Full text: Proceedings, XXth congress (Part 7)

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International Archives of the Photogrammetry, Remote Sensing and Spatial Information Sciences, Vol XXXV, Part B7. Istanbul 2004 
where JW is the seasonal water level for the ith well and jth 
observation, W,, its seasonal mean, and o is its standard 
deviation. 
SWI value has been classified and used as a measure of 
hydrological drought intensity. Since ground water level is 
measured down from the surface, positive anomalies correspond 
to drought and negative anomalies correspond to ‘no-drought’ 
or normal condition. Point values of SWI corresponding to the 
wells have been interpolated to generate SWI maps of the 
region using the same technique as for SPI. 
2.3 Vegetation Indices 
Vegetative and agricultural droughts reflect vegetation stress. 
NDVI reflects the vegetation condition through the ratio of 
responses in near infrared (Ch2) and visible (Chl) bands of 
Advanced Very High Resolution Radiometer (AVHRR) of 
NOAA. It is expressed as 
NDVI = (Ch2 — Chl) / (Ch2 + Chl) (3) 
VCI, TCI, and VHI have been developed further using the 
following equations as 
VCI = 100*(NDVI — NDVIpin) / NDVImax — NDVInin) (4) 
TCI & 100*(BT max FT BT) / (Blox m Blow) (5) 
VHL=0.(VCD £0:5(TCDH (6) 
where NDVI, NDVImin and NDVInax are the seasonal average 
of smoothed weekly NDVI, its multiyear absolute minimum and 
its maximum respectively; BT, BT, and BTmax are similar 
values for brightness temperature (Kogan, 2001). 
Brightness temperature values are obtained from the thermal 
band (Ch4) of NOAA-AVHRR. NDVI generally provides a 
broad overview of the vegetation condition and spatial 
vegetation distribution in a region. Vegetative drought is closely 
related with weather impacts. However, in NDVI, the weather 
component gets subdued by strong ecological component. VCI 
separates the short-term weather-related NDVI fluctuations 
from the long-term ecosystem changes (Kogan, 1990, 1995). 
Therefore, while NDVI shows seasonal vegetation dynamics, 
VCI rescales vegetation dynamics in between 0 and 100 to 
reflect relative changes in the vegetation condition from 
extremely bad to optimal (Kogan, 1995, 2003). VCI and TCI 
characterises respectively the moisture condition and thermal 
condition of vegetation while VHI represents overall vegetation 
health (Kogan, 2001). Since favourable weather provides 
optimal moisture condition, high values of VCI correspond to 
healthy and unstressed vegetation. On the other hand, low TCI 
values correspond to vegetation stress due to dryness by high 
temperature. TCI provides opportunity to identify subtle 
changes in vegetation health due to thermal effect as drought 
proliferates if moisture shortage is accompanied by high 
temperature (Kogan, 2002). During calculation of VHI, an equal 
weight has been assumed and assigned to both VCI and TCI 
since moisture and temperature contribution during a vegetation 
cycle is currently not known (Kogan, 2001). Regional VHI 
maps have been generated through interpolation of the point 
values and classified using the scheme developed by Kogan 
(2002) and further modified*. VCI and TCI have been classified 
following the same scheme as VHI. Kogan (1995, 2001, 2003) 
formulated, calculated, and applied VCI, TCI, and VHI based 
on smoothed weekly NDVI and BT values. However, in the 
present study all these parameters have been calculated and 
analysed season wise by averaging weekly values. For 
comparison and correlation among different kinds of drought, 
SPI, SWI, and VHI maps of the same years have been displayed 
one beneath the other (Figure 5). 
3. DROUGHT IN THE ARAVALLI TERRAIN 
3.1 Meteorological Drought 
Visual observation of the time series SPI maps of the monsoon 
and non-monsoon periods indicate that drought is frequent and 
even persistent in many parts of the Aravalli terrain. They 
further show that meteorological drought scenario in the terrain 
changed. continuously with season. Beside years with 
exceptional good non-monsoon rainfall, Aravalli terrain 
regularly experienced mild drought for most of its parts in the 
non-monsoon period. The condition returns to normalcy if the 
monsoon wind appears timely and showers heavily. Spatio- 
temporal drought scenario in the Aravalli terrain in both the 
monsoon and the non-monsoon periods fallows an erratic 
pattern due to inconsistent and unstable rainfall pattern 
(Bhuiyan er al., 2004). 
During the years 1984 - 1985, insufficient rainfall resulted 
seasonal drought in some pockets of northern and southwestern 
Aravalli. In the year 1986 drought resulted in those province 
during both the monsoon and non-monsoon seasons. Poor 
monsoon visited the Aravalli terrain in succession in the year 
1987 resulting severe drought in major sectors in the north and 
south. Some small pockets in the north, south, and central parts 
suffered even extreme drought. The drought condition improved 
and worsened alternatively in the monsoon and non-monsoon 
periods respectively during the years 1988 - 90. Although good 
monsoon rainfall helped most parts of the terrain to avoid 
drought in the year 1992, some pockets in the north, south, east, 
and west of the terrain experienced drought during 1992 — 1993 
non-monsoon and 1993 monsoon seasons. In the year 1995, 
moderate drought affected some pockets in the eastern and 
southern sectors, while during the non-monsoon period drought 
appeared in the northern and eastern Aravalli. However, it was 
the western Aravalli experiencing drought during 1996 
monsoon! The drought reappeared in the terrain during the 
monsoon of 1999 too but the situation became worst during the 
monsoon season of 2000, when northern, eastern, southern, and 
southwestern sectors of the province formed a continuous 
drought-belt (Figure 5). 
3.2 Hydrological Drought 
Time series analysis of SWI maps reveals that hydrological 
drought in the Aravalli terrain during both the pre-monsoon and 
post-monsoon periods follow an alternate pattern with minor 
local variations. During the pre-monsoon period, many discrete 
pockets all over the terrain experienced moderate to extreme 
hydrological droughts in last two decades. Although during the 
years 1984 — 1985, major parts of the terrain were free from 
drought, the drought situation degraded gradually in the 
following years. 
* Through personal communication 
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