Biotechnological
Communication
Biosci. Biotech. Res. Comm. 10(3): 431-437 (2017)
Spatial and temporal ground water responses to
seasonalrainfall replenishment in an alluvial aquifer
Sourabh Nema
1
, M. K. Awasthi
2
and R. K. Nema
3
1
Department of Soil & Water Conservation Engineering, JNKVV, Jabalpur
2
Professor, Department of Soil & Water Conservation Engineering, JNKVV, Jabalpur
3
Professor & Head, Department of Soil & Water Conservation Engineering, JNKVV, Jabalpur
ABSTRACT
Groundwater is an enormously vital water resource available on earth. Due to over exploitation of groundwater,
especially in dry regions and in the water scares areas, has led to irretrievable consequences due to deterioration of
water quality. The groundwater resources, which are found in shallow depth often have poor in water quality and in
most cases the ground water are severely over-exploited. Therefore, the study has been planned to identify the spatial
& temporal variation of aquifer responses of the study area to the natural recharge as well as Ground water level
trend in last 15 years. This study is conducted in Tawa command area, which lies in Hoshangabad District of Madhya
Pradesh. Also facing problem of water logging and shortage in the region. The study identi ed the spatial behavior of
ground water level in pre-monsoon and post monsoon. Insight of the current study, the spatial and temporal graphi-
cal analysis for the observation sites of the uncon ned aquifer indicated that there is a good hydraulic connection of
groundwater level with the rainfall.
KEY WORDS: AQUIFER, GROUNDWATER RESOURCES, WATER LOGGING, WATER LEVEL FLUCTUATION
431
ARTICLE INFORMATION:
*Corresponding Author:
Received 20
th
June, 2017
Accepted after revision 27
th
Sep, 2017
BBRC Print ISSN: 0974-6455
Online ISSN: 2321-4007 CODEN: USA BBRCBA
Thomson Reuters ISI ESC and Crossref Indexed Journal
NAAS Journal Score 2017: 4.31 Cosmos IF: 4.006
© A Society of Science and Nature Publication, 2017. All rights
reserved.
Online Contents Available at:
http//www.bbrc.in/
DOI: 10.21786/bbrc/10.3/16
432 SPATIAL AND TEMPORAL GROUND WATER RESPONSES TO SEASONALRAINFALL REPLENISHMENT BIOSCIENCE BIOTECHNOLOGY RESEARCH COMMUNICATIONS
Nema, Awasthi and Nema
INTRODUCTION
Water is the most vital resource of both biosphere and
human society, without which no life can sustain on
the earth. Over 95% of the earth’s useable freshwater is
stored as groundwater, of which about 50% exists within
the earth’s crust down to a depth of 800 m, while only
1.5% exists in rivers and lakes (World Bank, 2010). Over
exploitation of groundwater for irrigation and other pur-
poses, especially in dry climates and in areas which are
facing water stress, has led to irreversible consequences.
The water stress on different sessions leads to Groundwa-
ter-level  uctuations, which basically represent hydrau-
lic responses to changes in groundwater storage due to
aquifer recharge and drainage as well as to changes in
stress that include water mass loading and unloading
above the aquifer surface (Burgess etal., 2017).
In order to meet the requirement of fast growing popu-
lation and industrialization, the water demand has been
increased signi cantly all over the globe. Overexploitation
of groundwater in many part of the world has resulting a
threatening condition of falling groundwater levels, saline
water infringement, crop demand-supply gap, drying of
the shallow aquifers, increasing power consumption due
to increase in cost of lift, decrease in free  ow and even
local subsidence in some places (Singh and Singh, 2002).
In many regions there is a lack of surface water
resource and the water bearing sub-surface zones are
having severe water contamination. Shallow groundwa-
ter resources are often of poor quality and above that
they are severely over-exploited. In a recent study based
on the analysis of GRACE satellite data revealed that the
groundwater resources in the states of Rajasthan, Punjab
and Haryana are being depleted at a mean rate of mean
rate of 4.0+1 cm yr-1 (Rodell etal., 2009).
Thus, it is evident that the current patterns of water
development and consumption are not sustainable in
several countries of the world, including India. Impend-
ing global/regional climate change, increasing popula-
tion and growing socio economic changes are expected
to exacerbate existing groundwater depletion through
considerable rise in water demand (Sauer et al., 2010;
Brown et al., 2013) and alterations in the spatio-tem-
poral availability of freshwater resources (Healy, 2002;
Elliott etal., 2014; Schewe etal., 2014; Bouwer, 2002;
CGWB, 2012; Singh, 1997; Kumar, 2002; Vanderzalm
etal. 2015 Nema 2017, and Smith etal., 2016).
Therefore, there is an urgent need for ef cient man-
agement of freshwater resources in India in order to
ensure sustainable management of our depleting fresh-
water resources.In many parts of India, The water table
is declining at a very fast rate. In few locations, it has
been gone beyond to the depth where it is uneconomi-
cal for pumping water for non-commercial and com-
mercial uses. In few states, the situation is so critical
that Government has banned ground pumping to sta-
bilize the ground water. Groundwater extraction rate is
not only the one factor which is responsible for declin-
ing water levels, the low rainfall resulting due to inad-
equate monsoon is equally responsible. Majority of the
ground water stress areas categorized as overexploited
and critical units also lies in such states. Considering the
importance of Groundwater, the issue of Ground water
declination or waterlogging has to be taken with priority
considering all the proved water management technolo-
gies along with ef cient strategies shall be adopted that
could help to reduce the prevailing disaster. This cur-
rent study demonstrate a comprehensive analysis of the
effects of spatial and temporal precipitation patterns on
Ground water level  uctuations.
MATERIAL AND METHODS
Hoshangabad District which is situated in Upper Narmada
Region, M.P., lndia (Fig.1) was selected for this study. Nar-
mada River, the other main river of Hoshangabad is Tawa
River, which  ows towards north and joins river Narmada
near Hoshangabad.District Hoshangabad covers majority
of Tawa command areas which are the primary sources
of irrigation for entire district. The Hoshangabad district
lies between north latitudes 22º 15’ and 23º 00’ and east
longitudes 77º 15’ and 78º 42’ in part of survey of India
topo sheet Nos, 55F & 55J. Hoshangabad is the district
headquarter and Sohagpur, Piparia, Babai, Pachmarhi,
Seoni Malwa and Bankheri are some of the major towns.
The location map of study area is represented in Fig. 1.
Soils of the area are characterized by black grey, red and
yellow colors, often mixed with red and black alluvium
and ferruginous red ravel or lateritic soils.
Northern part of the study area (i.e. Hoshangabad dis-
trict), adjoining the Narmada river is covered with allu-
vium, which makes for more than 50% of the entire district.
Deccan traps occur as lava  ows in the west central
part of the district. The southern part of the district is hilly
and occupied by rocks belonging to Gondwanas. There
are two aquifer systems present in the study area. The top
phreatic aquifer range in thickness from 4 to 30m and
is encountered in the depth range of 4 to 20 mbgl. The
phreatic aquifer has intercalations of clay and silt, and at
places also of coarse sand or gravel. The Deeper aquifer
(i.e. con ned aquifer) ranges varies from 30 m to 60 m.
WATER LEVEL FLUCTUATION IN THE
STUDY AREA
Water table Declination in summer season is a common
problem for many part of the state as well as for India.
The current study has been done to observe the ground
BIOSCIENCE BIOTECHNOLOGY RESEARCH COMMUNICATIONS SPATIAL AND TEMPORAL GROUND WATER RESPONSES TO SEASONALRAINFALL REPLENISHMENT 433
Nema, Awasthi and Nema
water level of study area with observing the rainfall (pre
monsoon and post monsoon) and river gauge impact
over ground water level for 16 years period from year
2000 to year 2015. The  uctuations have been observed
in relation to rainfall (pre monsoon and post monsoon).
The water table  uctuations have been in uenced by
many factors. The decline of groundwater level occurs
when the out ow exceeds or less recharge over the area.
The groundwater-level level data of 74 observation
wells tapping uncon ned aquifer were collected for 15
years (2000-2015) from the Central Ground Water Board
(CGWB) and the Ground Water Survey and Investigation
(GWS&I), Bhopal, Madhya Pradesh.
RESULTS AND DISCUSSION
SEASONAL WATER LEVEL FLUCTUATIONS DUE
TO RAINFALL (YEAR 2000 TO 2015)
Monthly variations of rainfall in the study area over
16-year period (2000-2015) at eight rainfall/rain gauge
stations along with the line graphs are shown in Fig. 4.2
It is apparent from Fig. 2 that though the rainfall events
are somewhat distributed throughout the year, however
the magnitude of rainfall is quite less or zero in some
places. The rainy season usually starts from mid-June
and lasts up to the end of October.
FIGURE 1. Location map of the study area
FIGURE 2. Monthly variations of rainfall in the study area over 16 years
(2000-2015)
434 SPATIAL AND TEMPORAL GROUND WATER RESPONSES TO SEASONALRAINFALL REPLENISHMENT BIOSCIENCE BIOTECHNOLOGY RESEARCH COMMUNICATIONS
Nema, Awasthi and Nema
FIGURE 3. Variations of Annual Rainfall during 2000-2015 Period at
Eight Rainfall Stations
FIGURE 4. Spatial Variations of Mean Pre Monsoon Ground water Depth
Thus, the bulk of the annual rainfall is concentrated
in a relatively short span of time and hence runoff and
groundwater recharge are con ned to these months. As
suf cient rainfall is available during July, August, Sep-
tember and October, groundwater withdrawal is mini-
mum during these months. The standard line graph indi-
cate monthly variation of rainfall over 16-year period.
The large standard line graph during May to October
indicated considerable temporal variation of rainfall
in these months (Fig. 2). However, during November
through April, the variation in monthly rainfall is very
small. Furthermore, the rainfall of Pachmari station has
the highest rainfall for month of August, followed by
Hoshangabad & Seoni Malwa.
Long-term variations in the annual rainfall of the
study area from 2000 to 20l5 are shown in Fig. 3 for the
BIOSCIENCE BIOTECHNOLOGY RESEARCH COMMUNICATIONS SPATIAL AND TEMPORAL GROUND WATER RESPONSES TO SEASONALRAINFALL REPLENISHMENT 435
Nema, Awasthi and Nema
FIGURE 5. Spatial Variations of Mean Post Monsoon Ground water Depth
FIGURE 6. Spatial Variation of Mean ground water  uctuations depth classes
Nema, Awasthi and Nema
436 SPATIAL AND TEMPORAL GROUND WATER RESPONSES TO SEASONALRAINFALL REPLENISHMENT BIOSCIENCE BIOTECHNOLOGY RESEARCH COMMUNICATIONS
eight rain gauge stations. The average annual rainfall
over the study area is estimated at about 1099.24 mm
based on 16 years (2000-2015) rainfall records. In con-
trast, the rainfall at Pachmari station was found highest
and found above than average annual rainfall for all
years. The analysis were also done to  nd out the spatial
variation of mean ground water  uctuation depth class
(Mean of 2000-2015) over study area as shown in Fig.4.,
Fig. 5. & Fig. 6.
The minimum pre-post water  uctuation was
observed in Hoshangabad and Kesla Block. The  uctua-
tion of Pre-Post-monsoon groundwater depths (mean
of 2000-2015) was maximum in Bankhedi followed by
Babai, Sohagpur and Seoni Malwa block over the study
area is shown in Fig. 5 & Fig. 6. It is clearly evident
that the Bankhedi block of Hoshangabad showing the
maximum water  uctuation depth which may be due to
the non-command area exist on Bankhedi (Nema, 2017)
The average annual water level at downstream site
varies from 5.5 to 7.0 m in last 15 years. The rainfall
amount and ground water level from mean sea level has
been found inversely proposal similar to upstream and
middle stream sites.
The analysis of groundwater-depth contour maps of
pre- and post-monsoon seasons revealed that the mean
seasonal groundwater  uctuation in the study area
ranges from 3.45 to 7.70 m, with a major portion of the
study area having a mean groundwater  uctuation of
4.50 to 6.70 m.
Temporal analysis of Ground water level had been
done in to upstream, mid stram and down stram sites
represented in Fig 7(a-c). It has been evident from Fig.
7.(a) that in upstream, mean ground water depth varied
in the range of 10-13 m from mean sea level (MSL).
The ground water depth from MSL is seems to
be inversely correlated with rainfall. As the rainfall
amount increases the depth of water table from MSL has
decreases. Fig 7.(b) indicated the similar kind of pattern
of ground water behavious with respect to rainfall hav-
ing avg. depth 6 to 7.8 m. The trend of ground water
level wass also found increasing in middle region over
the period of time.
The similar kind of pattern of ground water depth
behaviour with respect to rainfall was found in down-
stream region. The avg. depth to ground water from
mean sea level is around 5.5 m to 7 m in last 15 years
CONCLUSION
Insight of the current study, the spatial and temporal
graphical analysis for the observation sites of the uncon-
ned aquifer indicated that there is a good hydraulic
connection of groundwater level with the rainfall. It can
also be revealed that the rainfall has reasonable correla-
tions with the groundwater level of Aquifer and sug-
gesting a signi cant contribution of recharge from the
rainfall sources to uncon ned aquifer. The study also
indicated that Bankeri block whichh lies in upstream fol-
lowed by Babai block having maximium water  uctua-
tion and depth in pre-monsoon & post monsoon which
needs to be addressed in future for arresting groundwa-
ter declination further.
FIGURE 7a. Temporal Response of Average
annual ground water level with respect to Rain-
fall for upstream region
FIGURE 7b. Temporal Response of Average annual
ground water level with respect to Rainfall for mid-
stream region
FIGURE 7c. Temporal response of Average annual
ground water level with respect to Rainfall for down-
stream region
Nema, Awasthi and Nema
BIOSCIENCE BIOTECHNOLOGY RESEARCH COMMUNICATIONS SPATIAL AND TEMPORAL GROUND WATER RESPONSES TO SEASONALRAINFALL REPLENISHMENT 437
REFRENCES
Bouwer, H. (2002). Arti cial recharge of groundwater: hydro-
geology and engineering. Hydrogeology Journal, 10:121-142.
Brown T.C., Foti R, and Ramirez I.A. (2013). Projected fresh-
water withdrawals in the United States under a changing cli-
mate, Water Resources Research, 49: 1259-1276, DOI: I 0.1002/
wrcr.20076
Burgess, W. G., Shamsudduha, M., Taylor R. G., Zahid, A.,
Ahmed, K.M., Mukherjee, A., Lapworth, D.J. and Bense V.F.
(2017). Terrestrial water load and groundwater  uctua-
tion in the Bengal Basin, Nature, Scienti c Reports 7(3872),
doi:10.1038/s41598-017-04159-w
CGWB. (2012). Dynamic Ground Water Resources of India (as
on March, 2009). Ministry of Water Resources, Government of
lndia, New Delhi.
Elliott J., Deryng D., Muller C., Frieler K., Konzmann M., Gerten
D. and Wisser D. (2014). Constraints and potentials of future
irrigation water availability on agricultural production under
climate change. Proceedings of the National Academy of Sci-
ences, 111(9): 3239-3244.
Healy, R. W. and Cook, P. G. (2002). Using groundwater levels
to estimate recharge. Hydrogeology Journal, 10: 91–109.
Kumar, C.P. and Seethapathi, P.V. (2002). Assessment of nat-
ural groundwater recharge in Upper Ganga Canal command
area. Journal of Applied Hydrology,15: 13-20.
Nema S. (2017) Ground water utilization using simulation
techniques in Tawa command area, Ph.D. thesis, JNKVV, Jabal-
pur, 205 p
Rodell M., Velicogua I., and Famiglietti J.S. (2009). Satellite-
based estimates of groundwater depletion in India, Nature 460:
999-1002.
Sauer T, Havlik P Schneider U.A., Schmid E Kindermann G.
and Obersteiner M. (2010). Agriculture and resource availabil-
ity in a changing world: The role of irrigation. Water Resources
Research, 46(6), DOI: I0.1029/2009WR007729
Schewe J Heinke J Gerten D Haddeland I Arnell NW Clark DB
and Kabat P. (2014) . Multimodel assessment of water scarcity
under climate change. Proceedings of the National Academy of
Sciences, 111(9): 3245-3250.
Singh, B. (1997).Water resources development in India - a
perspective. In Proceedings of International Symposium on
Emerging Trends in Hydrology, Department of Hydrology, Uni-
versity of Roorkee, Roorkee, India 1: 1-17.
Singh, D. K. and Singh, A. K. (2002). Groundwater Situation
in India: Problems and Perspective, International Journal of
Water Resources Development, 18(4): 563-580
Smith, M, Cross, K, Paden, M & Laban, P (2016). Spring: Manag-
ing groundwater sustainably, IUCN, Gland, Switzerland, 135 p.
Vanderzalm, JL, Dillon, PJ, Tapsuwan, S, Pickering, P, Arold,
N, Bekele, EB, Barry, KE, Donn, MJ & McFarlane, D. (2015),
Economics and Experiences of Managed Aquifer Recharge
(MAR) with Recycled Water in Australia <http://vuir.vu.edu.
au/32058/1/.
World Bank (2010). Deep wells and prudence: towards pro-
grammatic action for addressing groundwater overexploitation
in India. Washington DC, 120 p.