Chapter 4 Morphometric Analysis -...
Transcript of Chapter 4 Morphometric Analysis -...
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Chapter 4 : Morphometric Analysis
4.1 Introduction
Geology, geomorphology, structure and drainage patterns especially in hard
rock terrains are the primary determinants of river ecosystem functioning at the
basin scale (Lotspeich and Plats; Frissel et al., 1986). Morphometric descriptions
represent relatively simple approach to describe basin processes and to compare
basin characteristics. Anthropogenic changes have led to widespread modifications
in physical structure of rivers, biotic communities and ecological functioning of
aquatic ecosystems around the world (Thomson et al., 2001).
Understanding the drainage pattern of an area gives a perspective view of the
topography of the area which helps in the planning and development of water sheds
and also provides an indication of the potential zones for obtaining ground water.
Morphometric techniques are applied for interpretation of salient features of
drainage networks. It incorporates a quantitative study of the area, its altitude,
volume, slope, profiles of land and the drainage basin characteristics of the
concerned area (Singh, 1977).
It was the year 1932 when drainage basin attracted the attention of Horton,
an American engineer, who first of all presented an elaborate account of drainage
basin characteristics and in 1945 he acknowledged the drainage basin as a
morphometric system wherein he applied morphometric techniques vigorously for
interpretation of silent features of drainage network. In fact after the classical work
of Horton in 1945, drainage basin attracted attention of a large number of
geomorphologists, engineers and hydrologists, who accepted the drainage network
and the basin as a dynamic rather than static unit. Consequently significant
contribution in the field of drainage basin study came from Miller (1953); Schumm
(1956); Chorley (1967); Strahler (1957); Melton (1959); Morgon (1962); Gregory and
Walling (1973).
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The morphometric analysis using remote sensing and GIS techniques has
been well attempted by Srivastava and Mitra (1995); Srivastava (1997); Singh and
Singh (1997); Nag (1998); Srinivasa Vittala et al.; (2004) and Nilufer Arshad and G.S.
Gopalakrishna (2008) and all have arrived to the conclusion that remote sensing
technique and GIS have emerged as a powerful tools in the recent years. Satellite
remote sensing has the ability of obtaining synoptic view of large area at a time and
very useful in analyzing the drainage morphometry.
4.2 Data used and Methodology
For carrying out morphometric analysis, hydrological boundary is taken into
consideration rather than the geographical boundary of the study area. Hence, the
Lakshmantirtha River basin was chosen for the present work and not the Hunsur
Taluk. The map showing the drainage pattern of the entire Lakshmantirtha river
basin has been prepared based on the Survey of India (SOI) toposheets and the
drainage pattern has been updated by using the satellite imageries of LISS plus PAN
merged data of 2001. The satellite images used for this study have been taken from
Karnataka State Remote sensing Application Centre. These satellite images and the
SOI toposheets have been geo‐referenced and merged using Image Processing
software ERDAS IMAGINE (V 9.1), (ERDAS, 2001).
The drainages have been delineated using merged satellite data of Geocoded
FCC of bands ‐ 2 3 4 on 1:50,000 scale and SOI toposheets bearing number 57D/3,
57D/4, 57D/7, 57D/8, 48P/15, 48P/16 and 58A/1 have been used as a reference.
Ground truth checks have been made during the field visits (Fig. 4.1). AutoDesk
software like Auto CAD Map 2000 and ArcGIS softwares like Arcmap (v.9.1) and
ArcView (v.3.2a) have been used for digitization and computational purpose and also
for output generation (ESRI ArcGIS, 2001). The morphometric analysis can be
achieved through measurement of linear, aerial and relief aspects of basin and slope
contributions (Nag and Chakraborty, 2003). Factor analysis also has been applied on
the morphometric parameters and has grouped them into different factors and their
association with one another has been discussed in detail in the following sections.
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Figure 4.1: Drainage pattern of Lakshmantirtha basin
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4.3 Morphometric Analysis
Following the digitization of the drainage pattern of the Lakshmantirtha
basin, morphometric analysis was carried out for the whole basin and subsequently
for the 26 watersheds which were demarcated according to the water divider (Fig.
4.2). The linear, relief and aerial aspects of the each watershed has been described
and interpreted. The linear aspect treats with unidimensional, while relief and aerial
aspects describes two dimensional and three dimensional characteristics
respectively. The new drainages updated from the satellite Imagery have also been
taken into consideration for measurement of these aspects of the study area. In this
study the linear, aerial and relief aspects have been grouped into five categories: 1)
basic parameters, 2) derived parameters, 3) shape parameters 4) dissection intensity
parameters and 5) relief parameters. All the parameters have been discussed in
detail.
4.3.1 Basic Parameters
4.3.1.1 Area (A)
This is one of the most important physical characteristics, because it directly
affects the size of the hydrographs and magnitude of runoff. The total drainage area
of the Lakshmantirtha basin is 1582 sq.km, and the area of each of the watersheds
are shown in the Table 4.1. Watershed 12 is the smallest (A < 8.683 sq.km) and
watershed 18 is the biggest (A> 346.9 sq.km), (Table 4.1).
4.3.1.2 Perimeter (B)
The perimeter is the total length of the drainage basin boundary. It is the
total length along the water divide of the basin. The perimeter (P) is a linear measure
of the size of the basin and it is largely dependent on the texture of the topography.
The perimeter of the basin is 249 km, and the perimeter of the 26 watersheds is
shown in Table 4.1. Watershed 12 has the smallest perimeter (P< 14.28) and the
watershed 18 has the largest perimeter (P> 81.8) and coincides with highest value of
A in the same watersheds, (Table 4.1).
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Figure 4.2: Watershed boundary of Lakshmantirtha sub‐basin
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4.3.1.3 Basin Length (L)
Basin length has been given different meanings by different workers
(Schumm 1956; Gregory and Walling 1973; Gardiner 1975 and Cannon 1976).
According to Gregory and Walling (1973), the L is the longest length of the basin,
from the catchment to the point of confluence. The basin length also corresponds to
the maximum length of the basin and watershed measured parallel to the main
drainage line. The length of the Lakshmantirtha basin is 72 km and the values of L for
the 26 watersheds are shown in the Table 4.1. Watershed 18 is the longest
watershed (L> 28.5 km) while watershed 26 has the minimum value of L (L< 2.78 km),
(Table 4.1).
4.3.1.4 Stream Order (Nu):
The designation of stream orders is the first step in drainage basin analysis
and is based on a hierarchic ranking of streams. There are different methods to
indicate the order of a stream network. Horton (1945) designated a stream without
any tributaries as the first order stream. However, each second order stream is
considered to extend headwords to the tip of the longest tributary. The third order
receives second and first order channels as its tributaries and so on. Strahler (1952)
gave a modified definition and considered each fingertip channel as of first order.
The second order stream commences from the point where two first order channels
meet and continues down to the intersection of two second order streams for which
point a third order stream commences and so on. The modified method proposed by
Strahler (1964) is widely accepted and is the most popular system in classifying the
channels into orders.
In the present study, ranking of streams has been carried out based on the
method proposed by Strahler (1964) which is popularly known as Stream Segment
Method. The order wise stream numbers for all 26 watersheds are given in Table 4.1.
Out of these watersheds, watersheds 25 and 26 belong 20 second order, watershed
6,7,10, 12, 14, 15, 16, 17 and 20 belong to the third order streams, watersheds 1, 4,
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7, 9, 11, 13, 21, 22, 23 and 24 are of fourth order streams and the remaining
watersheds( 2, 3, 5, 18 and 19) are of fifth order streams.
Lakshmantirtha basin is designated as a sixth order stream. The details of
stream characteristics confirm with Horton’s first law (1945) of stream numbers,
which states that the numbers of different orders in a given drainage basin tends
closely to approximate an inverse geometric ratio. This means that there is a
negative correlation between the stream order and stream number. This can be seen
clearly in the linear regression graph where an almost straight line is formed when
log values of stream numbers are plotted against stream order (Fig. 4.3).
4.3.1.5 Stream length (Lu)
The number of streams of various orders in the basin and watersheds are
counted and their lengths from mouth to drainage divide are measured with the help
of GIS softwares. In the present study, stream length (Lu) has been computed based
on the law proposed by Horton (1945) for all the 26 watersheds and presented
(Table 4.1). Generally, the total length of stream segments is in maximum in first
order streams and decreases as the stream order increases. In Fig. 4.3 it can be seen
that there is a negative correlation between the stream lenght and stream order
when regression line is fitted. This observation is on the basis of Horton's law of
stream numbers (1932) which has received verification by accumulated data from
many localities (Strahler 1952; Schumm 1956; Smith 1958; Melton 1958). However
there is a sudden increase in length of streams of order III in (watersheds 13 and 4),
order IV ( watersheds 1, 5, 6, 7 and 11) and stream order V (in watershed 18), which
could be due to variation in relief over which the segments occur. This change may
indicate flowing of streams from high altitude, lithological variation and moderately
steep slopes as proposed by Singh and Singh (1997). Mostly all streams rise from the
hilly terrains. It is noticed that stream segments up to the 3rd order traverse the high
altitudes zones, which are mainly characterized by steep slopes, while the 4th, 5th and
6th order stream segments occur in comparatively plain land.
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Watershed/ Stream Stream Order Stream LengthPerimeter Area
Basin
I II III IV V VI I II III IV V
1 IV 93 24 5 1 0 0 58.32 31.711 12.09 10.75 0 43.36 69.71 14.8
2 V 165 43 8 2 1 0 113.10 40.78 21.27 21.84 18.86 73.7 139.5 20.78
3 V 165 34 10 3 1 0 109.02 38.8 23.37 9.54 12.86 61.91 116.4 22.5
4 IV 45 14 2 1 0 0 26.87 19.33 7.62 2.04 0 37.42 42.25 8
5 V 119 31 7 2 1 0 88.95 36.19 11.39 19.78 9.94 53.71 120.6 18.1
6 III 11 4 1 0 0 0 10.34 3.816 4 0 0 23.72 17.21 6.4
7 IV 69 17 2 1 0 0 59.05 21.8 8.3 15.81 0 44.15 70.95 18.41
8 III 28 6 2 0 0 0 20.09 5.38 3.12 33.94 26.13 5.7
9 IV 53 12 3 1 0 0 42.50 34.93 9.49 9.5 0 44.5 70.75 15
10 III 18 5 1 0 0 11.59 9.65 1 34.16 23.84 10.4
11 IV 24 8 2 1 0 0 14.25 5.46 1.03 7.18 20.03 18.27 7.74
12 III 14 4 1 0 0 0 8.54 4.99 0.56 0 0 14.28 8.683 4.24
13 IV 28 6 3 1 0 0 17.95 4.72 7.89 2.09 0 19.43 20.53 5.56
14 III 23 6 1 0 0 0 15.39 4.23 4.1 0 0 14.63 10.53 5.27
15 III 22 5 1 0 0 0 12.35 5.25 4.62 0 0 14.55 11.31 4.84
16 III 17 4 1 0 0 0 12.28 8.08 3.69 0 0 18.56 15.83 4.5
17 III 26 7 1 0 0 0 17.51 6.16 2.25 0 0 37.97 28.47 9.15
18 V 239 59 19 5 1 0 162.77 91.14 38.05 16.74 25.74 81.8 346.9 28.5
19 V 196 41 11 3 1 0 122.62 45.36 19.65 13.42 10.12 66.44 163.9 24.2
20 III 25 6 1 0 0 0 17.21 6.59 3.40 0 0 20.18 20.13 5.2
21 IV 48 11 3 1 0 0 31.91 18.81 10.51 1.79 0 26.37 43.27 9.6
22 IV 77 15 4 1 0 0 52.95 17.98 12.27 1.67 0 43.47 54.05 7.11
23 IV 55 12 5 1 0 0 35.53 12.96 10.72 0.66 0 53.11 53 6
24 IV 54 10 4 1 0 0 42.71 9.34 12.43 2.33 0 45.61 52.07 10.5
25 II 13 5 0 0 0 0 9.08 1.1 0 0 0 22.67 11.20 3.3
26 II 6 2 0 0 0 0 4.32 2.46 0 0 0 24.28 13.08 2.78
Basin VI 1642 393 94 25 5 1 1112 460.407 222.14 133.898 77.54 249 1582 72 Table 4.1: Basic parameters
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y = ‐0.638x + 3.8747R² = 0.9989
y = ‐0.218x + 3.108R² = 0.8796
0
0.5
1
1.5
2
2.5
3
3.5
0
0.5
1
1.5
2
2.5
3
3.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Lakshmantirtha Basin
Stream Number Stream Length
y = ‐0.5317x + 2.4047R² = 0.945
y = ‐0.4001x + 2.2766R² = 0.8815
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 1
Stream Number Stream Lenght
y = ‐0.5767x + 2.7412R² = 0.9839
y = ‐0.1827x + 2.0695R² = 0.7909
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 2
Stream Number Stream Lenght
y = ‐0.5489x + 2.692R² = 0.9952
y = ‐0.2465x + 2.1564R² = 0.865
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 3
Stream Number Stream Lenght
y = ‐0.436x + 1.9158R² = 0.8967
y = ‐0.3773x + 1.9062R² = 0.9668
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 4
Stream Number Stream Lenght
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y = ‐0.5341x + 2.545R² = 0.9858
y = ‐0.2166x + 2.0214R² = 0.7647
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 5
Stream Number Stream Lenght
y = ‐0.2685x + 1.1341R² = 0.7949
y = ‐0.2611x + 1.2231R² = 0.8926
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 6
Stream Number Stream Lenght
y = ‐0.4908x + 2.1465R² = 0.8876
y = ‐0.3682x + 2.1501R² = 0.7769
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 7
Stream Number Stream Lenght
y = ‐0.3672x + 1.607R² = 0.8909
y = ‐0.3337x + 1.5071R² = 0.9295
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 8
Stream Number Stream Lenght
y = ‐0.4528x + 2.0144R² = 0.9264
y = ‐0.3822x + 2.1721R² = 0.8657
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 9
Stream Number Stream Lenght
y = ‐0.321x + 1.3537R² = 0.7921
y = ‐0.3113x + 1.3438R² = 0.7676
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 10
Stream Number Stream Lenght
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y = ‐0.3664x + 1.6159R² = 0.9097
y = ‐0.2189x + 1.2091R² = 0.4425
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 11
Stream Number Stream Lenght
y = ‐0.2894x + 1.2179R² = 0.7867
y = ‐0.2561x + 1.0944R² = 0.7961
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 12
Stream Number Stream Lenght
y = ‐0.3672x + 1.6422R² = 0.9195
y = ‐0.2863x + 1.4881R² = 0.8574
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 13
Stream Number Stream Lenght
y = ‐0.3502x + 1.4785R² = 0.7941
y = ‐0.3002x + 1.386R² = 0.9009
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 14
Stream Number Stream Lenght
y = ‐0.3384x + 1.4234R² = 0.7858
y = ‐0.2904x + 1.3667R² = 0.9106
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 15
Stream Number Stream Lenght
y = ‐0.3063x + 1.2854R² = 0.7787
y = ‐0.3087x + 1.4388R² = 0.9365
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 16
Stream Number Stream Lenght
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y = ‐0.3675x + 1.5545R² = 0.7969
y = ‐0.3276x + 1.4601R² = 0.929
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 17
Stream Number Stream Lenght
y = ‐0.5829x + 2.974R² = 0.9967
y = ‐0.2338x + 2.3786R² = 0.8391
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 18
Stream Number Stream Lenght
y = ‐0.572x + 2.8008R² = 0.9962
y = ‐0.2695x + 2.2429R² = 0.937
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 19
Stream Number Stream Lenght
y = ‐0.3574x + 1.5074R² = 0.7921
y = ‐0.3291x + 1.5047R² = 0.9476
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 20
Stream Number Stream Lenght
y = ‐0.4404x + 1.9611R² = 0.9275
y = ‐0.4029x + 2.0194R² = 0.9504
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 21
Stream Number Stream Lenght
y = ‐0.4949x + 2.2177R² = 0.9354
y = ‐0.448x + 2.2021R² = 0.9555
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 22
Stream Number Stream Lenght
70
Figure 4.3: Geometric relationship between stream order, stream number and stream length
4.3.2 Derived parameters
4.3.2.1 Stream length ratio
Stream length ratio (RL) may be defined as the ratio of the mean length of the
one order to the next lower order of stream segment.
Where, RL = Stream Length Ratio
Lu = Total stream length of the order 'u'
y = ‐0.456x + 2.0717R² = 0.9425
y = ‐0.4214x + 2.0029R² = 0.8989
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 23
Stream Number Stream Lenght
y = ‐0.4465x + 2.0063R² = 0.9315
y = ‐0.3863x + 1.9717R² = 0.9149
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 24
Stream Number Stream Lenght
y = ‐0.2927x + 1.2406R² = 0.799
y = ‐0.2239x + 0.9278R² = 0.722
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 25
Stream Number Stream Lenght
y = ‐0.1857x + 0.773R² = 0.7447
y = ‐0.1664x + 0.705R² = 0.7985
0
0.5
1
1.5
2
2.5
0
0.5
1
1.5
2
2.5
0 1 2 3 4 5 6 7
Stream
lenght
Stream
number
Stream order
Watershed 26
Stream Number Stream Lenght
71
Lu – 1 = Total stream length of its next lower order to the next lower order of
stream segment.
Horton's law (1945) of stream length states that mean stream length
segments of each successive orders of a basin tends to approximate a direct
geometric series with streams length increasing towards higher order of streams.
The RL between streams of different order in the study area reveals that there is a
variation in RL in each watershed (Table 4.2). This variation might be due to changes
in slope and topography. The stream length ratio of the sub‐basin reveals that the
values are different for different watersheds and are changing haphazardly from 1.70
to 6.322. The RL variation can be attributed to differences in slope and topographic
conditions and has a relationship with surface flow discharge and erosional stage of
basin (Sreedevi et al., 2004). The same kind of condition too was observed in the
study area. This change could also be attributed to the late youth or medium stage of
geomorphic development (Singh and Singh, 1977).
4.3.2.2 Stream Frequency (Fs)
Horton (1932) introduced stream frequency (Fs) or channel frequency which
is the total number of stream segments of all orders per unit area. Hypothetically, it
is possible to have the basin of same drainage density differing in stream frequency
and basins of same stream frequency differing in drainage density. Table 4.2 shows
Fs for all the watersheds of the study area.
Fs = Nu / A.
Where, Fs = Stream Frequency
Nu = Total number of streams of all orders
A = Area of the Basin (Sq.Km)
72
4.3.2.3 Bifurcation ratio (Rb)
The term bifurcation ratio (Rb) may be defined as the ratio of the number of
the stream segments of given order to the number of segments of the next higher
order (Schumn, 1956). Horton (1945) considered the bifurcation ratio as an index of
relief and dissections. Strahler (1957) demonstrated that bifurcation ratio shows a
small range of variation for different regions or for different environment except
where the powerful geological control dominates.
Rb = Nu/Nu+1
Where, Rb = Bifurcation Ratio
Nu = Total number of stream segments of order 'u'
Nu + 1 = Number of segments of the next higher order
It is observed from Table 4.2 that the Rb is not same from one order to its next
higher order. According to Strahler, 1964 these irregularities are dependent upon the
geological and lithological development of the drainage basin.
Bifurcation ratio is a dimensional parameter indication of branching pattern
of a drainage network. The Rb for the basin is 4.42 and the values of all the
watersheds vary from 2.60‐5.0. The lower values of Rb are characteristics of the
watersheds which have suffered less structural disturbances (Strahler, 1964 and Nag,
1998).
4.3.2.4 RHO coefficient (RHO)
Horton (1945) defined this parameter as the ratio between the stream length
ratio and bifurcation ratio. It can be calculated from the following formula:
Where, RI: Mean Stream Length Ratio
73
Rb: Mean Bifurcation Ratio
Horton (1945) stated that by calculating this value one could estimate how
much water will be lost as runoff during flood period and also determine the amount
of water which could be stored in a basin showing the drainage capacity of a basin.
RHO is influenced by many external parameters like climate, anthropogenic factors
and also by the geologic and geomorphologic conditions of the terrain. The value of
RHO for the Lakshmantirtha basin is 0.38 and for the watersheds it varies from 0.370‐
1.686 (Table 4.2). Watershed 10, 11, 12 AND 23 show higher values than the other
watersheds and there is a possibility that that they have higher hydric storage during
flood period and attenuate the erosion effects during elevated discharge.
4.3.3 Shape parameters
4.3.3.1 Elongation ratio
Elongation ratio (Re) is the ratio between diameters of a circle of the same
area to the basin length (L) (Schumm, 1956).
1.128√ / ,
Where, Re = Elongation Ratio
A = Area of the Basin (Sq.Km)
Pi = 'Pi' value i.e., 3.14
Lb = Basin length
A circular basin is more efficient in the discharge of run‐off than an elongated
basin (Singh and Singh, 1997). The values of Re generally vary from 0.6 to 1.0 over a
wide variety of climatic and geologic types. Values close to 1.0 are typical of regions
of very low relief, whereas values in the range 0.6 ‐ 0.8 are usually associated with
high relief and steep ground slope (Strahler, 1964).
The Re of watersheds of the study area varies from 0.51–1.46 (Table 4.3). The
low values of Re in case of watersheds which their values are between 0.6‐0.8, reveal
74
an elongated shape and indicate higher relief and steep slope. The Value of Re for
the whole basin too is 0.62 which indicates an elongated shape. While very high Re
values 0.8 ‐1.0 and greater than 1, indicates that plain land with low relief and low
slope which are seen more on eastern part of the basin which the terrain is more or
less flat.
4.3.3.2 Circularity index (Rc)
According to (Miller, 1953 and Strahler 1964,) the circularity index is defined
as the ratio of basin area (A) and the area of a circle with the same parameter as that
of the basin. It is calculated from the following formula:
Rc = 4 * ∏ * A / P²
Where, Rc = Circularity Ratio
∏ = 'Pi' value i.e., 3.14
A = Area of the Basin (Sq.Km)
P² = Square of the Perimeter (Km)
The circularity ratio (Rc) is influenced by the length and frequency of streams,
geological structures, land use/land cover, climate, relief and slope of the basin.
The Rc of Lakshmantirtha basin is 0.32 while the Rc calculated for its 26
watersheds are shown in Table 4.3. The value of Rc of Lakshmantirtha basin clearly
shows lack of circularity in shape. This is because the value is less than 0.5. Almost all
the watersheds are showing values less than 0.5, which indicates an elongated
shape, while the watersheds 12, 13, 14, 20 and 21 are more or less circular in shape.
75
Watersheds Elongation ratio Circularity Ratio Form factor
W1 0.64 0.47 0.32
W2 0.64 0.32 0.32
w3 0.54 0.38 0.23
w4 0.86 0.44 0.72
W5 0.68 0.45 0.75
w6 0.73 0.38 0.42
w7 0.52 0.46 0.21
w8 1.01 0.28 0.80
w9 0.63 0.45 0.31
w10 0.53 0.26 0.22
w11 0.62 0.57 0.30
w12 0.78 0.53 0.48
w13 0.92 0.68 0.66
w14 0.69 0.62 0.38
w15 0.78 0.42 0.83
w16 1.00 0.48 0.78
w17 0.66 0.25 0.34
w18 0.74 0.48 0.43
w19 0.60 0.47 0.28
w20 0.97 0.62 0.74
w21 0.77 0.78 0.47
w22 1.17 0.36 0.37
w23 1.37 0.25 0.43
w24 0.78 0.31 0.47
W25 0.62 0.32 0.30
W26 0.64 0.47 0.32
basin 0.64 0.32 0.32
Table 4.2: Shape parameters
76
Watershed/ Elongation ratio Stream Length Ratio Mean Stream Length ratio
FS RHOBasin Rb1 Rb2 Rb3 Rb4 Rb5 Mean Rb I II III IV VW1 3.88 4.80 5.00 ‐ ‐ 4.56 1.84 2.62 1.12 ‐ ‐ 1.86 1.76 0.41
W2 3.84 5.38 4.00 2.00 ‐ 3.80 2.77 1.92 0.97 1.16 ‐ 1.70 1.57 0.45
W3 4.85 3.40 3.33 3.00 ‐ 3.65 2.81 1.92 2.45 0.74 ‐ 1.98 1.83 0.54
W4 3.23 6.50 2.00 ‐ ‐ 3.91 1.36 2.45 3.72 ‐ ‐ 2.51 1.55 0.64
W5 3.84 4.43 3.50 2.00 ‐ 3.44 2.46 3.18 0.58 1.99 ‐ 2.05 1.33 0.60
W6 2.75 4.00 ‐ ‐ ‐ 3.38 2.71 0.95 ‐ ‐ ‐ 1.83 0.93 0.54
W7 4.06 8.50 2.00 ‐ ‐ 4.85 2.71 2.63 0.52 ‐ ‐ 1.95 1.25 0.40
W8 4.67 3.00 ‐ ‐ ‐ 3.83 3.73 1.72 ‐ ‐ ‐ 2.73 1.38 0.71
W9 4.42 4.00 3.00 ‐ ‐ 3.81 1.22 3.68 1.00 ‐ ‐ 1.97 0.98 0.52
W10 3.60 5.00 ‐ ‐ ‐ 4.30 1.20 9.66 ‐ ‐ 5.43 1.01 1.26
W11 3.00 4.00 1.00 ‐ ‐ 2.66 2.61 5.29 0.14 ‐ ‐ 2.68 1.92 1.01
W12 3.50 4.00 ‐ ‐ ‐ 3.75 3.80 8.85 ‐ ‐ ‐ 6.32 2.19 1.69
W13 4.67 2.00 3.00 ‐ ‐ 3.22 3.80 0.60 3.78 ‐ ‐ 2.72 1.85 0.85
W14 3.83 6.00 ‐ ‐ 4.90 3.63 1.03 ‐ ‐ ‐ 2.33 2.85 0.48
W15 4.40 5.00 ‐ ‐ ‐ 4.70 2.35 1.13 ‐ ‐ ‐ 1.74 2.48 0.37
W16 4.25 4.00 4.13 ‐ ‐ 4.13 1.52 2.19 1.86 ‐ ‐ 1.86 1.39 0.45
W17 3.14 7.00 ‐ ‐ ‐ 5.00 2.84 2.74 ‐ ‐ 2.79 1.19 0.52
W18 4.05 3.11 3.80 5.00 ‐ 3.98 1.79 2.40 2.27 0.65 ‐ 1.78 0.93 0.45
W19 4.78 3.73 3.00 ‐ ‐‐ 3.84 2.70 2.31 1.46 1.33 ‐ 1.95 1.54 0.51
W20 4.17 6.00 ‐ ‐ ‐ 5.08 2.61 1.94 ‐ ‐ ‐ 2.27 1.59 0.45
W21 4.36 3.67 3.00 ‐ ‐ 3.67 1.70 1.79 5.86 ‐ ‐ 3.11 1.46 0.85
W22 5.13 3.75 4.00 ‐ ‐ 4.29 2.94 1.47 7.35 ‐ ‐ 3.91 1.79 0.91
W23 4.58 2.40 5.00 ‐ ‐ 3.99 2.74 1.21 16.25 ‐ ‐ 6.73 1.38 1.69
W24 5.40 2.50 4.00 ‐ ‐ 3.96 4.57 0.75 5.32 ‐ ‐ 3.55 1.33 0.90
W25 2.60 ‐ ‐ ‐ ‐ 2.60 4.33 ‐ ‐ ‐ ‐ 4.33 1.61 1.56
W26 3.00 ‐ ‐ ‐ ‐ 3.00 1.75 ‐ ‐ ‐ ‐ 1.75 0.61 1.70
Basin 4.17 4.18 3.76 5.00 5.00 4.42 2.42 2.07 1.66 1.73 1.73 1.72 1.35 0.38
Table 4.3: Derived parameters
77
4.3.3.3 Form Factor
According to Horton (1932), form factor (Rf) may be defined, as the ratio of
basin area to square of the basin length.
Rf = A / Lb²,
Where, Rf = Form Factor
A = Area of the Basin (Sq.Km)
Lb² = Square of Basin length
Rf value of the basin is 0.30 and the value for all the watersheds are shown in
Table 4.3.The low values of Rf for the basin and most of the watersheds once again
confirms an elongated shape. The index of Rf shows the inverse relationship with
square of axial length and a direct relationship with peak discharge (Gregory and
Walling, 1973). From the shape parameter analysis, one thing which is very clear is
that all the 3 above mentioned factors indicate an elongated shape of the basin
which in turn has an effect on the discharge characteristic of the basin. Floods take a
longer time to travel in an elongated basin when compared to a circular basin
(Gregory and Walling, 1973).
The relationship among form factor, circularity ratio, elongation ratio and
length of overland flow in each sub‐watershed has been presented in Fig. 4.4.
Figure 4.4: The relationship among form factor, circularity ratio and elongation ratio
0
0.5
1
1.5
2
2.5
1 3 5 7 9 11 13 15 17 19 21 23 25water shed
Form factor
Circularity ratio
Elongatio ratio
78
4.3.4 Parameters for Dissection Intensity
4.3.4.1 Drainage density (Dd)
Horton (1945) defined the drainage density as the ratio of total length of all
stream segments in a given drainage basin to the total area of that basin.
,
Where, D = Drainage Density
Lu = Total stream length of all orders
A = Area of the Basin (Sq.Km)
Dd is an indicator of basin dissection. Langbein (1947) recognized the
significance of Dd as a factor determining the time of travel by water and he also
suggested a drainage density varying between 0.55 and 2.09 km/sq.km in humid
region with an average density of 1.03 km/sq.km. Density factor is related to climate,
type of rocks, relief, infiltration capacity, vegetation cover, surface roughness and
run‐off intensity index. Of these only surface roughness has no significant correlation
with drainage density. The amount and type of precipitation influences directly the
quantity and character of surface run‐off. An area with high precipitation such as
thundershowers loses greater percentage of rainfall as run‐off resulting in more
surface drainage lines. Amount of vegetation and rainfall absorption capacity of soils,
which influences the rate of surface run off affects the drainage texture of an area.
The similar condition of lithology and geologic structures, semi‐arid regions have
finer drainage density texture than humid regions.
According to Nag (1998), low drainage density generally results in the areas of
highly resistant or permeable subsoil material, dense vegetation and low relief. High
drainage density is the result of weak or impermeable subsurface material, sparse
vegetation and mountainous relief. Low drainage density leads to coarse drainage
texture while high drainage density leads to fine drainage texture.
79
Smith (1950) has classified drainage density into 5 different textures as
follows:
Drainage Density (km/ sq.km) Texture
<2 Very coarse
2‐4 Coarse
4‐6 Moderate
6‐8 Fine
>8 Very fine
Table 4.4: Classification of drainage density (after Smith, 1950)
The parameters like resistance to erosion of rocks, infiltration capacity of land
and climate conditions influence the drainage density (Vestappan 1983). Drainage
density of the Lakshmantirtha basin as a whole is 1.33 and those of the 26
watersheds are shown in Table 4.5. According to the classification given by Smith
(1950), The Dd of the watersheds and the basin are all less than 2 which is a
characteristic feature of course drainage system and reveals to some extent the
permeable nature of the sub strata. It is noted that drainage density exhibits positive
and high correlation (0.871) with Fs values of the watersheds and the basin (Fig 4.6).
This was estimated by using the SPSS (V.16) statistical software.
According to Melton (1958), these are characteristics of moderately well
drained streams, having a higher runoff when compared to their infiltration rate
indicative of a medium dissected topography. It is suggested that low drainage
density indicates the region has highly permeable subsoil, dense vegetative cover
and low relief as suggested for similar watershed elsewhere (Nag, 1998).
80
Watershed/basin Drainage Density
Drainage Texture
Length of over land
flow
W1 1.62 2.86 0.30
W2 1.55 2.43 0.32
w3 1.66 3.04 0.30
w4 1.44 2.23 0.34
W5 1.38 1.83 0.36
w6 1.06 0.98 0.47
w7 1.48 1.86 0.33
w8 1.09 1.51 0.45
w9 1.36 1.33 0.36
w10 0.93 0.94 0.53
w11 1.53 2.93 0.32
w12 1.62 3.55 0.30
w13 1.59 2.95 0.31
w14 2.25 4.38 0.22
w15 1.97 4.87 0.25
w16 1.52 2.11 0.32
w17 0.91 1.09 0.54
w18 0.96 0.90 0.51
w19 1.29 1.98 0.38
w20 1.35 2.15 0.36
w21 1.46 2.12 0.34
w22 1.57 2.82 0.31
w23 1.13 1.56 0.44
w24 1.28 1.70 0.38
w25 0.99 1.60 0.50
w26 0.51 0.31 0.96
basin 1.33 1.79 0.37
Table 4.5: Dissection intensity parameters
Drainage Density Fs
Drainage Density Pearson Correlation 1 0.87**
Sig. (2-tailed) 0.00
N 27 27
Fs Pearson Correlation 0.87** 1
Sig. (2-tailed) 0.00
N 27 27
**. Correlation is significant at the 0.01 level (2-tailed).
Table 4.6: Correlation table between stream frequency and drainage density variable
81
Figure 4.5: Scatter plot matrix shows the correlation between Fs and Dd
4.3.4.2 Drainage texture (T)
An important geomorphic concept is drainage texture which defines the
relative capacity of drainage line (Smith, 1950). Drainage texture (T) is one of the
important concepts of geomorphology which means that the relative spacing of
drainage lines. Drainage lines are numerous over impermeable areas than permeable
areas.
Drainage texture can be calculated from the following formula:
T = Dd * Fs
Where, Dd = Drainage density
Fs= Stream Frequency
According to Smith many parameters like soil type, infiltration capacity have a
bearing on drainage texture. Based on value of T, the drainage texture can be
classified in the following categories (Smith 1950), (Table 4.7).
82
The T of the Lakshmantirtha basin as whole is 1.79 while that of the 26
watersheds are shown in Table 4.7. The T values of all the watersheds are below 4
and belong to the coarse texture.
4.3.4.3 Length of overland flow (Lg)
The Length of overland flow is described as the average length of flow of
water over the surface before it become concentrated in definite stream channel
(Horton, 1945). He defined Lg as the length of flow path, projected to the horizontal
of the non‐channel flow, from a point on the drainage divide to an overland flow as
one of the most important variable, affecting both hydrologic physiographic
development of drainage basin. The Lg is approximately equal to half of the
reciprocal of the drainage density. It is calculated from the following formula:
Lg = 1 / Dd * 2,
Where, Lg = Length of Overland flow
Dd = Drainage Density
Table 4.5 reveals that the Lg is more in watershed 26 as drainage density is
the least in this watershed when compared to remaining watersheds. The computed
value of Lg for all watersheds varies from 0.232 to 0.96. A high negative correlation
(r= ‐0.888) is seen between the drainage density and length of over land flow and by
plotting a correlation matrix, using SPSS software (v.16), this can be clearly seen in
Fig. 3.6.
T Value Drainage Texture
<4 Coarse
4‐10 Intermediate
10‐15 Fine
>15 Ultra f
Table 4.7: Classification of drainage texture (after Smith, 1950)
83
Figure 4.6: : Scatter plot shows the correlation between Dd and Lg
4.3.5 Relief aspects
4.3.5.1 Relief aspects
Vertical inequalities of an area play an important role not only in controlling
the distribution of precipitation, formation of surface water features like streams,
tanks etc., but also in the availability and circulation of ground water. Relief aspects
are the function of the elevation or elevation difference at various points in a basin
or along the channels. It includes relief measures, ruggedness number and
hypsometric analysis.
4.3.5.2 Relief measures
Relief measures are indicative of potential energy of a drainage basin by
virtue of elevation above a given datum line. Different relief characteristics viz.,
maximum basin relief (H), Minimum basin relief (h), relief ratio (Rh) and relative
relief are measured.
84
4.3.5.3 Basin relief
The basin relief is an important factor in understanding the extent of
denudational characteristics (the denudational landforms are formed as a result of
active processes of weathering, mass wasting and erosion caused by different
exogenesis geomorphic agents such as water, glaciers, wind etc., the landforms
formed by agents of dedudation are identified as pediments, pediplains etc., ) of the
basin. Relief is the difference between maximum and minimum elevations in the
basin.
Basin Relief= H‐h
where, H=Maximum height of basin
h=Minimum height of basin
Basin relief has an influence on the channel slope which controls the flood
pattern and the amount of sediments which get transported (Hedley and Schumm
1961). In the present study the basin relief of the basin is 840 m and for the
watersheds the values vary from 20 m to 780 m (Table 4.8).
4.3.5.4 Relief Ratio:
According to Schumm (1963), the relief ratio is the dimensionless height‐
length ratio equal to the tangent of the angle formed by two planes intersecting at
the mouth of the basin, one representing the horizontal, the other passing through
the highest point of the basin. The relief ratio is calculated by using the following
formula:
Relief ratio = H‐h/L
Where, H= highest elevation in the basin
h= lowest elevation in the basin
L= longest axis of the basin
85
Dimensionless relief ratio measures the overall steepness of a drainage basin
and also is an indicator of the intensity of erosion process operating on the slopes of
the basin and is closely related to peak discharge and runoff intensity. Relief ratio is
directly proportional to fluvial erosion material and drainage density. There is also a
correlation between hydrological characteristics and the relief ratio of a drainage
basin. The Rh normally increases with decreasing drainage area and size of sub‐
watersheds of a given drainage basin (Gottschalk, 1964).
In the present study, the values of Rh are given in Table 4.8. The relief ratio of
the whole basin is 0.011 and the values for the watersheds range from 0.004 to
0.037). It is noticed that the high values of Rh indicate steep slope and high basin
relief (780 m ), while the lower values may indicate the presence of basement rocks
that are exposed in the form of small ridges and mounds with lower degree of slope
(GSI, 1981).
4.3.5.5 Relative relief (Rr)
Melton (1958) suggested the relative relief as ratio of maximum basin relief
(H) to basin perimeter (P).
Rr = basin relief / P
Where, Rr = Relative Ratio
Basin relief= H‐h
P = Perimeter (km)
For calculating the relative relief, the method proposed by Melton (1958) has
been adopted for the present study and represented in Table 4.8. It can be seen from
table that the maximum value of Rr observed in watershed 2 (0.0105) and the
minimum in watershed 24 (0.0008).
86
4.3.5.6 Gradient ratio
Gradient ratio is an indication of channel slope from which and assessment
of the runoff volume could be elevated. Gradient ratio is calculated by using the
following formula:
Gradient ratio = (a‐b)/L
Where, a = Elevation at source of the basin
b= Elevation at Mouth of the basin
L= Length of the main stream
The basin has a gradient ratio of 0.0097 and the values for the 26 watersheds
are presented in Table 4.8 and range between 0.01 ‐ 0.003, showing low to moderate
gradient.
4.3.5.7 Ruggedness number (Nr)
To combine the qualities of slope steepness and length, a dimensionless
ruggedness number is formed of the product of basin relief (“H‐h”) and drainage
density “Dd” where both terms are in same units (Strahler, 1958).By using the
following formula ruggedness number is calculated.
Nr = Dd * H / 1000
Where, Nr = Ruggedness Number
Dd = Drainage Density
H (H‐h) = Total relief of the basin in Kilometres
If “Dd” increases while “H‐h” remains constant, the average horizontal
distance from divides to adjacent channels is reduced, with an accompanying
increase in slope steepness. If “H‐h” increases while “Dd” remains constant, the
elevation difference between divides and adjacent channels also increases, so that
87
slope steepness increases. Extremely high values of the ruggedness number occur
when both variables are large, this is when slopes are not only steep but long as well.
In the present study, the Nr for the basin and all watersheds have been
calculated and given in Table 4.8. High value of Nr for the basin (1.11) indicates that
lower order streams which extend very close to the water divide. Sharma (1982);
Prasad (1984); Balasubramanian (1986) and Venugopal (1988) have also observed
same type of results in the river basins of hard rock areas of South India.
4.4 Topography of the area
Topography maps are the most important source for a detailed study of
landforms and characteristic features of the surface area, which provide more
information about shape, size and relief of the area. Topographic map provides
details about shape, relief and size in three dimensional view of the area.
The contours of the study area were digitized using Auto CAD (V.2000). Using
the contour reading values the relief map was prepared by the help of Arcview (3.2a)
software (Fig. 4.7 and 4.8). The topographic map of the study area also was prepared
using Global Mapper software (v.10) (Fig. 4.9). In the Fig. 4.9 the profile of the terrain
is shown from the southwest (SW) to northeast (SE). In both the figures Fig. 4.8 and
Fig. 4.9 it can be clearly seen that the SW of the basin shows more undulation when
compared to the NE which is comparatively a flat terrain.
88
Figure 4.7: map of the drainage basin of Lakshmantirtha
89
Figure 4.8: map of the drainage basin of Lakshmantirtha
90
Figure 4.9: Profile of the drainage basin of Lakshmantirtha
4.5 Hypsometric analysis (Area altitude analysis)
Hypsometry involves the measurement and analysis of relationships between
altitude and basin area to understand the degree of dissection and stage of cycle
erosion. Here the hypsometric curve is used to show the relationship between the
altitude and area of a basin.
Hyposmetric Curve (HC) is generally used to show the proportion of area of
surface at various elevations above or below a datum (Morkhousa and Wilkinson,
1967) and thus the values of area are plotted as ratios of total area of the basin
against the corresponding height of the contours. Hypsometric analysis is appealing
because of its dimensionless parameter that permits comparison of watersheds
irrespective of scale issues (Dowling et al., 1998). Hypsometric curves (HC) and
hypsometric integrals are important indicators of watershed conditions (Ritter et al.
2002). Differences in the shape of the curve and the hypsometric integral value are
related to the degree of disequilibria in the balance of erosive and tectonic forces
(Weissel et al., 1994).
In the present study Hypsometric curve is obtained by plotting the relative
area along the abscissa and relative elevation along the ordinate.
91
Basin / Watershed
Relief Elevation in 'm"
basin relief
Longest Axis L
Relative Relief
Relief ratio (H‐h)/L
Gradient Elevation Height (a‐b)
Longest axis L
Ratio (a‐b)/L
Ruggedness No. (Nr)
Max H Min H Source a mouth b
1 1020 820 200 14.8 0.004 0.013 1000 820 180 14.8 0.0121 0.324 2 1600 820 780 20.78 0.010 0.037 1480 820 660 20.78 0.0317 1.207 3 1040 820 220 22.5 0.003 0.011 1000 820 180 22.5 0.01 0.366 4 880 800 80 8 0.002 0.01 880 800 80 8 0.01 0.115 5 1000 800 200 18.1 0.003 0.011 940 800 140 18.1 0.007 0.276 6 880 800 80 6.4 0.003 0.0125 860 800 60 6.4 0.009 0.084 7 1220 820 400 18.41 0.009 0.021 1000 820 180 18.41 0.009 0.592 8 840 800 40 5.7 0.001 0.007 840 800 40 5.7 0.007 0.044 9 980 800 180 15 0.004 0.012 940 800 140 15 0.009 0.245 10 840 800 40 10.4 0.001 0.0038 840 800 40 10.4 0.0038 0.037 11 880 800 80 7.74 0.003 0.01 880 800 80 7.74 0.01 0.122 12 860 800 60 4.24 0.004 0.014 860 800 60 4.24 0.014 0.097 13 880 800 80 5.56 0.004 0.015 860 800 60 5.56 0.01 0.127 14 880 800 80 5.27 0.005 0.015 860 800 60 5.27 0.011 0.180 15 840 800 40 4.84 0.002 0.008 840 800 40 4.84 0.008 0.079 16 840 800 40 4.5 0.002 0.008 840 800 40 4.5 0.008 0.061 17 840 780 60 9.15 0.001 0.0065 840 800 40 9.15 0.004 0.055 18 980 780 200 28.5 0.002 0.007 980 780 200 28.5 0.0108 0.193 19 900 780 120 24.2 0.001 0.004 900 780 120 24.2 0.0049 0.155 20 900 780 120 5.2 0.005 0.023 820 780 40 5.2 0.007 0.162 21 900 780 120 9.6 0.004 0.0125 860 780 80 9.6 0.008 0.175 22 840 760 80 7.11 0.001 0.011 820 760 60 7.11 0.008 0.126 23 800 780 20 6 0.001 0.0004 800 780 20 6 0.0004 0.023 24 820 780 40 10.5 0.0008 0.003 820 780 40 10.5 0.003 0.051 25 800 780 20 3.3 0.0001 0.0060 800 780 20 3.3 0.0060 0.020 26 860 800 60 2.78 0.002 0.0215 860 800 60 2.78 0.0215 0.031
Basin 1600 760 840 72 0.003 0.01101 1460 760 700 72 0.0087 1.117 Table 4.5: Relief parameters
92
The relative area is obtained as a ratio of the area above a particular contour to the
total area of the watershed encompassing the outlet (a/A) and the relative elevation is
calculated as the ratio of the height of the given contour (h) from the base plane to the
maximum basin elevation (H), (up to the remote point of the watershed from the
outlet), (Sarangi et al., 2001 and Ritter et al., 2002). The resulting curve called the
hypsometric curve starts at the top left hand corner at 1.00 and ends at the bottom
right hand corner at 1.00 (Fig. 4.10). For computing the relative area of the basins and
the watersheds, with the help of the of the surface analysis tool in the Arcview software
the area above each contour was computed. Another important parameter in
hypsometric analysis is the hypsometric integral (HI). The hypsometric integral is
obtained from the hypsometric curve and is equivalent to the ratio of the area under
the curve to the area of the entire square formed by covering it. It is expressed in
percentage units and is obtained from the percentage hypsometric curve by measuring
the area under the curve. This provided a measure of the distribution of landmass
volume remaining beneath or above a basal reference plane. According to Strahler
(1952), the entire period of cycle of an erosion of a basin can be grouped in to three
stages viz., monadnock (old) (Hsi≤0.3), in which the watershed is fully stabilized;
equilibrium or mature stage (0.3≤Hsi≤0.6); and inequilibrium or young stage (Hsi≥0.6),
in which the watershed is highly susceptible to erosion (Strahler 1952; Sarangi et al.,
2001), (Fig. 4.10).
Figure 4.7: Cycle erosion of a basin (after Strahler, 1952)
93
4.5.1 Estimation of Hypsometric Integral (HI)
The hypsometric integral or the area under the curve can be estimated by four
different methods which are as follow:
1) Integration of Hypsometric Curve
2) Use of the Leaf Area Meter (LAM)
3) Use of the Planimeter Equipment
4) Use of Elevation–Relief Ratio (E)
In the present study the integral values of the basin and the watersheds were
calculated using the mathematical integration value. The plotted hypsometric curves
were fitted with a trend line (polynomial) in excel software to represent an equation of
the curve and the best fitting equation was obtained for highest coefficient of
determination (R2) value. The equation was further integrated within the limits of 0 to 1
(due to the non‐dimensional nature of the graph) for estimating the area under the
curve. Thus the estimated area gives the hypsometric integral value of the hypsometric
curve. The developed polynomial equation by fitting the hypsometric curve of the basin
is shown in Fig. 4.11. The fitted equation was integrated within the desired limits to
estimate the area under the HC. The hypsometric integral values, relative area and
relative heights obtained for the basin and 26 watersheds are presented in Table 4.9.
Figure 4.8: The fitted equation of the hypsometric curves for the basin
y = ‐20.648x5 + 56.269x4 ‐ 58.044x3 + 28.626x2 ‐ 7.1344x + 0.9273
R² = 0.9945
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.20 0.40 0.60 0.80 1.00
Relative
height (h/H
)
Relative area (a/A)
basin
94
Contour
values
Relative area
(a/A)
Relative
height
Hypsometric
Integral
Basin
760 1 0
0.204
800 0.96 0.047840 0.72 0.095880 0.46 0.14920 0.32 0.19960 0.22 0.231000 0.18 0.281050 0.14 0.341100 0.11 0.401150 0.09 0.461200 0.07 0.521250 0.06 0.581300 0.04 0.641350 0.03 0.701400 0.02 0.761450 0.007 0.821500 0.001 0.881550 0.0005 0.941600 0 1
Watershed 1
820 1 0
0.267
840 0.32 0.11860 0.17 0.22880 0.136512 0.33900 0.108 0.44920 0.06 0.55940 0.03 0.66960 0.01 0.77980 0.008 0.881000 0.0030 0.91020 0 1
Watershed 2
820.00 1.00 0.00
0.287
860.00 0.66 0.05900 0.58 0.10940 0.54 0.15980 0.48 0.211020 0.44 0.261100 0.36 0.361180 0.29 0.461260 0.22 0.561340 0.16 0.671420 0.08 0.771500 0.01 0.871600 0.00 1.00
Watershed 3
820 1.00 0.00
0.245
860 0.69 0.13900 0.41 0.27940 0.13 0.40980 0.04 0.531020 0.02 0.671060 0.01 0.801080 0.00 0.931100 0.00 1.00
Watershed 4
800 1.00 0.00
0.562 820 0.91 0.25840 0.66 0.50860 0.18 0.75880 0.00 1.00
95
Watershed 5
800.00 1.00 0.00
0.253
840.00 0.85 0.11880.00 0.45 0.22920.00 0.22 0.33960.00 0.09 0.441000.00 0.05 0.561040.00 0.03 0.671080.00 0.01 0.781120.00 0.00 0.891140.00 0.00 0.941160.00 0.00 1.00
Watershed 6
800 1.00 0.00
0.385
820 0.79 0.20840 0.46 0.40860 0.15 0.60880 0.03 0.80890 0.01 0.90900 0.00 1.00
Watershed 7
800 1.00 0.00
0.319
840 0.90 0.10880 0.69 0.19920 0.45 0.29960 0.29 0.381000 0.21 0.481020 0.17 0.521060 0.11 0.621100 0.06 0.711120 0.05 0.811160 0.02 0.901200 0.00 0.951220 0.00 1.00
Watershed 8
800 1.00 0.00
0.203
820 0.62 0.14840 0.22 0.29860 0.13 0.43880 0.09 0.57900 0.05 0.71920 0.02 0.86940 0.00 1.00
Watershed 9
800.00 1.00 0.00
0.389 820 0.89 0.11840 0.70 0.22860 0.56 0.33880 0.35 0.44900 0.24 0.56
920 0.14 0.67940 0.04 0.78960 0.01 0.89980 0.00 1.00
Watershed 10
800.00 1.00 0.00
0.382
820 0.89 0.11840 0.70 0.22860 0.56 0.33880 0.35 0.44900 0.24 0.56920 0.14 0.67940 0.04 0.78960 0.01 0.89980 0.00 1.00
Watershed 11 800 1.00 0.00 0.429 820 0.88 0.20
96
840 0.60 0.40860 0.17 0.60880 0.04 0.80900 0.00 1.00
Watershed 12
800 0.00 1.00
0.496 820 20.00 0.69840 40.00 0.30860 60.00 0.00
Watershed 13
800 1.00 0.00
0.407
820 0.87 0.20840 0.51 0.40860 0.13 0.60880 0.06 0.80900 0.00 1.00
Watershed 14
800 1.00 0.00
0.392 820 0.74 0.25840 0.25 0.50860 0.11 0.75880 0.00 1.00
Watershed 15
800 1.00 0.00
0.517 810 0.74 0.25820 0.51 0.50830 0.31 0.75840 0.00 1.00
Watershed 16 800 1.00 0.00
0.601 820 0.68 0.50840 0.00 1.00
Watershed 17
780 1.00 0.00
0.445 800 0.69 0.33820 0.19 0.67840 0.00 1.00
Watershed 18
780 1.00 0.00
0.244
820 0.95 0.10860 0.68 0.19900 0.28 0.29940 0.14 0.38980 0.08 0.481020 0.05 0.571060 0.03 0.671100 0.02 0.761140 0.01 0.861180 0.00 0.951200 0.00 1.00
Watershed 19
780 1.00 0.00
0.476
800 0.88 0.17820 0.70 0.33840 0.44 0.50860 0.24 0.67880 0.09 0.83900 0.00 1.00
Watershed 20
780 1.00 0.00
0.377
800 0.75 0.20820 0.42 0.40840 0.19 0.60860 0.05 0.80880 0.00 1.00
Watershed 21
780 1.00 0.00
0.411 800 0.90 0.17820 0.67 0.33840 0.30 0.50860 0.07 0.67
97
880 0.02 0.83900 0.00 1.00
Watershed 22
760 1.00 0.00
0.477 780 0.79 0.25800 0.48 0.50820 0.15 0.75840 0.00 1.00
Watershed 23
780 1.00 0.00
0.267 800 0.37 0.33820 0.05 0.67840 0.00 1.00
Watershed 24
760 1.00 0.00
0.374 780 0.66 0.25800 0.27 0.50820 0.10 0.75840 0.00 1.00
Watershed 25
780 0.0075 0.00
0.377 785 0.0045 0.25790 0.0023 0.50795 0.0008 0.75800 0.00 1.00
Watershed 26
800 1.00 0.00
0.45 820 0.74 0.33840 0.05 0.67850 0.02 0.83860 0.00 1.00
Table 4.6: Relevance of relative area, relative height and Hypsometric Integral (HI) on Watershed Hydrologic Responses
The HI value of Lakshmantirtha basin (0.204) indicated that 20.4% the original
rock masses still exist in this basin. The estimated HI values reveal that the basin (0.204)
and few watersheds mainly on the western part were in the monadnock stage and the
remaining watersheds were all in the mature stage. The watersheds with mature stages
were located at lower elevations, the reason of which can be mainly attributed to the
human interventions in the form of construction of roads, intensive agricultural
practices and deforestation activities. It is understood that the hydrologic response of
the sub basins attaining the mature stages will have slow rate of erosion (Ritter et al.,
2002) unless there is very high intense storms leading to high runoff peaks. According to
Omvir Singh (2008), the HI values less than 0.5 needs minimum mechanical and
vegetative measures to arrest sediment loss but may require more water harvesting
type structures to conserve water at appropriate locations in the watershed for
conjunctive water use. Whereas watersheds, which are having hypsometric integral
values more than 0.5 (i.e., approaching youthful stage) need construction of both
vegetative and mechanical soil and water conservation structures to arrest sediment
load and conserve water for integrated watershed management.
98
Legend: X axis: Relative area (a/A) Y axis: Relative height (h/H)
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
basin
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w1
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w2
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w3
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w4
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w5
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w6
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w7
99
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w8
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w9
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w10
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w11
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w12
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w13
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w14
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w15
100
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w16
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w17
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w18
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w19
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w20
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w21
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w22
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w23
101
Figure 4.9 : Hypsometric curve of the basin and its 26 watersheds
4.6 Interrelationship of Different Morphometric Parameters by Using factor Analysis
Statistics methods are applied in a variety of fields in hydrological research.
Factor analysis is useful for interpretation of morphometric parameters and relating the
same to specific hydrological processes. Multivariate analysis is simply a collection of
procedures for analysing the associations between two or more sets of data that have
been collected on each object in one or more samples of objects. By using factor
analysis the less significant variables are eliminated and the remaining is arranged in a
manner which would make interpretation an easy task.
Adopting statistical applications in hydrological studies began with Synder (1962)
who introduced some solutions in hydrological modelling. Later on many other workers
like Wong (1979); Wallis (1965); Shukla and Verma, (1975) and Mishra and
Satyanarayana (1988), also used different statistical methods like cluster analysis and
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w24
0.00
0.20
0.40
0.60
0.80
1.00
0.0075 0.5075
w25
0.00
0.20
0.40
0.60
0.80
1.00
0.00 0.50 1.00
w26
102
principal component analysis for developing hydrological prediction equation and to
group the most likely significant groups.
The method of factor analysis and varimax rotation is based on the principles
demonstrated by Davis (1973). A correlation matrix was first computed in the first step
for the given geomorphic parameters (Table 4.10). The eigen values were computed
since these eigen values of each component explains the total variance explained by the
variables on the component. The factor extraction was done with a minimum
acceptable eigen values of > 1. The fourteen variables were reduced to four factors. The
factors account for 82% of the total variability of the data. The factor‐loading matrix is
rotated to varimax rotation which results is maximisation of the variance of the factor
loadings of the variables on the factor matrix (Table 4.11). The factor loading is a
measure of the degree of closeness between variables and the factor.
By observing the correlation matrix on the 12 selected geomorphic parameters,
it is very clear that a good correlation exists among some of the variables and some of
the variables do not show any significant correlations. For this purpose, by the rotation
factor matrix in factor analysis using SPSS software (V16), the variables were further
classified as factors and these factors having one or few variables in each (Table 4.11)
As shown in the Table 4.11, the variables are classified in to 5 factors, which are
discussed as bellow:
Factor 1: This factor includes the area, perimeter and the basin length of the 26 watersheds.
Factor 2: Drainage density and stream frequency
Factor 3: Relative relief and Rugedness number
Factor 4: Elongation ratio, Circularity ratio and form factor
Factor 5: Bifurcation ratio
103
The first factor is mainly loaded on variables i.e., basin perimeter, basin area and
basin length and it reveals that these parameters have the greatest influence on the
form and processes of the drainage basin. The second factor which is termed as run‐off
factor shows a high correlation between the drainage density and stream frequency
(r=0.872) and these geomorphic variables control the run‐off of the basin. Calculating
the run‐off an area is important specially in hydrologic modelling. For example when
one wants to calculate sediment yield silted by this run off in reservoirs of the
watershed and also in management of water resources this factor plays an important
role. Factor 3 is termed as the relief parameter and exhibits a high correlation between
relative relief and Nr (r=0.844). By this it can be said that if the relative relief increases,
the Nr also increases and influences on the slop of the terrain. As it can be seen in the
correlation Table 4.7 of the fourth factor, a moderately negative correlation exists
between the elongation ratio and circularity ratio and a moderately positive correlation
exist between the form factor and elongation ratio. As discussed earlier, all the
mentioned parameters suggest an elongated shape for the whole basin while is some of
the watersheds were circular in shape. A negative loading also is seen on the steam
length ratio in the fourth factor which concludes that this variable does not effect on
the shape parameter. The last factor is seen with a single variable of high loading and it
is the bifurcation ratio.
4.7 Significance
Laskmantirtha basin and its 26 watersheds exhibit a dendritic drainage pattern.
The variation in stream length ratio is due to change in slope and topography. The
higher values of mean bifurcation ratio of watersheds indicate that geological structure
has a stronger control on their drainage pattern compare to the watersheds with lower
values.
104
Correlation Matrix
area Perimeter
Basin
Length
Stream Length
Ratio(mean)
Drainage
Density
Elongation
ratio
Circularity
Ratio
Form
factor Fs
Relative
Relief Nr.
Bifurcation
Ratio(mean)
Correlation
area 1.00 0.86 0.88 -0.28 -0.13 -0.28 -0.007 -0.22 -0.26 0.11 0.36 -0.005
Perimeter 0.86 1.00 0.88 -0.16 -0.20 -0.26 -0.31 -0.37 -.035 0.12 0.50 0.03
Basin Length 0.88 0.88 1.00 -0.37 -0.00 -0.59 -0.008 -0.42 -0.22 0.29 0.55 0.06
Stream Length
Ratio(mean)
-0.28 -0.16 -0.37 1.00 -0.14 0.30 -0.22 -0.11 0.08 -0.34 -0.35 -0.08
Drainage Density -0.13 -0.20 -0.005 -0.14 1.00 -0.36 0.55 0.14 0.87 0.42 0.27 .028
Elongation ratio -028 -0.26 -0.59 0.30 -0.36 1.00 -0.24 0.35 -.015 -0.38 -040 -0.25
Circularity Ratio -.00 -0.31 -0.008 -0.22 0.55 -0.24 1.00 0.19 0.41 0.38 0.026 0.01
Form factor -0.22 -0.37 -0.42 -0.11 0.14 0.35 0.19 1.00 0.18 -0.20 -0.30 0.01
Fs -0.26 -0.35 -0.22 0.08 0.87 -0.15 0.41 0.18 1.00 0.19 0.04 0.19
Relative Relief 0.11 0.12 0.29 -0.34 0.42 -0.38 0.38 -0.20 0.19 1.00 0.84 0.21
Nr. 0.36 0.50 0.55 -0.35 0.27 -0.40 0.02 -0.30 0.04 0.84 1.00 0.09
Bifurcation
Ratio(mean)
-0.00 0.03 0.06 -0.08 0.28 -0.25 0.01 0.01 0.19 0.21 0.09 1.00
Table 4.7: Correlation matrix of morphometric units
105
Component
1 2 3 4 5
area 0.93
Perimeter 0.87
Basin Length 0.95
Stream Length Ratio(mean) -0.71
Drainage Density 0.89
Elongation ratio 0.51
Circularity Ratio 0.73
Form factor 0.72
Fs 0.87
Relative Relief 0.92
Nr. 0.87
Bifurcation Ratio(mean) 0.95
Extraction Method: Principal Component Analysis.
Rotation Method: Varimax with Kaiser Normalization.
a. Rotation converged in 6 iterations.
Table 4.8: Rotated Component Matrix
The Dd of the basin as well as those of the watersheds, reveal that the nature
of the subsurface is permeable. This is a characteristic feature of coarse drainage.
The shape parameters also reveal the elongated shape for the basin. Due to this
characteristic, the basin will tend to have lesser flood peaks but longer lasting flood
flows compared to round basins. This particularly is very important while considering
the management and reservoir projects and a progressive land use pressures. The
geomorphic development of the basin also reveals it is in the monadnock stage.
Factor analysis was carried out on morophmetric units and grouped them in to 5
factors.