The International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences. Vol. XXXVII. Part B4. Beijing 2008
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CONTAG
X X
(p.) /“
X*.
z*.
2 In m
Where m = number of patch types (classes)
Pi = proportion of the landscape occupied by patch
type (class) i,
g ik = number of adjacencies (joins) between pixels of
patch types (classes) i and k.
• Shannon diversity index (SHDI)
m
SHDI = Y,(Pi xLn P) (7)
i=i
Where Pi = proportion of the landscape occupied by patch
type (class) i.
• Modified Simpson's diversity index (MSIDI)
MSID1 = -\r\Yj P i 2 (8)
/=1
Where Pi = proportion of the landscape occupied by patch
type (class) i.
• Shannon evenness index (SHEI)
m
YjPi xLn Pi
SHEI = - (9)
Lnm
Where Pi = proportion of the landscape occupied by patch
type (class i)
m is number of patch types (classes).
• Modified Simpson's evenness index (MSIEI)
m
-InX-ff
MSIEI = (10)
In m
Where Pi = proportion of the landscape occupied by patch
type (class i)
m is number of patch types (classes)
Landscape index
year
Grass land
Farmland
Construction land
Woodland
Water land
Unused land
Landscape
1977
0.0604
0.0171
0.0024
0.0491
0.0036
0.0412
0.1738
PD
1996
0.0751
0.1134
0.1073
0.0598
0.0041
0.0551
0.4148
2000
0.0765
0.1148
0.0994
0.0596
0.0037
0.0591
0.413
2006
0.0949
0.1013
0.0662
0.0635
0.0107
0.0675
0.404
1977
1032.3618
1224.1253
36.0503
116.5965
968.9796
181.0381
575.4012
MPS
1996
830.9357
166.1222
10.3887
99.7627
917.0495
143.7226
241.0636
2000
812.8416
165.1289
10.3396
99.3936
1274.8394
121.988
242.113
2006
624.8233
201.6722
11.4228
102.2128
475.3234
117.8512
247.5038
1977
9.9399
3.8337
0.057
3.5426
1.8848
3.7504
11.5042
ED
1996
20.9804
14.295
1.6763
4.9309
2.1573
5.0372
24.5386
2000
21.0998
14.1118
1.532
4.8889
2.2434
5.0225
24.4492
2006
19.9437
12.6308
1.0374
4.581
2.1944
5.0391
22.7132
1977
40.0701
25.5219
5.7009
47.521
29.7752
41.1095
37.7611
LSI
1996
79.1217
97.8841
46.8301
63.0677
32.7915
53.5884
76.1448
2000
81.1646
96.3921
44.5822
62.8039
30.5859
56.0493
75.9063
2006
81.7104
83.3806
35.2884
56.7011
28.7456
53.4477
70.7972
1977
34.8372
6.6973
0.0418
0.6008
1.2417
1.9997
34.8372
LPI
1996
9.1917
2.6185
0.0593
0.4186
1.9565
2.6494
9.1917
2000
11.4713
2.0707
0.0559
0.417
3.2208
1.8083
11.4713
2006
16.9765
2.0745
0.0557
0.9659
2.6392
2.604
16.9765
Table 2 Landscape pattern index in areas of cascade hydropower station construction
The computed results of those indices are listed in Table 2. For
the construction of cascade hydropower station, the original
natural ecosystem was affected. The patch density of the
grassland, farmland, woodland, water area and unused land
increased steadily while the mean patch size decreased
correspondingly, which accounted for fragmentation of these
landscape types. The PD of the construction land dropped in the
last ten years while the MPS went up recently, which indicated
the ascending trend of connectivity and integrity of construction
land. The Largest Patch Index (LPI) of water area has climbed
rapidly, but as for the Mean Patch Size (MPS) of grassland, it
has shown a decreasing tread, it can be explained that as the
grassland patches were extensively distributed in the landscape
around the water area, the rising of the water level because of
the construction of the cascade hydropower station contributed
to the fragmentation of the grassland. The LPI provided the
information about the role the largest patch played in the total
patches of the same land use. For the landscape change, the LPI
of the water area, construction land, woodland and unused land
climbed. The calculated LSI in the table did not fluctuate
obviously, which suggested the reservoir construction did not
change the patch shape intensively.
Year
CONTAG
SHDI
MSIDI
SHEI
MSIEI
1977
66.4342
1.1025
0.8157
0.6153
0.4553
1996
62.623
1.1515
0.8298
0.6427
0.4631
2000
62.4593
1.158
0.8351
0.6463
0.4661
2006
61.5337
1.2013
0.9001
0.6705
0.5024
Table 3 Index comparisons of landscape diversity structure
According to reviews of the regional landscape evolution, the
Contagion Index (CONTAG) presents a declining trend while
the landscape diversity indexes such as Shannon's Diversity
Index (SHDI) rises, which implies that regional landscape
patches turn to be more fragmented and the landscape had a
trend of diversity and regularity surrounding the hydropower
station field. The increased SHDI meant the diversity degree of
each land use climbed up and centralized. The calculation of the