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Volumn 28, Issue 7, 1999, Pages 604-612

Evaluating the use of natural capital with the ecological footprint

Author keywords

[No Author keywords available]

Indexed keywords

CAPITAL MARKET; ECOLOGICAL ECONOMICS; WASTE MANAGEMENT;

EID: 0033367888     PISSN: 00447447     EISSN: None     Source Type: Journal    
DOI: None     Document Type: Article
Times cited : (200)

References (60)
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    • The data sources are: Food and Agriculture Organization of the United Nations (FAO). 1995. FAO Yearbook: Production 1994, Vol. 48. FAO, Rome. Food and Agriculture Organization of the United Nations (FAO), 1994. FAO Yearbook: Trade 1993, Vol. 47. FAO, Rome. Food and Agriculture Organization of the United Nations (FAO), 1995. FAO Yearbook: Forest Production 1993, FAO, Rome. World Resources Institute, 1996. World Resources 1996-1997. World Resources Institute, UNEP, UNDP, The World Bank, Washington DC. Food and Agriculture Organization of the United Nations (FAO), 1995. State of the World's Forests, FAO, Rome.
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    • The data sources are: Food and Agriculture Organization of the United Nations (FAO). 1995. FAO Yearbook: Production 1994, Vol. 48. FAO, Rome. Food and Agriculture Organization of the United Nations (FAO), 1994. FAO Yearbook: Trade 1993, Vol. 47. FAO, Rome. Food and Agriculture Organization of the United Nations (FAO), 1995. FAO Yearbook: Forest Production 1993, FAO, Rome. World Resources Institute, 1996. World Resources 1996-1997. World Resources Institute, UNEP, UNDP, The World Bank, Washington DC. Food and Agriculture Organization of the United Nations (FAO), 1995. State of the World's Forests, FAO, Rome.
    • (1995) State of the World's Forests
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    • 12944321940 scopus 로고    scopus 로고
    • note
    • Biomass yields, measured in dry weight, are taken from FAO statistics as listed in note 35. In the case of sea space, the production of fish protein is directly compared to the animal protein production of pasture as discussed in note 39.
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    • 2 per capita of protected space for water provision (World Resources Institute. 1996. World Resources 1996-1997. Oxford Press, New York. p. 306).
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    • W.H. Freeman, San Francisco
    • A rough analysis is provided in Cox, G. and Atkins, M. 1979. Agricultural Ecology: An Analysis of World Food Production Systems. W.H. Freeman, San Francisco, p. 571. More detailed accounts are given by Pauly, D. and Christensen, V. 1995. Primary production required to sustain global fisheries. Nature. Vol. 374. The first inclusion of sea space in footprint accounting was presented by Wada, Y., 1995. Ecological Foolprint of Consumption of an Average Japanese - (Aquatic Area), University of British Columbia, Canada.
    • (1979) Agricultural Ecology: An Analysis of World Food Production Systems , pp. 571
    • Cox, G.1    Atkins, M.2
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    • Primary production required to sustain global fisheries
    • A rough analysis is provided in Cox, G. and Atkins, M. 1979. Agricultural Ecology: An Analysis of World Food Production Systems. W.H. Freeman, San Francisco, p. 571. More detailed accounts are given by Pauly, D. and Christensen, V. 1995. Primary production required to sustain global fisheries. Nature. Vol. 374. The first inclusion of sea space in footprint accounting was presented by Wada, Y., 1995. Ecological Foolprint of Consumption of an Average Japanese - (Aquatic Area), University of British Columbia, Canada.
    • (1995) Nature , vol.374
    • Pauly, D.1    Christensen, V.2
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    • University of British Columbia, Canada
    • A rough analysis is provided in Cox, G. and Atkins, M. 1979. Agricultural Ecology: An Analysis of World Food Production Systems. W.H. Freeman, San Francisco, p. 571. More detailed accounts are given by Pauly, D. and Christensen, V. 1995. Primary production required to sustain global fisheries. Nature. Vol. 374. The first inclusion of sea space in footprint accounting was presented by Wada, Y., 1995. Ecological Foolprint of Consumption of an Average Japanese - (Aquatic Area), University of British Columbia, Canada.
    • (1995) Ecological Foolprint of Consumption of An Average Japanese - (Aquatic Area)
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    • note
    • The ratio for the sea is 0.2 based on the fact that the area appropriated for the catch of one unit of fish protein is three times the area of unimproved pasture appropriated for the production of the same quantity of meat protein.
  • 46
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    • FAO: Rome
    • For arable land, the factor is calculated by dividing national cereal yield by global cereal yield. The Swedish average yields were taken from the government statistics. The global yields stem from the Food and Agriculture Organization of the United Nations (FAO), 1995. FAO Yearbook: Production 1994. Vol. 48.: FAO: Rome. In the case of the Kävlinge catchment area, local yields were extrapolated from averages in Södra Götaland's coastal area and Södra Götaland's intermediate areas.
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    • Na11 SM9501, Statistiska Centralbyrån and Naturvårdsverket, Stockholm. In Swedish
    • Statistik för avrinningsområden 1992 (Statistical data for drainage areas 1992), Na11 SM9501, Statistiska Centralbyrån and Naturvårdsverket, Stockholm. (In Swedish).
    • (1992) Statistical Data for Drainage Areas 1992
  • 48
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    • 2-abs.xls). The spreadsheets also document the references used. The tables in the text present condensed aspects of the spreadsheet for illustrative purposes. The main spreadsheet and the two supplementary ones can be downloaded from Lund University's server at http://www.darwin.biol.lu.se/zoofysiol/ Lewan/Footprint.html.
  • 49
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    • Büro für Analyse und Ökologie, Zürich
    • 2 Balance). Büro für Analyse und Ökologie, Zürich. For chemical products the footprint component is that of its embodied energy (assumed to be fossil fuel).
    • (1991) 2 Balance)
    • Hofstetter, P.1
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    • note
    • 2 accumulation in the atmosphere.
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    • (The improved version of Our Ecological Footprint (24) in German).: Birkhäuser Verlag, Basel
    • Wackernagel, M. and Rees, W.E. 1997. Unser ökologischer Fußabdruck. (The improved version of Our Ecological Footprint (24) in German).: Birkhäuser Verlag, Basel. p. 104.
    • (1997) Unser Ökologischer Fußabdruck. , pp. 104
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    • note
    • An additional argument for calculating nuclear power like fossil fuel is the nuclear industry's economic shortcomings, nuclear power (without government subsidies) is not economic because of the high operational costs, not to mention the long-term costs for waste handling, safeguarding or risk. The simplest, least expensive for the operator (but not for our climate) and therefore most likely energy substitute at present is fossil fuel. This supports the idea of calculating nuclear power as if it were fossil fuel.
  • 53
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    • private communication, November
    • 2 concentration in the atmosphere (Alan AtKisson. private communication, November 1997).
    • (1997)
    • Atkisson, A.1
  • 54
    • 12944325531 scopus 로고    scopus 로고
    • Folke et al., 1997 (see 25)
    • Folke et al., 1997 (see 25).
  • 55
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    • Retention av växtnäring i vätmarker och sjöar. Kväve och fosfor i mark och vatten - En ödesfråga inför 2000-talet
    • Seminarium 22-23 mars
    • Leonardsson, L. 1995. Retention av växtnäring i vätmarker och sjöar. Kväve och fosfor i mark och vatten - en ödesfråga inför 2000-talet. Seminarium 22-23 mars. Kungliga Skogs och Lantbruksakdemiens Tidskrift 135/3. (In Swedish).
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    • note
    • The capacity of plant nutrient detention per wet area and of leakage from agricultural land was estimated by the Landskrona Ecology Group Consultants who are employed in a long-term project by the Kävlinge River Water Alliance.
  • 58
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    • note
    • The agricultural load in Malmöhus County exceeds the load from sewage plants. In e.g. the Kävlinge catchment with small nucleated settlements the factor is at least 20. K-Konsult, 1992. Kävlingeån Landskapsvårdsplan. The load balance is documented in the spreadsheet file malmö.xls., see note (42).
  • 59
    • 12944298496 scopus 로고    scopus 로고
    • note
    • We thank Carl Folke, Charles Hall, Larry Onisto, David Yount and an anonymous reviewer for their valuable and encouraging comments. We would also like to acknowledge the support of the Swedish Council for Planning and Coordination of Research (FRN), the Swedish Council for Forestry and Agricultural Research (SJFR), the Human Ecology Department of Lund University, the Lund University International Master's Programme in Environmental Science, the Institute for Resource Theory at Chalmers University, the Department of Systems Ecology at Stockholm University, The Baltic Youth Forum, the Stockholm Environment Institute, The Natural Step, Sweden, and Anáhuac University of Xalapa, Mexico.
  • 60
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    • note
    • First submitted 27 July 1998. Accepted for publication after revision 11 February 1999.


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