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  • ACRS 1999


    Environment
    Estimation of Emission changes about green house effect gasses by land-cover changes using remote sensing and GIS in Sumatra Island, Indonesia

    Aboveground carbon stock changes
    Aboveground carbon content estimation of each land cover was calculated by multiplying the area of each land cover with carbon stock per unit area. Table 3 has showed the changes of aboveground carbon due to land cover changes. Total above ground carbon stock decrease from 6.16 x 108 ton in 1986 to 5.66 x 108 ton in 1992 or loss of about 0.50 x 108 ton within 6 years equal to 8.3 millions ton per year. The loss of aboveground carbon was mainly came from primary forest conversion. IPCC have divided the loss of aboveground carbon content into on site and off-site release. These two categories were classified further into direct burning (fuel wood and slash and burn agricultural) and decomposition process release of unburned biomass (Houhton et.al., 1996). Thus the amount of carbon and GHG released to the atmosphere were depended on these processes. Estimation of the amount carbon and GHG release need yearly basis time series of spatial data and the information on commercial wood and fuel wood harvest, and burning efficiency data of each land cover type.

    Soil Greenhouse gas emission changes
    GHG flux of soil varies depend on type the site condition and season. The comparisons below were made based on flux measurement conducted in November 1997 in several sites of Jambi Province. The calculation results of total flux based on 1986 and 1992 land cover data for major land cover presented in Table 4. Comparison of the total GHG flux of the two periods of time studies could not be performed since there are still no information on GHG flux of soil surface under cash crops plantation and secondary forest. However, it seems that the conversion of natural forest will cause on the decrease of methane gas absorption and induce the increase of nitrous oxide and carbon dioxide flux emission.

    Table 4 Greenhouse gases flux changes between 1986 and 1992
    Land-
    use/Land
    cover class
    Total flux of CO2 (mg/day) Total flux of N2O (mg/day)Total flux of CH4 (mg/day)
    19861992 1986 1992 1986 1992
    Primary
    forest
    1.69x10141.28x10143.2x1092.43x109-1.45x1010 -1.10x1010
    Secondary
    forest
    0.00 5.75x10120.007.03x1080.00-3.36x109
    Logged
    forest
    1.24x10141.54x10142.48 x1093.08x109-1.04x1010-1.29x1010
    Fallow
    land
    1.31x10148.46x10134.51 x1092.91x109-1.00x1010-6.47x109
    Grassland7.76x10127.58x10121.42 x1081.38x1080.000.00
    Bare
    land
    2.44x10102.44x10105.67x1055.67x105-6.25x105-6.25x105
    Cash
    crops
    plantation*
    1.87x10136.75x10134.68x1081.69x1090.000.00
    Paddy
    field
    - -9.63x107 6.23x1077.22x1084.67x108
    Upland
    field
    0.002.41x10120.004.03x1070.00 0.00
    Cultivated
    land and
    Secondary vegetation
    8.00x10139.02x10133.43 x1093.87x109-3.33x109-3.75x109
    Cultivated
    lands and
    Settlement
    6.85x1012 8.33x10121.16 x1081.41x1080.000.00
    Total flux536.5x1012548.3x101214.4 x10915.1x109-37.5x109-37.0x109
    Note : calculations were made based on field measurement in November 1997, conducted by IC-SEA

    * : assumed flux of CH4 and CO2 of cash crops plantation are equal upland, while flux of N2O is equal to three times of upland field flux due to intensive fertilizer application.

    References
    • Adger., W. Neil and K. Brown. 1994. Land-use and the causes of global warming. John Wiley & sons. New York. 27I p
    • Ball, D. and R. Babbage. 1989. Geographical information system; defense application. New South Wales. Macathur Press. 257 p
    • Bappeda Jambi. 1985 and 1988. Jambi province statistics. Bappeda (in Indonesian)
    • Barbier, E.B, Joanne C. B. and A. Markandya. 1991. The economic of tropical deforestation. Ambio 20 (2) : 55 – 58
    • Burrough, A. 1986. Principles of geographical information system for land resources assessment, Oxford, Clarendon Press. Oxford, 193 p
    • Houghton, J.T., et.al. Greenhouse gas inventory reference Manual : page 5.1 – 5.74
    • Ikeda, H., Okamoto, K., and Fukuhara, M., 1994, Estimation of carbon budgets in croplands using Landsat TM data. In Proceedings of the 7th IUAPPA Regional Conference on Air Pollution and Waste Issues, held on November 2-4, 1994, Taipei, I, 139-146.
    • Khalil, M.A.K., R.A. rasmussen, M.X. Wang and L.Ren. 1991. Methane emissions from rice fields in china. Environ. Sci. Tech. 25: 979-981
    • Kira, Tatuo and Keiji Iwata. 1989. Nature and Life in Southeast Asia Volume IV, 1989. Fauna and Flora Research society, Kyoto, Japan.
    • Mahmood, N. etc. 1991. Characterization of environmental changes using remote sensing technique - a case study applied to Klang valley area. in Application of remote sensing in Asia and Oceania - Environmental change monitoring.. (Murai eds) Asian Assoc. on Remote Sensing
    • Maguire, J. etc. 1991. Geographical information system; principles and application. New York. John Wiley and Sons Inc. 588p
    • Myers, N., 1994. Tropical deforestation; rates and pattern in The causes of tropical deforestation (Brown, K. and D.W. Pearce eds.) England, UCL Press, pp 27 – 40
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