VEG_CLSS.DOC


                             1.  TITLE

1.1  Data Set Identification.

     Global land cover classification from satellite data.

     (Fixed ; UMD, NASA/GSFC)

1.2  Data Base Table Name.

     Not applicable.

1.3  CD-ROM File Name. 

      \DATA\VEGTATN\VEG_MAP\VEG_CLSS.VGC

     Note: capital letters indicate fixed values that appear on the CD-ROM 
     exactly as shown here, lower case indicates characters (values) that 
     change for each path and file.

     The filename extension (.sfx), identifies the data set content for the 
     file (see section 8.2) and is equal to .VGC for this data set.

1.4  Revision Date Of This Document.

     April 5, 1995.

                         2.  INVESTIGATOR(S)

2.1  Investigator(s) Name And Title.

     Dr. Ruth DeFries
     Department of Geography
     University of Maryland, College Park

     Dr. J.R.G. Townshend
     Department of Geography
     University of Maryland, College Park

2.2  Title Of Investigation.

     Global Mapping of Vegetative Land Cover

2.3  Contacts (For Data Production Information).

_________________________________________________________
              |      Contact 1     |    Contact 2        |
______________|____________________|_____________________|
2.3.1 Name    | Dr. Ruth DeFries   | Dr. John Townshend   |
2.3.2 Address | Dept. of Geography | Dept. of Geography  |
              | 1113 Lefrak Hall   | 1113 Lefrak Hall    |
      City/St.| College Park, MD   | College Park, MD    |
      Zip Code| 20742-8225         | 20742-8225          |
2.3.3 Tel.    | 301 405-7861       | 301 405-4050        |
2.3.4 Email   | rd63@umail.umd.edu | jt59@umail.umd.edu  |
______________|____________________|_____________________|

2.4  Requested Form of Acknowledgment.

     Please cite the following publication when ever these data are used:

      DeFries, R. S. and J. R. G. Townshend, 1994a, NDVI-derived land 
           cover classification at global scales. International Journal of 
           Remote Sensing, 15:3567-3586. Special Issue on Global Data Sets.

                            3.  INTRODUCTION

3.1  Objective/Purpose.

     The data set was developed to explore the conceptual and methodological 
     issues that arise when using the Normalized Difference Vegetation Index 
     (NDVI) as a basis for global classification of vegetative land cover.  
     The purpose of the study is to use satellite data to improve currently 
     available information on global land cover for applications to global 
     change research.

3.2  Summary of Parameters.

     The data set describes the geographic distributions of eleven major
     cover types based on interannual variations in NDVI (see section 
     8.2 for listing of cover types included).  Vegetation-type dependent 
     parameters as used in SIB2 are included in this documentation, see 
     section 11.

3.3  Discussion.

     Phenological differences among vegetation types, reflected in temporal
     variations in NDVI derived from satellite data, have been used to 
     classify land cover at continental scales.  This study explored 
     methodologies for extending this concept to a global scale.  A coarse 
     resolution (one by one degree) data set of monthly NDVI values for 1987  
     (Los, et al. 1994, Sellers, et al. 1994, 1995b) was used as the basis 
     for a supervised classification of eleven cover types that broadly 
     represent the major biomes of the world. Because of missing values at 
     high latitudes, the Pathfinder AVHRR data set for 1987 (James and 
     Kalluri, 1994)  for summer monthly NDVI and red reflectance values were 
     used to distinguish the following cover types: tundra, high latitude 
     deciduous forest and woodland, coniferous evergreen forest and woodland.

     The eleven cover types were selected primarily to conform with the cover 
     types required as input to climate models.  Training sets for each of the
     eleven cover types were identified as the areas where three existing 
     ground-based data sets of global land cover (Matthews 1983, Olson, et 
     al. 1983, Wilson and  Henderson-Sellers 1985) agree that the land cover 
     is present.

     The global land cover data set is the result of a maximum likelihood 
     classification of eleven cover types.  The data set has not been
     systematically validated.  Cursory validation indicates that the user
     should be aware of the following problems: 1) the distinction between 
     "cultivated" and "grassland" cover types may be inaccurate because the
     NDVI temporal profiles of these two cover types are not significantly 
     distinct, and 2) the "tundra" cover type may be inaccurate because of
     missing data at high latitudes.

                        4.  THEORY OF MEASUREMENTS

Not available at this revision.

                            5.  EQUIPMENT

5.1  Instrument Description.

     The global land cover data set was based on AVHRR maximum monthly 
     composites for 1987 of NDVI values at approximately 8 km resolution, 
     averaged to one by one degree resolution  (Los, et al. in press) .  A 
     Fourier transform was applied to smooth the temporal profiles and remove 
     aberrant low values (Sellers, et al. 1994, 1995b) .  At high northern 
     latitudes, the data set was based on the AVHRR Pathfinder data set for 
     1987  (James and Kalluri, 1994), resampled to a spatial resolution of 
     one by one degree and composited to obtain maximum monthly NDVI values 
     and corresponding red reflectance values for summer months.

     5.1.1  Platform (Satellite, Aircraft, Ground, Person...).

            Not applicable.

     5.1.2  Mission Objectives.

            Not applicable.

     5.1.3  Key Variables.

            Not applicable.

     5.1.4  Principles of Operation.

            Not applicable.

     5.1.5  Instrument Measurement Geometry .

            Not applicable.

     5.1.6  Manufacturer of Instrument.

            Not applicable.

5.2  Calibration.

     5.2.1  Specifications.

            Not applicable.

            5.2.1.1  Tolerance.

     5.2.2  Frequency of Calibration.

            Not applicable.

     5.2.3  Other Calibration Information.

            Not applicable.

                          6.  PROCEDURE

6.1  Data Acquisition Methods.

     Not available at this revision.

6.2  Spatial Characteristics.

     6.2.1  Spatial Coverage.

            The coverage is global.  Data in file are ordered from North to 
            South and from West to East beginning at 180 degrees West and 90 
            degrees North.  Point (1,1) represents the grid cell centered at 
            89.5 N and 179.5 W (see section 8.4).

            For additional information on acquisition and processing of the 
            data sets that were used to derive global land cover, see  (Los, 
            et al. 1994), (Sellers, et al. 1994, 1995b), and (James and 
            Kalluri, 1994) .

     6.2.2  Spatial Resolution.

            The data are given in an equal-angle lat/long grid that has a 
            spatial resolution of 1 X 1 degree lat/long.

6.3  Temporal Characteristics.

     6.3.1  Temporal Coverage.

            The data set is derived from data collected in 1987.

     6.3.2  Temporal Resolution.

            Not applicable.

                           7.  OBSERVATIONS

7.1  Field Notes.

     Not applicable.

                         8.  DATA DESCRIPTION

8.1  Table Definition With Comments.

--------------------------------------------------------------------------------
|                 8.2.1                   |            |           |           |
|Parameter/Variable Name                  |            |           |           |
--------------------------------------------------------------------------------
|    |                8.2.2               |     8.2.3   |  8.2.4    |  8.2.5   |
|    | Parameter/Variable Description     |Range        |Units      |Source    |
--------------------------------------------------------------------------------
|LAND_COVER_CLASSIFICATIONS               |             |           |          |
|    |                                    |Min = 0      |Not        |DeFries & |
|    | Value   Land Cover class           |Max = 15     |Applicable |Townshend |
|    | =====   ================           |             |           |          |
|    | 0   0   water                      |             |           |          |
|    | 1   1   broadleaf evergreen forest |             |           |          |
|    | 2   2   broadleaf deciduous forest |             |           |          |
|    |         and woodland               |             |           |          |
|    | 3   3   mixed coniferous and broad-|             |           |          |
|    |         leaf deciduous forest and  |             |           |          |
|    |         woodland                   |             |           |          |
|    | 4   4   coniferous forest and      |             |           |          |
|    |         woodland                   |             |           |          |
|    | 5   5   high latitude deciduous    |             |           |          |
|    |         forest and woodland        |             |           |          |
|    |6,8  6   wooded c4 grassland        |             |           |          |
|    | 7   6   c4 grassland               |             |           |          |
|    | 9   7   shrubs and bare ground     |             |           |          |
|    |10   8   tundra                     |             |           |          |
|    |11   6   desert, bare ground        |             |           |          |
|    |12   9   cultivation                |             |           |          |
|    |13       ice                        |             |           |          |
|    |14   9   c3 wooded grassland        |             |           |          |
|    |15   9   c3 grassland               |             |           |          |
--------------------------------------------------------------------------------
The data values in the first column are consistent with SiB vegetation classes 
(Dorman and Sellers, 1989).  It was not possible to separate SiB vegetation
classes 6 (broadleaf trees with groundcover) and 8 (broadleaf shrubs with
groundcover) using the classification method described here.  Class 6, 
therefore, includes both types, and there are no class 8 values in the data 
set.

In the SiB2 GCM application of Sellers et. al. (1995a, b) and for the purpose
of producing the NDVI related data sets elsewhere on the CD-ROM, this
classification is simplified to the right-hand column, where most
tropical seasonal biomes are assigned C4 grassland properties and temperate 
biomes with c3 ground cover are assigned cultivation properties. For the
FASIR corrections (see FASIR document elsewhere on the CD-ROM) classes 1,6 and
14 were merged and represented classes 1, 6, 8 and 14, classes 2 and 3 were 
merged, class 4 represented class 4 and 5 and class 12 represented classes 
7,9,10,11,12 and 15.

The cover class descriptions used in DeFries and Townshend (1994a) differ 
somewhat from the classes shown in Table 8.2.2. Their method resolved 11 
classes which are regrouped into SiB classes as shown in the following Table.

--------------------------------------------------------------------------------
|        8.2.6            |                      8.2.7                         |
--------------------------------------------------------------------------------
|  Classification numbers | DeFries and Townshend                              |
|  from the first column  |                                                    |
|  in Table 8.2.1         |    nomenclature                                    |
--------------------------------------------------------------------------------
|                         |                                                    |
|           1             |  Broadleaf evergreen trees                         |
|           2             |  Broadleaf deciduous trees                         |
|           3             |  Mixed trees                                       |
|           4             |  Needleleaf evergreen trees                        |
|           5             |  High latitude deciduous trees                     |
|           6,8           |  Grass with 10 - 40% woody cover                   |
|           7             |  Grass with <10% woody cover                       |
|           9             |  Shrubs and bare soil                              |
|          10             |  Moss and lichens                                  |
|          11             |  Bare                                              |
|          12             |  Cultivated                                        |
--------------------------------------------------------------------------------

For descriptions of the functional characteristics of these cover types, in 
terms of approximate height of mature vegetation, percent ground surface 
covered by vegetation, seasonality, and leaf type, see Table 1 in DeFries and 
Townshend  (1994a).  

8.3  Sample Data Base Data Record.

     Not applicable.

8.4  Data Format.

     The CD-ROM file format is ASCII, and consists of numerical fields of 
     varying length, which are space delimited and arranged in columns and 
     rows.  Each column contains 180 numerical values and each row contain 360 
     numerical values.  

          Grid arrangement

             ARRAY(I,J)
             I  = 1 IS CENTERED AT 179.5W
             I INCREASES EASTWARD BY 1 DEGREE
             J  = 1 IS CENTERED AT 89.5N
             J INCREASES SOUTHWARD BY 1 DEGREE

             90N - | - - - | - - - | - - - | - -
                   | (1,1) | (2,1) | (3,1) |
             89N - | - - - | - - - | - - - | - -
                   | (1,2) | (2,2) | (3,2) |
             88N - | - - - | - - - | - - - | - -
                   | (1,3) | (2,3) | (3,3) |
             87N - | - - - | - - - | - - - |
                  180W   179W    178W   177W

            ARRAY(360,180)

8.5  Related Data Sets.

     For other global land cover data sets, see  (Matthews 1983) ,  (Olson, et 
     al. 1983), (Wilson and Henderson-Sellers 1985) and vegetation 
     classification map (Dorman and Sellers 1989, Nobre et al. 1991).

                         9.  DATA MANIPULATIONS

9.1  Formulas.

     9.1.1  Derivation Techniques/Algorithms.

            Maximum likelihood classification based on 12 monthly NDVI values
            was used to obtain the global land cover data set.  In outline,
            the maximum likelihood procedure classifies each pixel to the land
            cover type that it most resembles in terms of its remotely sensed
            properties.  The remotely sensed properties are used to define a 
            multi-dimensional space within which pixels of each cover type can 
            be located. The mean vector and variance-covariance matrix for 
            each cover type are estimated using its worldwide population of 
            pixels from the training set. Then, using the maximum likelihood 
            rule (Swain and Davis 1978), the multidimensional space is 
            partitioned into sub-spaces each uniquely associated with one land 
            cover type.  The whole of the global land mass is then classified 
            according to the remotely sensed properties of each pixel.  Thus, 
            if a pixel falls within the sub-space associated  with cover type 
            ci, it is labeled ci.  If the pixel falls within the sub-space 
            associated with cover type cj, it is labeled as that cover type, 
            cj.

9.2  Data Processing Sequence.

     9.2.1  Processing Steps and Data Sets.

            To account for phasing of seasons, maximum likelihood 
            classification was based on monthly NDVI values sequenced from the 
            peak value at each pixel (see DeFries and Townshend  (1994a)  
            for more detail).

            Training sets for each of the eleven cover types were
            identified as the areas where three existing ground-based data 
            sets of global land cover (Matthews 1983, Olson, et al. 1983, 
            Wilson and Henderson-Sellers 1985) agree that the land cover is 
            present.  Although there is considerable disagreement among these 
            data sets  (DeFries and Townshend 1994b), the locations where the 
            three data sets agree were selected as those with the greatest 
            confidence that the cover type actually exists on the ground.  The 
            following steps were taken to ensure that each training set was as 
            spectrally distinct as possible or to further subdivide the 
            training set so that each would be spectrally distinct:

            1) each training set was split into Northern and Southern 
               Hemispheres to account for phasing of seasons in the two 
               hemispheres.

            2) the feature space occupied by each training set was visually
               examined.  Pixels that were obvious outliers were removed, and
               clusters were examined to determine if they were falling in 
               different geographic areas.  Where this was the case, the 
               training set was subdivided.  The most obvious example where 
               subdivision was required was cultivated crops whose spectral 
               signatures vary considerably among continents.

            3) Bhattacharrya Distances--a measure of the separability of the 
               training sets--and overlaps in the feature space were examined 
               to determine if some cover types should be combined.  This was 
               the case, for example, for Southern Hemisphere broadleaf 
               deciduous forest located mainly in Africa and Southern 
               Hemisphere wooded grassland.

     9.2.2  Processing Changes.

            Not applicable.

9.3  Calculations.

     9.3.1  Special Corrections/Adjustments.

            The global land cover data set was modified from the original 
            maximum likelihood classification result as follows to eliminate 
            stray pixels that were obviously incorrectly classified:  pixels 
            falling within training areas that were not correctly classified 
            were changed to the cover type indicated by the training area;  
            pixels surrounded on all sides by a different cover type were 
            changed to that cover type; pixels classified as broadleaf 
            evergreen in mid-latitudes were changed to the wooded grassland 
            cover type; pixels classified as coniferous evergreen within the 
            tropics were changed to the broadleaf evergreen cover type; pixels 
            classified as mixed deciduous and evergreen forest and woodland 
            within the tropics were changed to the wooded grassland cover 
            type.  In total, these changes altered approximately 10 percent of 
            the total land surface.
            
            The following modifications have been made to the global land
            cover data set by:
            
            G. James Collatz and Sietse Los, Biospheric Sciences Branch,
            Code 923, NASA/Goddard Space Flight Center, Greenbelt MD 20771.
            
            The land cover data set was further modified to be consistent with 
            the SiB vegetation classes described in Dorman and Sellers, 
            (1989), Sellers et. al. (1995a) and Sellers et. al. (1995b) in the 
            following ways:
            
            a) The Matthews (1983) vegetation map is used as the global 
               land/ocean mask except for Africa where Kuchler (1983) is used.  
            
            b) Vegetation class 8 (broad leaf shrubs and ground cover) was not 
               distinguishable from class 6 (wooded grassland) using the 
               classification methods described here so class 6 includes both 
               wooded grasslands and shrubs with groundcover understory.
               
            c) The original classification data set had 90 missing points in
               Arctic that are classified as land points in the land/ocean 
               mask.  These were set to class 11 (bare ground). Two other 
               points not classified lie in the southwestern Pacific 
               (latitudinal index, longitudinal index=94,329 and 94,330).  
               These points are set to class 1 to match an adjoining point 
               that had been classified.
               
            d) Class 6 (wooded c4 grassland) and class 7 (c4 grasslands) 
               occurring in regions with climates unfavorable for c4 grasses 
               were reclassified to class 14 (wooded c3 grassland) and class 
               15 (c3 grasslands) respectively.  The main criteria for 
               deciding whether the climate is favorable for c4 grasses are 
               that the following two conditions apply for any month at that 
               grid point: a) mean monthly temperature is above 22 degree C 
               and b) mean monthly precipitation is above 25mm.  The mean 
               monthly temperature and precipitation fields were from Leemans 
               and Cramer (1991). 

9.4  Graphs and Plots.

     See DeFries and Townshend (1994a).

                          10.  ERRORS

10.1  Sources of Error.

      Wintertime NDVI values were missing for large areas in high latitudes in 
      the primary data set used for this study  (Los, et al., 1994) .  For 
      these areas, results from a maximum likelihood classification using 
      AVHRR Pathfinder data (James and Kalluri, 1994) for summertime monthly 
      NDVI and red reflectance values were used.

10.2  Quality Assessment.

      10.2.1  Data Validation by Source.

              The data set has not been systematically validated.

      10.2.2  Confidence Level/Accuracy Judgment.

              Cursory validation indicates that the user should be aware of 
              the following problems: 

              1) the distinction between "cultivated" and "grassland" cover 
                 types may be inaccurate because the NDVI temporal profiles of 
                 these two cover types are not significantly distinct.

              2) the "tundra" cover type may be inaccurate because of missing 
                 data at high latitudes.

      10.2.3  Measurement Error for Parameters and Variables.

              Not available.

      10.2.4  Additional Quality Assessment Applied.

              None.

                             11.  NOTES

11.1  Known Problems With The Data.

      See section 10.2.

11.2  Usage Guidance.

      See section 10.2.

11.3  Other Relevant Information.

      The following two tables (Biome dependent and Biome independent
      parameters) were compiled by G. James Collatz, Code 923, NASA/GSFC,
      Greenbelt MD 20771, phone: 301-286-1425, e-mail: 
      jcollatz@biome.gsfc.nasa.gov

      Tables: Time-invariant land surface properties. These can be used in
      conjunction with the vegetation classification to specify global
      parameter fields. Most parameter fields are derived for use in the 
      Simple Biosphere model (SiB2; see Sellers et al., 1994, 1995b and 
      Sellers et al., 1995a,b and papers referenced) and may need to be 
      adapted for use in other models. (Parameters are from Sellers et al., 
      1995a,b).
______________________________________________________________________________
______________________________________________________________________________
11.3.1 Biome dependent morphological and physiological parameters.
______________________________________________________________________________

                                                   SiB Vegetation Type
Name                    Symbol    Units     1     2     3     4     5     6   
______________________________________________________________________________
Canopy top height         z_2      m       35.0  20.0  20.0  17.0  17.0  1.0

Inflection height for
   leaf area density      z_c      m       28.0  17.0  15.0  10.0  10.0  0.6
   
Canopy base height        z_1      m        1.0  11.5  10.0   8.5   8.5  0.1

Canopy cover fraction      V       -        1.0   1.0   1.0   1.0   1.0  1.0

Leaf angle distribution
   factor                 chi_l    -        0.1  0.25  0.13  0.01  0.01 -0.3
   
Leaf width                l_w      m       0.05  0.08  0.04 0.001 0.001 0.01

Leaf length               l_l      m        0.1  0.15   0.1  0.06  0.04  0.3

Total soil depth          D_t      m        3.5   2.0   2.0   2.0   2.0  1.5

Maximum rooting depth     D_r      m        1.5   1.5   1.5   1.5   1.5  1.0

1/2 inhibition water
   potential              psi_c    m       -200  -200  -200  -200  -200  -200
   
Leaf reflectance, visible,
   live                  alpha_v,l -        0.1   0.1  0.07  0.07  0.07  0.11
   
Leaf reflectance, visible,
   dead                  alpha_v,d -       0.16  0.16  0.16  0.16  0.16  0.36
   
Leaf reflectance, near IR,
   live                  alpha_n,l -       0.45  0.45   0.4  0.35  0.35  0.58
   
Leaf reflectance, near IR,
   dead                  alpha_n,d -       0.39  0.39  0.39  0.39  0.39  0.58
   
Leaf transmittance, visible,
   live                  delta_v,l -       0.05  0.05  0.05  0.05  0.05  0.07
   
Leaf transmittance, visible,
   dead                  delta_v,d -      0.001 0.001 0.001 0.001 0.001  0.22
   
Leaf transmittance, near IR,
   live                  delta_n,l -       0.25  0.25  0.15   0.1   0.1  0.25
   
Leaf transmittance, near IR,
   dead                  delta_n,d -      0.001 0.001 0.001 0.001 0.001  0.38
   
Soil reflectance, visible   a_s,n   -      0.11  0.11  0.11  0.11  0.11  0.11*

Soil reflectance, near IR  a_s,v   -      0.225 0.225 0.225 0.225 0.225 0.225*

Maximum rubisco capacity,         mol m^-2
   top leaf              V_max0    s^-1    6e-5  6e-5  6e-5  6e-5  6e-5  3e-5
   
Intrinsic quantum yield  epsilon   -       0.08  0.08  0.08  0.08  0.08  0.05

Stomatal slope factor       m      -        9.0   9.0   7.5   6.0   6.0   4.0

Minimum stomatal                  mol m^-2
   conductance              b      s^-1    0.01  0.01  0.01  0.01  0.01  0.04
   
Photosynthesis coupling
   coefficient           beta_ce   -       0.98  0.98  0.98  0.98  0.98   0.8
   
High temperature stress
   factor, photosynthesis   s_2     K        313   311   307   303   303   313
   
Low temperature stress
   factor, photosynthesis   s_4     K        288   283   281   278   278   288
   
Minimum leaf resistance**  r_min   s m^-1    80    80   100   120   120   110
   
_____________________________________________________________________________
11.3.2 Biome dependent parameters continued.
_____________________________________________________________________________
                                                   SiB Vegetation Type
 Name                    Symbol    Units     7     8     9    10    11   12  
_____________________________________________________________________________
Canopy top height         z_2      m        1.0   1.0   0.5   0.6   1.0  1.0

Inflection height for
   leaf area density      z_c      m        0.6   0.6   0.3  0.35   0.6  0.6
   
Canopy base height        z_1      m        0.1   0.1   0.1   0.1   0.1  0.1

Canopy cover fraction      V       -        1.0   1.0   0.1   1.0   1.0  1.0

Leaf angle distribution
   factor                 chi_l    -       -0.3  -0.3  0.01   0.2  -0.3 -0.3
   
Leaf width                l_w      m       0.01  0.01 0.003  0.01  0.01 0.01

Leaf length               l_l      m        0.3   0.3  0.03   0.3   0.3  0.3

Total soil depth          D_t      m        1.5   1.5   1.5   1.5   1.5  1.5

Maximum rooting depth     D_r      m        1.0   1.0   1.0   1.0   1.0  1.0

1/2 inhibition water
   potential              psi_c    m       -200  -200  -300  -200  -200 -200
   
Leaf reflectance, visible,
   live                  alpha_v,l -       0.11  0.11   0.1  0.11  0.11  0.11
   
Leaf reflectance, visible,
   dead                  alpha_v,d -       0.36  0.36  0.16  0.36  0.36  0.36
   
Leaf reflectance, near IR,
   live                  alpha_n,l -       0.58  0.58  0.45  0.58  0.58  0.58
   
Leaf reflectance, near IR,
   dead                  alpha_n,d -       0.58  0.58  0.39  0.58  0.58  0.58
   
Leaf transmittance, visible,
   live                  delta_v,l -       0.07  0.07  0.05  0.07  0.07  0.07
   
Leaf transmittance, visible,
   dead                  delta_v,d -       0.22  0.22 0.001  0.22  0.22  0.22
   
Leaf transmittance, near IR,
   live                  delta_n,l -       0.25  0.25  0.25  0.25  0.25  0.25
   
Leaf transmittance, near IR,
   dead                  delta_n,d -       0.38  0.38 0.001  0.38  0.38  0.38
   
Soil reflectance, visible   a_s,n   -       0.11* 0.15*  0.3* 0.11   0.3*  0.1

Soil reflectance, near IR  a_s,v   -      0.225* 0.25* 0.35* 0.23  0.35* 0.15

Maximum rubisco capacity,         mol m^-2
   top leaf              V_max0    s^-1    3e-5  3e-5  6e-5  6e-5  3e-5  6e-5
   
Intrinsic quantum yield  epsilon   -       0.05  0.05  0.08  0.08  0.05  0.08

Stomatal slope factor       m      -        4.0   4.0   9.0   9.0   4.0   9.0

Minimum stomatal                  mol m^-2
   conductance              b      s^-1    0.04  0.04  0.01  0.01  0.04  0.01
   
Photosynthesis coupling
   coefficient           beta_ce   -        0.8   0.8  0.98  0.98   0.8  0.98
   
High temperature stress
   factor, photosynthesis   s_2     K        313   313   313   303   313   308
   
Low temperature stress
   factor, photosynthesis   s_4     K        288   288   288   278   288   281
   
Minimum leaf resistance**  r_min   s m^-1   110   110    80    80   110    80

_____________________________________________________________________________

*Soil reflectance for areas with bare soil are specified according to ERBE
data which is available elsewhere on this CD ROM.

**Minimum leaf resistance is the light saturated, unstressed resistance to 
water vapor diffusion through the leaf surface.  It is calculated using table 
values of V_max and m and the photosynthesis and stomatal models described in
Collatz et. al. 1991, Agric. For. Meteor., 54:107-136.  The total canopy 
resistance can be calculated using the minimum leaf resistance scaled by 
environmental conditions and integrated over all the leaves in the canopy.  
A simple way to perform the integration would be to multiply the environment-
modified minimum leaf resistance by the leaf area index (LAI) or by the 
fraction of incident PAR that is absorbed by the canopy (FPAR).  Global fields
of LAI and FPAR are available elsewhere on this CD-ROM.
     
______________________________________________________________________________
     Biome independent parameters
______________________________________________________________________________
     Name                                        symbol    units       value
______________________________________________________________________________
     Ground roughness length                       z_s       m          0.05
     
     Augmentation factor for momentum              G_1       -          1.449
     
     Transition height factor for momentum         G_4       -         11.785
     
     Depth of surface soil layer                   D_1       m          0.02
     
     Rubisco Michaels-Menten constant for CO2      K_c       Pa      30*2.1^Qt
     
     Rubisco inhibition constant for oxygen        K_o       Pa  30,000*1.2^Qt
     
     Rubisco specificity for CO2 relative to       S         -   2,600*0.57^Qt
     oxygen
     
     Q10 temperature coefficient                   Qt        -      (T-298)/10
     
     Photosynthesis coupling coefficient           beta_ps   -           0.95
     
     High temperature stress factor, photosynthesis s_1       K^-1        0.3
     
     Low temperature stress factor, photosynthesis  s_3       K^-1        0.2
     
     High temperature stress factor, respiration    s_5       K^-1        1.3
     
     High temperature stress factor, respiration    s_6       K           328
     
     Leaf respiration factor                       f_d       -           0.015
______________________________________________________________________________
______________________________________________________________________________

                           12.  REFERENCES

12.1  Satellite/Instrument/Data Processing Documentation.

      None.

12.2  Journal Articles and Study Reports.

      DeFries, R. S. and J. R. G. Townshend, 1994a, NDVI-derived land 
           cover classification at global scales. International Journal of 
           Remote Sensing, 15:3567-3586. Special Issue on Global Data Sets.
      DeFries, R. S. and J. R. G. Townshend, 1994b. Global land cover:
           comparison of ground-based data sets to classifications with AVHRR 
           data. In Environmental Remote Sensing from Regional to Global 
           Scales, edited by G. Foody and P. Curran, Environmental Remote 
           Sensing from Regional to Global Scales. (U.K.: John Wiley and 
           Sons).
      James, M. E. and S. N. V. Kalluri, 1994. The Pathfinder AVHRR land 
           data set: An improved coarse resolution data set for terrestrial 
           monitoring. International Journal of Remote Sensing,  Special Issue 
           on Global Data Sets. 15(17):3347-3363.
      Kuchler, A.W., 1983,  World map of natural vegetation.  Goode's World 
           Atlas, 16th ed., Rand McNally, 16-17. 
      Leemans, R., and W. P. Cramer, 1991, The IIASA database for mean monthly
           values of temperature, precipitation and cloudiness on a global
           terrestrial grid, technical report, International Institute for
           Applied Systems Analysis, Laxenburg, Austria.
      Los, S.O.,  C.O. Justice, C.J. Tucker, 1994. A global 1 by 1 degree NDVI 
           data set for climate studies derived from the GIMMS continental 
           NDVI data. International Journal of Remote Sensing, 15(17):3493-
           3518. 
      Matthews, E., 1983. Global vegetation and land use: new high resolution 
           data bases for climate studies. Journal of Climate and Applied 
           Meteorology, 22: 474-487.
      Olson, J. S., Watts, J. and L. Allison, 1983. Carbon in live vegetation 
           of major world ecosystems. W-7405-ENG-26, U.S. Department of 
           Energy, Oak Ridge National Laboratory.
      Sellers, P.J., S.O. Los, C.J. Tucker, C.O. Justice, D.A. Dazlich, G.J. 
           Collatz, and D.A. Randall, 1994. A global 1*1 degree NDVI data set 
           for climate studies. Part 2: The generation of global fields of 
           terrestrial biophysical parameters from the NDVI. International 
           Journal of Remote Sensing, 15(17):3519-3545.
      Sellers, P.J., D.A. Randall, C.J. Collatz, J.A. Berry, C.B. Field, D.A. 
          Dazlich, C. Zhang, and C.D. Collelo, 1995a. A revised land surface 
          parameterization (SiB2) for atmospheric GCMs. Part 1: Model 
          formulation. submitted to Journal of Climate.
      Sellers, P.J., S.O. Los, C.J. Tucker, C.O. Justice, D.A. Dazlich, G.J. 
         Collatz, and D.A. Randall, 1995b. A revised land surface 
         parameterization (SiB2) for atmospheric GCMs. Part 2: The generation 
         of global fields of terrestrial biophysical parameters from satellite 
         data. submitted to Journal of Climate.
      Swain, P. H. and S. M. Davis, (ed.), 1978. Remote Sensing: The 
           Quantitative Approach. (New York: McGraw-Hill Book Company).
      Wilson, M. F. and A. Henderson-Sellers, 1985. A global archive of land 
           cover and soils data for use in general circulation models. Journal 
           of Climatology, 5: 119-143.
 
12.3  Archive/DBMS Usage Documentation.

      Contact the EOS Distributed Active Archive Center (DAAC) at NASA Goddard 
      Space Flight Center (GSFC), Greenbelt Maryland (see Section 13 below).
      Documentation about using the archive or information about access to the 
      on-line information system is available through the GSFC DAAC User 
      Services Office.

                             13.  DATA ACCESS

13.1  Contacts for Archive/Data Access Information.

      GSFC DAAC User Services
      NASA/Goddard Space Flight Center
      Code 902.2
      Greenbelt, MD 20771

      Phone:     (301) 286-3209
      Fax:       (301) 286-1775
      Internet:  daacuso@eosdata.gsfc.nasa.gov

13.2  Archive Identification.

      Goddard Distributed Active Archive Center
      NASA Goddard Space Flight Center
      Code 902.2
      Greenbelt, MD 20771

      Telephone:  (301) 286-3209
      FAX:        (301) 286-1775
      Internet:   daacuso@eosdata.gsfc.nasa.gov

13.3  Procedures for Obtaining Data.

      Users may place requests by accessing the on-line system, by sending 
      letters, electronic mail, FAX, telephone, or personal visit.

      Accessing the GSFC DAAC Online System:

      The GSFC DAAC Information Management System (IMS) allows users to 
      ordering data sets stored on-line.  The system is open to the public.

      Access Instructions:

      Node name:  daac.gsfc.nasa.gov
      Node number: 192.107.190.139
      Login example: telnet daac.gsfc.nasa.gov
      Username:  daacims
      password:  gsfcdaac

      You will be asked to register your name and address during your first
      session.

      Ordering CD-ROMs:

      To order CD-ROMs (available through the Goddard DAAC) users should 
      contact the Goddard DAAC User Support Office (see section 13.2).

13.4  GSFC DAAC Status/Plans.

      The ISLSCP Initiative I CD-ROM is available from the Goddard DAAC.

                   14.  OUTPUT PRODUCTS AND AVAILABILITY

14.1  Tape Products.

      None.

14.2  Film Products.

      None.

14.3  Other Products.

      None.

                       15.  GLOSSARY OF ACRONYMS

AVHRR          Advanced Very High Resolution Radiometer
CD-ROM         Compact Disk (optical), Read Only Memory
DAAC           Distributed Active Archive Center
EOS            Earth Observing System
GCM            General Circulation Model of the atmosphere
GSFC           Goddard Space Flight Center
IDS            Inter-disciplinary Science
ISLSCP         International Satellite Land Surface Climatology Project
NASA           National Aeronautics and Space Administration
NDVI           Normalized Difference Vegetation Index