UK
T Hofer, FAO, Forest Resources Division, Forestry Department, Viale delle
Terme di Caracalla, 00100 Rome, Italy
R.G.M Hofstede, University of Amsterdam, Proyecto Paramo, Isla
Fernandina, N93-41 y T de Berlanga, Quito, Ecuador
C Howard, Forest House, Tropical Research Consultancy, Barbadoes Hill,
Tintern, Monmouthshire NP16 6SU, UK
J.W Humphrey, Forest Research, Northern Research Station, Roslin,
Midlothian EH25 9SY, UK
J.L Innes, Forest Resources Management, University of British Columbia,
Forest Sciences Centre, 2424 Main Hall, Vancouver, British Columbia,V6T 1Z4, Canada
M Iracka, Institute of Geodesy and Cartography, Department of
Cartography, 2/4 Jasna St, 00-950 Warsaw, Poland
M.N Jimmie, Nicola Tribal Association, 2090 Coutlee Avenue, PO Box 188,
Merritt, BC, V1K 1B8, Canada
J.E Johnson, College of Forestry and Wildlife Resources, 324 Cheatham
Hall, Virginia, Tech, Blacksburg, VA 24061-0324, USA
W Jongsma, Department of Physical Geography and Soil Science, University
of Amsterdam, Nieuwe Prinsengracht 130, 1018 VZ Amsterdam, TheNetherlands
A.L Joshi, NARMSAP, PO Box 8713, Babar Mahal, Kathmandu, Nepal M.E Juárez, Proyecto ECOMAPAS, Institution Nacional de Biodiversidad
(INBio), PO Box 22-3100, Santo Domingo de Heredia, Costa Rica
A.R.S Kaoneka, Sokoine University of Agriculture, PO Box 3010,
Morogoro, Tanzania
V Kapos, WCMC, 219 Huntingdon Road, Cambridge CB3 0DL, UK
M Kappelle, Proyecto ECOMAPAS, Institution Nacional de Biodiversidad
(INBio), PO Box 22-3100, Santo Domingo de Heredia, Costa Rica
G.T Kim, Department of Forest Resources, College of Agriculture and Life
Sciences, Seoul National University, Suwon 441-744, Republic ofKorea
Trang 18I Kissling-Näf, Swiss Federal Institute of Technology (ETH), 8092 Zurich,
N Ledgard, Forest Research, Forestry Road, University of Canterbury, Ilam,
Christchurch, New Zealand
D.K Lee, Department of Forest Resources, College of Agricultural and Life
Sciences, Seoul National University, Suwon, 441-744, Republic ofKorea
H Liniger, Centre for Development and Environment (CDE), Institute of
Geography, University of Bern, Hallerstraße 12, 3012 Bern,Switzerland
F Maoyi, Research Institute of Subtropical Forestry (RISF), Chinese Academy
of Forestry, Fuyang, 311400 Zhejiang, People’s Republic of China
R.A Mather, Forest Products Research Centre, Buckinghamshire Chilterns
University College, Queen Alexandra Road, High Wycombe,Buckinghamshire HP11 2JZ, UK
S.F McCool, School of Forestry, The University of Montana, Missoula, MT
R Motta, Department Agroselviter, University of Turin, 44 Via Leonardo Da
Vinci, 10095 Grugliasco (TO), Italy
N Ndam, The Mount Cameroon Project, Limbe Botanic Garden, PO Box 437,
Limbe, South West Province, Cameroon
S.K Nepal, Centre for Development and Environment, Institute of
Geography, University of Bern, Hallerstrasse 12, 3012 Bern,Switzerland
Trang 19Y.M Ngaga, Sokoine University of Agriculture, PO Box 3010, Morogoro,
Tanzania
H Omura, Department of Forestry, Faculty of Agriculture, Kyushu
University, Fukuoka, 812 8581, Japan
A Ottitsch, Policy Analysis, European Forest Institute, Torikatu 34,
Fin-8010, Joensuu, Finland
S Pandey, International Centre for Integrated Mountain Development
(ICIMOD), 4/80 Jawalakhel, PO Box 3226, Kathmandu, Nepal
D.L Peterson, College of Forest Resources, University of Washington, Box
352100, Seattle, WA 98195-2100, USA
D Pettenella, Dipart Territoriae Sistemi Agro-Forestal, Università di
Padova, Agripolis, I-35020 Legnaro PD, Italy
P Piussi, Istituto di Selvicoltura, Via S Bonaventura, 13, 50145 Firenza,
Italy
S Pokharel, IUCN Nepal, PO Box 3923, Kathmandu, Nepal
C Pollini, Forest and Range Management Research Institute, 28050
Villazzano, Trento, Italy
P.V.D Prasad, Department of Life Sciences, University of the West Indies,
Mona, Kingston 7, Jamaica
J.D Pratt, Mountain Institute, Main and Dogwood Streets, PO Box 907,
Franklin, WV 26807, USA
M.F Price, Director, Centre for Mountain Studies, Perth College, University
of the Highlands and Islands, Crieff Road, Perth PH1 2NX, UK
S.J Prichard, College of Forest Resources, University of Washington, Seattle,
WA 98195, USA
M.V Pridnya, Research Institute of Mountain Forestry and Forest Ecology,
Russian Federal Forest Service, 74 Str Kurotnyi Prospekt, KrasnodarRegion (Kray), Sochi 354002, Russia
U Pröbstl, Freie Landshaftsarchitekin, BDLA, St Andra-Strasse 8, 82398,
Etting-Polling, Germany
Punam, Department of Agroforestry and Environment, COA, Himachal
Pradesh Agricultural University, Palampur, 176062, India
P.S Ramakrishnan, School of Environmental Sciences, Jawaharlal Nehru
University, New Delhi, 110067, India
C Ravilious, WCMC, 219 Huntingdon Road, Cambridge CB3 0DL, UK
F Reimoser, Research Institute of Wildlife Ecology, Vienna Veterinary
University, Savoyenstrasse 1, A-1160 Vienna, Austria
J Rhind, Ministry of Agriculture, Fisheries and Food, Room G33, Nobel
House, 17 Smith Square, London SW1P 3JR, UK
K Rijal, International Centre for Integrated Mountain Development
(ICIMOD), PO Box 3226, Jawalakhel, Kathmandu, Nepal
G.E Rodríguez Navarro, Fundación Pro-Sierra Nevada de Santa Marta,
Calle 17, No 3-83, Santa Marta, Magdalena, Colombia
Trang 20M Ruiz Pérez, Departmento de Ecologia, Facultad de Ceincias-Edificio
Biológicas, Universidad Autónoma de Madrid, 28049 Madrid, Spain
F.O Sarmiento, Center for Latin American and Caribbean Studies, The
University of Georgia, Room G40, Baldwin Hall, Athens, GA30602-1619, USA
S.J Scherr, Agricultural and Resources Department, 2200 Symons Hall,
University of Maryland, College Park, MD 20742, USA
F Schmithüsen, Swiss Federal Institute of Technology (ETHZ), CH 8092,
Zurich, Switzerland
W Schönenberger, Swiss Federal Institute for Forest, Snow and Landscape
Research, CH 8903, Birmensdorf, Switzerland
H Schreier, Institute for Resources and Environment, University of British
Columbia, Vancouver, British Columbia, Canada
W Sekot, Universität für Bodenkultur, Gregor Mendel Strasse 33, A-1180,
Wien, Austria
E.H.M Sène, Forest Resources Division, Forestry Department, FAO, Viale
delle Terme di Caracalla, 00100 Rome, Italy
M Shiba, Forest Information and Resource Management Science, Graduate
School of Agriculture, Kyoto University, Kitashirakawa, Oiwake-cyo,Sakyo-ku, 606-8502 Kyoto, Japan
T.B Shrestha, IUCN Nepal, PO Box 3923, Kathmandu, Nepal
F.L Sinclair, Agricultural and Forest Sciences, University of Wales, Bangor,
Gwynedd LL57 2DG, UK
R.M Singhal, Indian Council of Forestry Research and Education, PO Box
New Forest, Dehradun, 248006, India
G.K Solntsev, Research Institute of Mountain Forestry and Forest Ecology,
Russian Federal Forest Service, 74 Str Kurortnyi Prospekt, KrasnodarRegion (Kray), Sochi, 354002, Russia
R Spinelli, CNR-IRL, via Barazzuoli 23, I-50136 Firenze, Italy
C Stadel, Institut für Geographie und Angewandte Geoinformatik,
Universität Salzburg, A-5020 Salzburg, Austria
P.A Stevens, Department of Life Sciences, University of the West Indies,
Mona, Kingston 7, Jamaica
M Suda, Technical University of Munich, Am Hochanger 13, 85354
Freising, Germany
P.G Tchouto, The Mount Cameroon Project, Limbe Botanic Garden, PO Box
437, Limbe, South West Province, Cameroon
S.R Templeton, Department of Agricultural and Resource Economics and
Policy, 207 Gianni Hall, MCH 3310, University of California, USA
T.H Thomas, Agricultural and Forest Sciences, University of Wales, Bangor,
Gwynedd LL57 2DG, UK
A.J Thomson, Canadian Forest Service, Pacific Forestry Centre, 506 West
Burnside Road, Victoria, British Columbia, V8Z 1M5, Canada
Trang 21K Thornber, International Institute for Environment (IIED), 3 Endsleigh
Street, London WC1H 0DD, UK
G Torta, Viale A Volta, 81-50122 Florence, Italy
V Tosi, Forest and Range Management Research Institute, 38050
Villazzano, Trento, Italy
N.J Turner, School of Environmental Studies, Box 1700, University of
Victoria, Victoria, British Columbia, V8W 2Y2, Canada
S Varela, Ministry of the Environment, Natural Resources and Fisheries,
Mexico
P Warren, Via Gratia Deledda 100, 00137 Rome, Italy
R Weingartner, Group for Hydrology, Institute of Geography, University of
Bern, Hallerstrasse 12, 3012 Bern, Switzerland
G Weiss, Institute of Forest Sector Policy and Economics, Universität für
Bodenkultur Wien, Gregor Mendel Strasse 33, A-1180, Vienna, Austria
E Wisniewska, Institute of Geodesy and Cartography, Department of
Cartography, 2/4 Jasna St, 00-950 Warsaw, Poland
P.C Xanthopoulos, Economic and Regional Development Department,
Panteion University, Athens, Greece
Y Xiaosheng, Research Institute of Subtropical Forestry (RISF), Chinese
Academy of Forestry, Fuyang, 311400 Zhejiang, People’s Republic ofChina
T Ya, International Centre for Integrated Mountain Development (ICIMOD),
4/80 Jawalakhel, PO Box 3226, Kathmandu, Nepal
Y.C Youn, Department of Forest Resources, Seoul National University,
Suwon, 441-744, Republic of Korea
I Yunusova, Kyrgyz–Swiss Forestry Support Programme, Forest Institute,
PO Box 2011, Bishkek 720000, Kyrgyz Republic
A Zanzi Sulli, DEEAF, Piazza delle Cascine 18, 50144 Florence, Italy
T Zawila-Niedzwiecki, Institute of Geodesy and Cartography, Department
of Cartography, 2/4 Jasna St, 00 950 Warsaw, Poland
W Zimmermann, Swiss Federal Institute of Technology (ETHZ), CH-8092
Zurich, Switzerland
P.C Zingari, European Observatory of Mountain Forests, Les Thermes,
F-73230 Saint Jean d’Arvey, France
Trang 22Foreword: Linking mountain forests
conservation with sustainable human development
For aeons, mountains, particularly those covered in deep forest, have ated an aura of hidden power, mysticism and spiritual authority on humanlife As a multidimensional landscape, their towering features are believed tocontrol human welfare Even now, many believe that these ancient percep-tions are real This was demonstrated by the inclusion of mountains in Agenda
gener-21 of the 1992 Earth Summit While this blueprint for sustainable humandevelopment recognized that mountain forests play a central role in providinggoods and services for the benefit of humankind, there is a paucity of targetedresearch and empirical data demonstrating tangible links between mountainforest conservation and sustainable human development
The problem
Japan, South Korea, Sweden and Finland are among the countries where forestconservation is most intimately linked with economic development, yet nearly60–80% of their surface area is forested, in contrast with the world average ofless than 27% In these four countries, both tangible and intangible values offorests have been integrated into forest policies and plans Consequently, forestcover has not diminished here Natural forest in most of the world is shrinking
as forestry management, particularly extraction of indigenous species, hasnot been sustainable Global loss of forest cover is forecasted to be between
16 million and 20 million ha in the next two decades (Palo and Uusivuori,1999) These observations raise the question: Can the forestry policies and
Trang 23practices in Japan, Korea, Sweden and Finland be replicated elsewhere indeveloping countries? Are these options practical and pragmatic in poordeveloping mountainous countries with limited capacity? These questions willremain largely theoretical unless the developing countries follow the examples
of these four countries They too must orient forestry research and practices
to respond to national priorities and paradigms with agendas based not onrhetoric but on harsh realities
Japan, Korea, Sweden and Finland have demonstrated that good sciencecoupled with good economics and pragmatic politics, can be effective in linkingmountain forests with sustainable human development It would be risible toassume otherwise merely because international donors and NGOs makeclarion calls for ‘sustainable development’ as a panacea for developingcountries’ problems
Sustainable development vs sustainable use
While ‘sustainable development’ was the buzzword of the 1990s, it meansdifferent things to different people, particularly when ethical values, culturaland religious beliefs rather than economic parameters are considered Theparameters and tools used to measure sustainable development have been atbest ‘creatively vague’ Consequently, developing country planners often findthe difference between ‘normal’ development and ‘sustainable development’ isblurred, particularly when addressing issues related to health, education,poverty, unemployment and underemployment Without clearly definedoperational parameters, time frames and verifiable time-sensitive indicators,these discussions will remain largely hypothetical
In 1987, the World Commission on Environment and Developmentdefined sustainable development as ‘the ability to meet the needs of the presentwithout compromising the ability of future generations to meet their ownneeds’ (WCED, 1987) Consequently, sustainable development has often beenequated with sustainable use Sustainable use is more complex in mountainforests than the lowlands In the mountains, the non-timber value of forests forthe goods and services they render may often exceed the commercial value
of exploitation of forest produce It is thus necessary to review the role ofmountain forests holistically, in the context of sustainable use of the ecosystemrather than sustainable use of forest produce
Use-it-or-lose-it vs no-use-is-best-use
Recently, sustainable use has triggered debates among economists, ecologistsand natural resource managers These debates can be generalized in two
Trang 24categories Firstly, the Use-it-or-lose-it mantra; secondly, the
No-use-is-the-best-use paradigm Nowhere is this epitomized more than by mountain forests.
Proponents of Use-it-or-lose-it preach that only tangible market-based
usage provides the best options to link forest conservation with sustainabledevelopment; they have faith in market-based incentives to resolve the
problems In contrast, supporters of No-use-is-the-best-use claim that
non-tangible benefits, and the services provided by mountain forest in sustainingclean air and clean water, and their role in controlling land degradation andenvironmental pollution, outweigh any financial value They question thepracticality of attaching a market value to the non-marketable goods andservices of mountain forests They also challenge the morality of attaching aprice tag to ethical and spiritual values of ‘Mother Nature’
Strategic options for the next millennium
The role of mountain forests in protecting soil and water supplies, maintainingrainfall, tourism development, providing water and energy, holding worldbiodiversity, ethical values and spiritual needs, has been greatly amplified(Messerli and Ives, 1997) However, few of these prescriptions have beentranslated into concrete action Mountain ecosystems in general do not ratehigh in the priority list of development aid agencies and governments exceptfor a handful of accessible or tourism sites This will remain largely unchangedunless the linkages between mountain forest conservation and sustainabledevelopment can be empirically demonstrated with science-based facts andfigures
Strategic options for targeted research and development must be site- andobjective-specific Five strategic options could be optimized to link mountainforest conservation with sustainable human development, as described below
Link mountain forest conservation with potable water supply
Water gives life – mountain ecosystems are water reservoirs for civilization Aunique feature of mountain forests is that they harvest a significant amount ofwater in the clouds engulfing them; forest canopies continually trap moisturefrom the clouds Consequently, they regulate precipitation and evaporationrates and control the water supply Forest felling in the mountains changes notonly the volume but also the distribution of water in the lowlands
The state of New York provides a good example of linking highland forestswith lowland water supply; although 200 km from New York, large areas ofthe Catskill Mountains are preserved solely to protect the water source.Government law prohibits any resource harvesting This is akin to forestprotection on the southern slopes of Langtang–Gosikunda–Helembu in order
Trang 25to assure water supply to the burgeoning population and water deficient city ofKathmandu, yet engineers and development planners who have designedmultimillion dollar schemes to harvest water in Melamche in the Gosikunda–Helembu axis have largely ignored this linkage.
Link mountain forests with soil and water conservation, prevention of land degradation and hydrological benefits
The assumed linkages between deforestation in the highland with water-flowreductions in the lowland are not new Greek philosophers as far back as in
400BCbelieved that loss of hillside forests reduced the availability of spring andground water, yet there is a dearth of scientific research to substantiate theseassumptions It is claimed that lack of forest litter and undergrowth (ratherthan lack of canopy) are the key factors triggering erosion, but also believedthat it is not tree removal itself, but the methods of extraction that triggermassive erosion
A few studies have linked deposits of eroded materials and river-bornesediments with reducing the benefits accrued by dams, hydropower, irrigationand flood control devices The global cost of loss of reservoir capacity isestimated to be US$6 billion per annum (Mahmood, 1987) However, there isonly a handful of studies that provide any hard data on the economic impacts
of upland forestry practices on dam performance A large effort is needed toconvince decision-makers to take the issues seriously
Link mountain forest conservation with climate change
In the later part of the 20th century, climate change became a popular topic ofconcern The causes and consequences of climate change recognize no politi-cal boundary; mitigation measures are recognized as their ‘common future’ forboth developed and developing countries
While the 1997 Kyoto Protocol of the United Nations Framework tion on Climate Change specifically recognizes the role of forests in combatingglobal warming, scientific data linking climate change with mountain forests
Conven-is grossly inadequate Price and Barry (1997) have reviewed the relationshipsand gaps in research in linking climate change and mountain ecosystems.More targeted research is needed to substantiate the intrinsic value of moun-tain forests with regard to climate change, particularly as carbon sinks
Link mountain forest conservation with sustainable tourism
Tourism is the world’s largest industry Mountain tourism, particularly in theHimalayas and the Andes, has the highest growth rates In the past, much
Trang 26attention has been paid to the negative impacts of tourism on the forests,particularly in the Himalayas.
The criticisms stemming from tourism impacts on forests and culture areoften voiced by outsiders, mostly anthropologists and environmentalists,rarely by residents The residents see tourism as source to supplement theirlivelihood and escape from poverty The Annapurna and Sagarmatha (MtEverest) basins in Nepal clearly demonstrate that despite criticism and con-cerns of its impacts on forest and local culture, mountain tourism is notwaning, but increasing Procrastination by a few outsiders will not drivetourism away; the efforts of targeted research in the mountain forests shouldnot now be geared only towards looking at the negative aspects of tourism, butshould be turned around to investigate the mitigation and positive aspects,particularly on how to manage tourism and orient it towards sustainabledevelopment
Link mountain forest with biodiversity benefits
Mountain forests are a repository for the world’s highly significant species,ecosystems and genetic material; half of the world’s 90,000 species of higher
plants in the neotropics are found in the montane zone (Churchill et al., 1995).
The total number of plant species in the Himalayas alone is estimated to be over25,000 In addition, the forests and grasslands in the same region areestimated to harbour 75,000 species of insects and invertebrates and morethan 1200 species of mammals and birds Mountain forests are also home tomany of the world’s endemic species, and species of high value for pharma-ceutical and agricultural industries
The rationale for conserving biodiversity has been extensively described(UNEP, 1995) Direct consumptive economic benefits stem from their use forfood, fodder and medicinal plants, mostly critical to modern pharmaceuticaland agro-based industries The value of mountain forest biodiversity to servicehumankind has not been fully realized – an inventory of medicinal andaromatic plants, and other species, in the world’s mountain forests is lacking.Though more than 100 million people in and around the Himalayas usetraditional medicine, applied research in ethnobotanical studies is scarce Gaps
in scientific research have promoted inconsistencies in policy and practice onconservation and sustainable use They have also been detrimental to themountain communities by directly affecting their incomes (Olsen and Helles,1997)
Today, the forests in developed and industrialized countries seem to be ing In contrast, the developing countries, particularly the tropical countries,are losing 14 million ha of forests annually (FAO, 1997a) In developedcountries, the relationship between good science and sustainable development
Trang 27expand-has been essential in linking forestry with economic growth and quality oflife Unless forestry research can produce a clear and simple picture thatconcomitantly links good forestry practices in mountain ecosystems withsustainable human development, the fate of mountain forests in developingcountries is, at best, uncertain.
Nearly a decade has passed since the Earth Summit adopted mountainecosystems, yet progress is not satisfactory With the probable exception of afew such as Global Environment Facility (GEF), the Food and AgricultureOrganization of the United Nations (FAO), the International Centre forIntegrated Mountain Development (ICIMOD) and some research orientedbodies and NGOs, most governments and development aid agencies have onlypaid lip service to the mountain ecosystems chapter (Chapter 13) of Agenda
21 The GEF has developed an operational programme specifically targeted atmountain ecosystems This operational programme embodies cross-cuttingglobal themes for sustainable development, as outlined in Chapter 13 ofAgenda 21, as it links conservation of mountain forests and biodiversitywith socio-economic development goals It has also provided more thanUS$60 million to assist developing countries and countries in transition forconservation and sustainable use of mountain ecosystems The GEF is only one
of the players – it cannot face all of the emerging challenges alone
The challenges include: How to conserve and manage dwindlingmountain forest resources in a sea of conflicting resource consumption andland-use practices? How to integrate traditional practices and cultural values
in forest conservation with economic growth? How to fulfil the needs of manydiverse players and stakeholders when all sectors seek preferential treatment?How to garner public support and acceptance for sustainable development,which by nature is long term? How to resolve conflicts without imposing thetop-heavy command and control approaches prevalent today? How to findfunds for research and development, and how to implement their findings?
It has often been said that linking forest conservation with sustainablehuman development is not science but politics; it is an art – an art of thepossible This art of the possible also requires an ability to distinguish betweenwhat is desirable and what is practicable Good science and good research havebeen the foundation of successful programmes The art of linking mountainforest conservation with sustainable development is no exception to this rule.These five areas provide some viable strategic options for the new millennium.But the outcomes of these science-based practices must not only be tangibleand visible; they must also be ecologically sustainable, politically palatable andeconomically viable
Hemanta R MishraGlobal Environment Facility Secretariat, World Bank,
Washington, DC 20433, USA
Trang 28Preface
In 1996, the Executive Board of the International Union of Forestry ResearchOrganizations (IUFRO) established a Task Force on Forests in SustainableMountain Development This report is the primary output of the Task Force,which concludes its work at the IUFRO Congress 2000 Its terms of referencerecognize that it should build on four linked trends:
1. A widespread shift in the science and practice of forestry, from emphasis
on the production of wood towards management based on recognition thatforests serve multiple functions and produce a wide range of outputs (as recog-nized in many recent actions and initiatives, including those relating to thework of the Intergovernmental Forum on Forests);
2. Changing expectations regarding the roles of mountain forests amongpopulations around the world, in an increasingly urbanized global society;
3. Rapid rates of change, both perceived and measured, in the cover and uses
of forests and adjacent ecosystems in mountains around the world;
4. The growing recognition of the global importance of mountain regionsand their inhabitants, underlined by the inclusion of a chapter (Chapter13: Managing Fragile Ecosystems: Sustainable Mountain Development)
in ‘Agenda 21’, which notes the central role of mountain people inmanaging mountain resources and the importance of integrated watershedmanagement
With respect to the roles of forests in the sustainable development of mountainareas, the general objectives of the Task Force were to:
Trang 291. Advise IUFRO’s Executive Board on current issues, initiatives, andresearch needs;
2. Provide a framework for developing and strengthening linkages, bothwithin the IUFRO membership and between the membership and otherrelevant organizations and initiatives
Initial activities of the Task Force included developing a database of activeindividuals and a side meeting at the World Forestry Congress, held inAntalya, Turkey, in October 1997 (see http://iufro.boku.ac.at/iufro/taskforce/tffmd/evtffmd.htm) Together with these activities, it is hoped thatthis report goes a considerable way towards achieving the objectives of theTask Force It should be realized, however, that the report does not provide anexhaustive overview of all of the highly diverse range of topics which itconsiders; particularly for general background on sustainable development in
mountain regions, the reader is directed to Mountains of the World: a Global
Priority (Messerli and Ives, 1997) Another major recent publication is the
proceedings of IUFRO’s Inter-divisional conference on ‘Forest ecosystem andland use in mountain areas’, held in Seoul, Korea, in October 1998 (KoreanForestry Society, 1998)
The authors of the 91 contributions to this report come from a very diverserange of backgrounds, and I am grateful to each of them for their time, energyand willingness to be flexible For some topics, authors have been able toprovide a comprehensive overview at the global scale For others, an overview
is provided at a regional or country scale Other authors have provided casestudies which illustrate topics at local to national scales This approach wastaken in recognition that a comprehensive global overview of all the relevanttopics is probably not possible at present; in addition, a secondary aim was toensure reasonable representation within the authorship – and the topicsconsidered – from different parts of the world The need for such a diversity of
authors has been noted as a problem with Mountains of the World: a Global
Priority, which was largely written by male authors from Western Europe and
North America However, given the relative availability of literature resourcesand the variation in scientific cultures across the world, the principle ofdiversity may in some cases have led to a less developed treatment of an issuethan might be expected
Each author was asked to include the following elements in her or hiscontribution:
1. Why we need to know (i.e importance of topic vis-à-vis the roles of forests
in sustainable development in mountain regions);
2. What we know (e.g results of research);
3. How we know (e.g methodology);
Trang 304. What we need to know (e.g missing information or data, importance ofgaps in information or data; or insufficient research activities in certain places
or on certain sub-topics);
5. What next (e.g desirable future research or other activities)
Most authors attempted to answer these questions – or were asked to do so,after review of their initial contributions – and the recommendations for futureaction deriving from the answers to the last two questions may be used todefine priorities for future research and action, as discussed in the intro-ductions to each of the ten sections of the report
The selection of authors and the structure of the report were developed asfollows, with the help of a number of people whose assistance is gratefullyacknowledged A review of recent literature was undertaken in summer 1998
by Mark Dwyer This was then used as the basis for a first draft table ofcontents, including potential authors of papers, prepared by Thomas Mather.This, and a series of later drafts, were circulated among members of the FAOForestry Department, the Intergovernmental Forum on Forests, the IUFROTask Force, the Mountain Institute, and the Swiss Agency for Developmentand Cooperation, who commented on the structure and contents andsuggested potential authors I am particularly grateful to Elizabeth Byers,Larry Hamilton, Christian Küchli, Mette Løyche Wilkie, Uli Lutz, DougMcGuire, Tage Michaelsen, Jane Pratt, Pietro Piussi and El Hadji Sène for theirassistance in this phase and later in the preparation of the report All of thiswork was done on a voluntary basis; however, the process of contactingauthors, commissioning contributions, editing and compilation requiredsignificant funding I am very grateful to the following agencies for theirfinancial contributions to the eventual production and dissemination of thereport: the Department for International Development (UK), the Swiss Agencyfor Development and Cooperation, the Food and Agriculture Organization ofthe United Nations, and the Norwegian Ministry of Foreign Affairs Theirassistance permitted me to employ Nathalie Butt to assist in all aspects ofpreparing the report, and I would like to record my great appreciation for herpatience, efficiency and hard work in ensuring its eventual smooth delivery –especially after her computer crashed just before the manuscript wascompleted Finally, I would like to thank Jeff Burley, President of IUFRO, forgiving me the opportunity to coordinate the Task Force, and Tim Hardwick
of CAB International, for his support during all phases leading up to the
publication of this report
Martin F PriceOxford, December 1999
Trang 31List of Acronyms and Abbreviations
List of Acronyms and Abbreviations
CATIE Centre Agronómico Tropical de Investigación y Enseñanza
CGIAR Consultative Group on International Agricultural Research
CIFOR Centre for International Forestry Research
CNR Consiglio Nazionale delle Ricerche, Italy
CONDESAN Consorcio para el Desarollo Sostenible de la Ecorregión
Andina
COST European Cooperation in the field of Scientific and Technical
Research
DFID Department for International Development
ETHZ Swiss Federal Institute of Technology, Zurich
FAIR The EC specific programme for Research, Technological
Development and Demonstration in the Field of Agricultureand Fisheries
FAO Food and Agriculture Organization of the UN
Trang 32FDF Forestry Development Fund, Costa Rica
FECOFUN Federation of Community Forest Groups of Nepal
FNCFF National Federation of Forest Communes, France
FONDECYT National Fund of Science and Technology, Chile
HIFCOM Hindu Kush–Himalayan Forum for Forest Conservation
ICIMOD International Centre for Integrated Mountain Development
ICRAF International Centre for Research on Agroforestry
IFAD International Fund for Agricultural Development
IIED International Institute for Environment and Development
ILRI International Livestock Research Institute
INBAR International Network on Bamboo and Rattan
INBio National Biodiversity Institute, Costa Rica
INEF International Network on Ethnoforestry
INGO international non-governmental organization
ISO International Organization for Standardization
ITE Institute of Terrestrial Ecology, UK
ITTO International Tropical Timber Organization
LIFE L’Investissement Financier pour l’Environment (EC)
MINAE Ministry of Environment and Energy, Costa Rica
NUKCFP Nepal–UK Community Forestry Project
ONF Office National des Forêts, France
PEFC Pan-European Forest Certification Scheme
SEEA System of Integrated Economic and Environmental
Accounting
UNCED United Nations Conference on Environment and
Development
UNCSD United Nations Commission on Sustainable Development
Trang 33UNEP United Nations Environment Programme
UNESCO United Nations Educational, Scientific, and Cultural
Organization
USAID United States Agency for International Development
USDA United States Department of Agriculture
US-EPA United States Environmental Protection Agency
WECS Water and Energy Commission Secretariat, Nepal
Trang 34Mountain Forests: Location, Characteristics and Trends
Chapter 1
1
Mountain Forests: Location,
Characteristics and Trends
The principal focus of this report is on the world’s mountain forests However,until now there has been no clear definition of where these forests are.Consequently, as part of the funding for the report from the Swiss Agency forDevelopment and Cooperation, a map of the world’s mountain forests wascommissioned from the World Conservation Monitoring Centre (WCMC) The
process of developing the map is described in the first section, by Kapos et al It
shows that, globally, there are about 9 million km2of mountain forest: 28% ofthe total global forest area However, while based on consistent data, this result
is preliminary, and further research could be valuable to refine the approach,particularly at regional and national scales
The other contributions in Chapter 1 provide the broad context for the rest
of the report, primarily from a biophysical viewpoint, but also referring tohuman populations as they interact with mountain forests in various ways.Three case studies continue the theme of mapping and monitoring mountainforests at national and regional scales: Kremsa and Varela describe themapping of Mexico’s forests; Castro and Kapelle discuss the development of ageographic information system (GIS) focusing on the biodiversity resources of
Costa Rica; and Zawila-Niedzwiecki et al present the results of a detailed study
of the decline of mountain forests in Central Europe using remote sensing All
of these case studies show that it is essential to combine a wide variety ofdata and information sources to characterize mountain environments, asnoted in the only book to focus on GIS and mountain environments (Price andHeywood, 1994) Particularly in terrain whose high topographic complexity
is overlain with a remarkable variety of ecosystems and changing land usepatterns – and where cloud cover is frequent – data from the interpretation of
CAB International 2000 Forests in Sustainable Mountain Development
Trang 35remotely sensed images and aerial photographs must always be combinedwith ground surveys and map interpretation to deliver products that aremeaningful and useful However, when this is done in a GIS, this can become
an irreplaceable means for aiding understanding, management and making
decision-As noted by Sène in this volume (page 138), FAO’s Forest ResourcesAssessment (FRA) unit is beginning to give special attention to trends in thestatus of mountain forests Data from the previous FRA (FAO, 1993b) showedthat tropical upland forests were disappearing at a greater rate than forests inany other biome: 1.1% per year The forthcoming assessment will showwhether this rate has increased or decreased; and deforestation continues inmany tropical regions due to a complex combination of economic, political anddemographic factors However, the pattern is rather different throughoutmuch of the temperate zone, where the area and/or the density of mountainforests is generally stable or increasing Piussi describes the process of sponta-neous reforestation in Europe, noting that its principal cause is land abandon-ment by farmers and shepherds; and that this is not a new phenomenon,having occurred during previous phases of depopulation, such as wars andplagues Another cause of an expansion of forest area is plantations, as
described by Good et al in their case study on the Welsh mountains Mountain
forests are also increasing in area and/or density in Japan, Korea and NorthAmerica, again primarily because of changing economic forces and/or depop-ulation Given the widespread nature of this phenomenon, research is needed
on a number of topics From the biophysical side, these include the need tobetter understand the dynamics of ecological processes and the impacts ofchanging forest cover and composition on water flows and erosion Research
is needed on best practices for establishment (for afforestation, rather thanspontaneous reforestation), management and marketing of forest products.The interactions of ecological and societal forces also need to be better under-stood, in order to determine which areas should be allowed to return to forest,
or planted, in relation to societal values and goals
Among the central values of mountain forests is their rich biodiversity.Grabherr notes that mountains are biodiversity hotspots, and provides anoverview of the various factors that make them so Kappelle and Juárez provide
an overview of one of these hotspots – Costa Rica – detailing research activitiesand needs, the designation and roles of protected areas, and the societal values
of these forests Ndam et al discuss the issues affecting Mount Cameroon,
one of the most biodiverse parts of Africa These three contributions make itclear that the conservation of biodiversity is a long-term process that must beimplemented with the full involvement of local people, and must not be based
on purely scientific justifications However, as Grabherr states, knowledgeregarding the biodiversity of mountain forests is scattered There are major
Trang 36gaps with regard to almost every aspect, from inventory and description,
to understanding and prioritising human uses, and predicting the potentialimpacts of climate change While a Global Mountain Biodiversity Assessmenthas recently been started by Diversitas, in partnership with the InternationalGeosphere-Biosphere Programme (IGBP) and Swiss organizations (http://www.unibas.ch/gmba/), this only focuses on the ecosystems from the uppermontane forest upwards A coordinated effort is also needed to address thediverse aspects of mountain forest biodiversity
One characteristic of mountain ecosystems is that they are particularlydynamic in both space and time Major disturbances may only occurinfrequently, but have significant influences on forest ecosystems Peterson
et al outline the three most common ‘natural’ types of disturbance – fire,
wind and geomorphic – and note their interactions both with other types
of ecological processes and with human activities Moving on from thisglobal overview, Sarmiento discusses the history of ‘natural’ and humandisturbance of Andean forests, and the needs and means for their restoration.Both of these papers stress the importance of bringing together a wide range
of players – research scientists, foresters, engineers, local communities, ernmental bodies – in all aspects of research, decision-making and programmeimplementation, and that much research is needed to better understandprocesses of disturbance and restoration at all temporal and spatial scales.Sarmiento also calls for specific legislation and policies to foster restoration
gov-of degraded ecosystems; an issue discussed particularly in Chapter 8 gov-of thisreport
Peterson et al note that global climate change and air pollution may
be considered as particular types of anthropogenic disturbance, and that, overthe time scale of decades to centuries, global climate change may be the mostsignificant agent of change in many of the world’s mountain ecosystems.These two major issues for the future are considered in papers by Benistonand Innes Beniston begins by stressing the importance of the interannual andintra-annual variability of climate, and particularly extreme events, formountain forests He traces recent research on climatic variability, long-termclimatic changes and extreme events in the mountains of Europe and else-where, and presents modelling approaches developed to try to understand thepotential responses of forests to climate change Innes delves in greater detailinto the responses of forests to both air pollution and climate change, under-lining the fact that species respond individually to environmental change, andthat most studies of such responses have considered the impacts of only onetype of change on mountain forests Both authors identify major areas forexperimental research, field studies, monitoring, and modelling, all with theultimate aim of providing usable multidisciplinary information for decision-making for sustainable management
Trang 371.1 Developing a map of the world’s mountain forests
V Kapos, J Rhind, M Edwards, M.F Price and C Ravilious
The many contributions in this book consider the diverse roles of mountainforests in relation to sustainable development To provide a global context forthese contributions, it is first necessary to define the locations and types ofmountain forests
The first global digital map of forests was published by the World vation Monitoring Centre (WCMC) in 1996, but this did not identify mountainforests While subsequent versions did identify some mountain forests based onclassifications in the source data, coverage of these important ecosystems wasnot consistent Global forest data are constantly being updated both at WCMCand through remote sensing programmes (e.g US Geological Survey’s EROSData Centre in collaboration with FAO and WCMC), but explicitly identifyingmountain forests in a globally consistent manner is not at present included inany of these efforts
Conser-In this paper, we present the approach taken by WCMC to generating amap of the distribution of the world’s mountain forests This required us todefine and map mountains in a manner that could be used to identify thesubset of the world’s forests that fill the important roles and characteristics ofmountain forests
1.1.1 Defining mountains
In the extensive literature on mountains that has developed in recentyears there has been a distinct reluctance to produce a concise definition ofmountains or mountain areas Although this is to some degree justified by thestatement that mountains are defined by local perceptions, it is not helpful inproviding a global overview of mountains in a geographical context Gerrard(1990) noted that ‘Numerous definitions of what constitutes a mountainhave been proposed, but mountains are extremely diverse landforms and ithas proved difficult to achieve consistency in description and analysis Severalcriteria have been used, such as elevation, volume, relief, and steepness, as well
as spacing and continuity’ A recent map of ‘Mountains and highlands ofthe world’ in Messerli and Ives (1997) used altitude as its only criterion, and asdiscussed below, highlights large areas of mid-elevation plateau that cannotreally be considered mountainous, while failing to distinguish low mountainareas It neither substantiates nor provides an alternative to the often-citedstatistic of 20% of the globe being mountainous (Louis, 1975); a statistic usedless often is that of Fairbridge (1968), who estimated that 36% of the Earth’sland area is composed of mountains, highlands and hill country
Trang 38The agreed components in defining mountains are (relative) altitudeand steep slopes, which combine to generate environmental gradients and
‘high energy’ unstable environments (Ives et al., 1997) It is difficult to select
a specific threshold altitude for defining mountains While there is littledispute that very high elevations are mountain environments, and humanphysiology is affected by changes in atmospheric oxygen levels at elevationsabove about 2500 m (Houston, 1964), there are a number of recognizedmountain areas at rather low elevations Using simple altitude thresholdsboth excludes older and lower mountain systems, such as the Appalachiansand the Urals, and includes areas of relatively high elevation that have littletopographic relief and few environmental gradients, such as the US state ofKansas and the East African Rift Valley, which are largely above 1500 m.Using slope as a criterion on its own or in combination with altitude canresolve the latter problem, but not the former Steep slopes are a feature ofyoung mountain systems, but older mountains are characterized by moregentle topography
It is also difficult to link these physical parameters to ecological variation
in any simple fashion The effect of altitude on natural vegetation varies withlatitude, continentality and size of the mountain mass A number of reviewsaddress the issues of what factors determine the altitude of timberline, theupper limit of forest growth, which varies from below 500 m at high latitudes
to nearly 5000 m near the equator (Troll, 1973; Tranquillini, 1979;Holtmeier, 1994) However, the variation at any given latitude is also large,for example 1100–2500 m at 44° N Lower limits to biological variationassociated with mountains are also difficult to pinpoint In recent vegetationmapping efforts in Central America, a regional committee of experts agreedthat montane forest formations can usually be identified by a loweraltitudinal threshold of 1000–1200 m and premontane vegetation by limits of500–700 m However, it is well recognized that isolated mountains and smallmountain masses in the same region have a much-compressed zonation ofvegetation due to a tropical version of the Massenerhebung effect (Grubb,1977)
Another previous area of study has been to identify mountain protectedareas (Thorsell and Harrison, 1992) This approach used both a minimumaltitude threshold (1000 m) and total elevation range (1500 m) to identifythese areas These criteria were useful for limiting the number of protectedareas under consideration, but excluded a number of mountain areas ofconsiderable importance
In the present study, we used digital data on elevation and forest cover,first to define mountain areas by empirically testing combinations of elevation,slope and local elevation range, and subsequently to identify forest coveroccurring in mountain areas
Trang 391.1.2 Data and Methods
Digital elevation model (DEM)
GTOPO30 is a global digital elevation model (DEM) with a horizontal gridspacing of 30 arc seconds (approximately 1 km) GTOPO30 was derived fromseveral raster and vector sources of topographic information GTOPO30,completed in late 1996, was developed over a 3-year period through acollaborative effort led by staff at the US Geological Survey’s EROS DataCentre We used ARC-INFO and this dataset both to identify the location ofareas above particular altitudes and to generate grids containing the followingparameters:
• Slope – this is calculated by fitting a plane to a nine-cell grid centred on thetarget cell and using trigonometric relations to calculate the plane’s slopeangle, which is then assigned as the slope of the target cell
• Local elevation range – by defining a radius of interest around each gridcell it is possible to measure the maximum and minimum elevation within
a particular neighbourhood, and their difference This enables one toidentify areas that occur in regions with significant relief, even thoughelevations may not be especially high, and conversely high-elevationareas with little local relief
Forest data
In recent years, WCMC has compiled digital maps of global forest cover
by drawing together data from a variety of national and international
sources These include: the WWF World Forest Map (WCMC, 1996); the data compiled for the CD-ROM, A Global Overview of Forest Conservation
(WCMC, 1997a); and the updated version included in the final report ofthe World Commission on Forests and Sustainable Development (1999).The data used in this analysis are a further update, version 3, in whichforest cover in the early 1990s (on average) is mapped in a total of 26temperate and tropical classes at a nominal resolution of 1 km The classesare principally closed forests (canopy cover >30%), with the exception ofthe ‘sparse trees and parkland’ classes, which represent open forests and
woodlands with a canopy cover of 10–30% (Iremonger et al., 1997) The
sources of the data are predominantly satellite remote sensing, but a widerange of national sources and biological information were used to produce thisdataset Full source information for the forest data can be obtained fromWCMC
Trang 40Defining mountains
We combined the parameters derived from the DEM iteratively, starting from anumber of first principles Firstly we used 2500 m, the threshold above whichhuman physiology is affected by oxygen depletion, as a limit above which anyenvironment at all would be considered mountainous Secondly, we consid-ered that at middle elevations, some degree of slope was a necessary feature ofmountainous terrain, and that slopes should be steeper at lower elevations Weused empirical testing to select a slope criterion that was effective in excludingmid-elevation plateaux like those in Kansas and East Africa Finally, weexamined local elevation range as a way of including low-elevation and oldermountains of regional significance without designating all areas at theseelevations as mountains The local elevation range was evaluated for a five-cell (or 7 km) radius around the target cell
Identifying mountain forests
Although some of the source data on forests include explicit identification ofmontane forests, many of the other sources used in the WCMC global forestdataset do not Therefore, the forest data with a simplified classification wereoverlaid on the mountains map so that forests of all classes occurring inmountain areas could be identified in a consistent manner
1.1.3 Results
The analytical approach described above led us to identify six classes of
moun-tain area as shown in the insert map, Mounmoun-tain Areas of the World – 2000.
The upper three classes are delimited purely by elevation: 2500–3499 m;3500–4499 m and≥4500 m Land between 1500 m and 2499 m is classed asmountain if it slopes more than 2°; this threshold proved to be appropriate foreliminating mid-elevation plateaux Between 1000 m and 1499 m, land thateither surpasses a steeper slope threshold of 5°, or has a local elevation range
of 300 m or more, is classified as mountain Between 300 m and 999 m, landwas classed as mountainous if the local elevation range was 300 m or more.Finally a spatial filter was applied that reclassified isolated ‘non-mountain’grid cells in mountain areas according to the predominant class among theimmediate neighbours
The map shows clearly the major high-altitude mountain ranges of theworld and equally clearly the lower, gently sloping older mountain ranges,such as the Urals, the Appalachians and the Atlantic Highlands of Brazil.Mountains such as the Rwenzori that rise from mid-elevation plateaux are