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Analysis of Water Level Fluctuations and TDS Variations in the Groundwater at Mewat (Nuh) District, Haryana (India)

Priyanka 1 * , Gopal Krishan 2 , Lalit Mohan Sharma 3 , Brijesh Kumar Yadav 4 and N. C. Ghosh 2

DOI: http://dx.doi.org/10.12944/CWE.11.2.06

Groundwater is the major source for fulfilling the water needs of domestic and agricultural sectors in Mewat district, Haryana, India and its continuous use has put an enormous pressure on the groundwater resource, which along with low rainfall and variable geographical conditions lead to the declining water levels.  The other problem of this area is high salinity which is reported intruding to the freshwater zone1. Taking into account the twin problem of declining water level and high salinity the study was taken up jointly by National Institute of Hydrology, Roorkee; Sehgal Foundation, Gurgaon and Indian Institute of Technology, Roorkee. Groundwater level and TDS (Total dissolved solids) data for pre-monsoon and post-monsoon seasons for the time period of 2011–2015 of 40 monitoring wells developed by Sehgal Foundation, Gurgaon was collected and analysed. It has been found that the groundwater level is decreasing in the area while TDS values show inconsistent trends during 2011-15.  Further monitoring of the wells is continued to get the more information on water level and TDS which will help in facilitating the researchers in finding out the applicable solutions for the above problems in the Mewat, Haryana.


Groundwater Level; TDS; Salinity; Mewat; Haryana

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Priyanka, Krishan G, Sharma L. M, Yadav B. K, Ghosh N. C. Analysis of Water Level Fluctuations and TDS Variations in the Groundwater at Mewat (Nuh) District, Haryana (India). Curr World Environ 2016;11(2) DOI:http://dx.doi.org/10.12944/CWE.11.2.06

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Priyanka, Krishan G, Sharma L. M, Yadav B. K, Ghosh N. C. Analysis of Water Level Fluctuations and TDS Variations in the Groundwater at Mewat (Nuh) District, Haryana (India). Curr World Environ 2016;11(2). Available from: http://www.cwejournal.org/?p=1545


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Article Publishing History

Received: 2016-07-18
Accepted: 2016-08-02

Introduction

With an estimated abstraction of around 230 billion cubic meter per year, India is reported as one of the largest groundwater users in the world. Nationally, groundwater accounts for 85% of India’s rural domestic water requirements and more than 60% of its irrigation requirements2. This excessive use of groundwater has led to its depletion and deterioration of quality in north-west India and across the Gangetic basin which has been reported in many studies3-18.

It has been reported that 20% of the world’s irrigated areas are affected by secondary salinization and India is one among these countries accounting for the most salinized soils to the tune of 9.38 million ha, out of which 3.88 million ha area is covered by alkali soils and 5.5 million ha area is covered by saline soils (IAB, 2000)19. Mewat district, Haryana, India is major agricultural land area with deficit of perennial surface water sources20 and therefore, the main source of irrigation and domestic use is groundwater20,21. The natural surface water sources like Kotla and Ujina lakes also remains dry most of the time of the year because of the limited number of rainy days20. The major crops grown in this area are wheat, millet and mustard, which requires huge amount of water22 and result in extraction of large amount of groundwater.  The recharge is very less due to the low rainfall being hot and semi-arid zone with the diverse physiography.

On the other hand, high salinity adversely affects productivity by deteriorating soil quality and limits the choices of crops for farmers1,23. Taking into account the twin problem of declining water level and high salinity the study was taken up jointly by National Institute of Hydrology, Roorkee along with Sehgal Foundation, Gurgaon and Indian Institute of Technology, Roorkee. Sehgal Foundation, Gurgaon has developed 40 monitoring wells in the Mewat district of Haryana where the continuous monitoring is going on.

In the present paper, groundwater level and TDS data was collected for the period 2011-15 to analyse the variations for the last 5 years.

Study Area

Recently named as Nuh, Mewat district is newly carved district among the 21 districts of Haryana state. The district lies between 26o and 28o N latitude and 76o and 77o E longitude and comprises of 5 blocks, namely Firozpur Jhirka, Nuh, Nagina, Taoru, Punahana (Figure 1).  The total population of Mewat is 1,089,263 (Census 2011)24, and 88.6% of total population comes under rural population with agriculture as main occupation and has a crop intensity of around 150%. Cultivable area is 1,53,257 ha which is around 74% of total and it depends on two main sources for irrigation- (i) canal, which covers 16432 ha area (21.6%) and (ii) groundwater- tube wells/bore wells/open wells which covers 59527 ha (78.4%) out of the net irrigation area, i.e. 75959 ha. The principle crops (wheat, Millet and Mustard) covers 192000 ha area. Also, non-cultivable area is 108334 ha (around 70%) of land25.

The land is extended by ridges of Delhi Quartzite and is majorly covered by alluvial plains. The land proximity to National Capital Region (NCR) of Delhi and also being a part of aravalli range which comprises of rocky area having below average vegetation, gives the district some specific geophysical, topographical and ecological feature values. The elevation of the district is 189 meters in height, equivalent to 620 feet. The normal annual rainfall in the district is 594 mm, out of which maximum contribution (approximate to 75%) takes place during monsoon season. May-June is the driest months of the year highlighting the water issues at that time25.

 Fig. 1: Location map of Study area, Mewat, Haryana (India)


Figure 1: Location map of Study area, Mewat, Haryana (India)
Click here to View figure


Methodology

Groundwater level and TDS were recorded for 40 monitoring wells during the time period 2011-15 (Table 1). These wells are developed by Sehgal foundation, Gurgaon and their distribution and location is shown in Fig. 2. The wells were mainly concentrated in the zones having problems of declining water level and TDS1. The groundwater levels are recorded using water level indicator and are measured as ‘meter below ground level (m bgl)’ and TDS readings were measured in-situ with TDS meter as ‘parts per million (ppm)’. The database of five years groundwater level, TDS readings and average rainfall (IMD, New Delhi) has been prepared and analyzed for the changes and trends during the period of observations. The average of the rainfall was taken between December-May (pre-monsoon) and between June-November (Post-monsoon) (Table 2).  The pre-monsoon and post-monsoon groundwater levels and TDS were plotted as time-series plots with reference to average rainfall data (Figures 3-4). The data was analyzed statistically (Tables 3-8).

There’s a constraint in the analysis of TDS data for 15 wells which was not recorded for post-monsoon season in 2012 (i.e. for Nov, 2012). The wells for which data was not recoded are: Dalli well, Huch tower well, Abdul well, Haji Mauji Khan well, Bari masjid well, Sweet well, Panchayati Kua (school), Raheem well, Johad wala well, Kamrudden well, Balmiki wala kua, Rehman well, Rasheed well, Sayyad well, Nooru well.

Table 1: Details of the wells

S.No.

Village Name

Place of Well

S.No.

Village Name

Place of Well

1

Multhan

Panchayati well near tower

21

Agon

Huch tower well

2

Badru Well

22

Abdul well

3

Ulheta

Panchayati Dholposh Kua

23

Haji Mauji Khan well

4

Karhera

Mandir Kui

24

Naharika

Bari masjid well

5

Harijan Well

25

Sweet well

6

Kabristan Well

26

Panchayati Kua (school)

7

Ratti Khan well

27

Raheem well

8

Sathawari

Wali ji well

28

Jali Khori

Johad wala well

9

Sumair well

29

Kamrudden well

10

Nagina

Asthal mandir well

30

Raniyali

Balmiki wala kua

11

Bag wala Kua

31

Nasir bas

Rehman well

12

Badkali wala kua

32

Poll

Rasheed well

13

Bich wala well

33

Thekri

Sayyad well

14

Rahat wala Kua

34

Bhond

Nooru well

15

Masjid bandh bore

35

Satakpuri

Panchayati well

16

Bhoron wala well

36

Islam well

17

Khatikan well

37

Kotla

Bangali Khola well

18

Baldev Saini well

38

Andha Kua

19

Chaypur well

39

Bali well

20

Agon

Dalli well

40

Khalid well


Table 2: Rainfall Data (2011 - 2015)

Time Period

Pre-Monsoon

Post-Monsoon

 

2010- 2011

2011- 2012

2012 - 2013

2013- 2014

2014- 2015

2011

2012

2013

2014

2015

Rainfall (mm)

0

0.2

0

8.3

0

202.6

250.2

356.6

219

509.9

*Source: Customized Rainfall Information System (CRIS), Hydromet Division, India Meteorological Department, Ministry of Earth Sciences26.

 Fig. 2. Distribution of wells in Mewat, Haryana (India)


Figure 2: Distribution of wells in Mewat, Haryana (India)
Click here to View figure


Results and Discussions

Groundwater Level

The results obtained for groundwater level data of 40 wells in five aforementioned blocks during period of 2011-15 for pre-monsoon and post-monsoon season in Mewat district are given in Tables 3 & 4 and Figure 3.

As evident from the Figure 3, groundwater level in most of wells is almost constant but decline is also observed in some wells. The water level is found to increase after the rainfall events. In pre-monsoon season, the rainfall is very less or negligible except in May 2014, where the level of the groundwater has also raised above due to recharge in aquifers. In post-monsoon season, increase in water level is observed for most of the wells. Rainfall has a direct effect on the water level in the study area. From the Fig. 3, it is clearly visible that, recharge through rain water plays an important role for aquifers at Mewat, as decline water level during the pre-monsoon time was recouped by a rise in water level in post-monsoons.

 Fig. 3. Variations in Groundwater level for pre & post monsoon seasons for the period 2011-15


Figure 3: Variations in Groundwater level for pre & post monsoon seasons for the period 2011-15
Click here to View figure


From the tables 3 & 4, it is evident that groundwater level is declining during five years’ time period. In the pre-monsoon season, the minimum decline is 1 m and maximum decline of 6.8 m with an average of 2.4 m was observed in Mewat, Haryana. For post-monsoon season, the minimum decline is 1.1 m and maximum decline of 13.3 m with an average of 2.7 m was observed in Mewat, Haryana.

Table 3: Statistical summary of groundwater level data (n = 40)

S.No.

 

Pre - Monsoon

Post - Monsoon

May 2011

May 2012

May 2013

May 2014

May 2015

Nov 2011

Nov 2012

Nov 2013

Nov 2014

Nov 2015

1.

Min

2.0

2.5

3.1

2.0

3.0

1.3

2.2

0.9

1.9

2.4

2.

Max

25.7

27.1

29.1

27.9

32.5

24.8

26.1

29.1

26.7

38.1

3.

Average

8.2

9.3

9.7

9.7

10.6

7.9

9.4

8.8

9.2

10.6

4.

Std. Dev

5.8

6.1

6.1

5.8

6.3

5.6

5.9

5.7

5.6

7.1

*readings are in ‘meter below ground level’ (mbgl).

As per the data presented in table 5, it has been found that during May 2011 to November 2015 out of 40 wells the rise in water level was observed in 4 wells while in 36 wells there was fall in water level.  Out of 36 declining wells, in 12 wells water level decreased between 0.0-2.0 mbgl; in 19 wells it decreased between 2.1-5.0 mbgl; in 3 wells it decreased between 5.1-10.0 mbgl and a decline of more than 10.0 mbgl was observed in 1 well during years 2011-2016. In pre-monsoon season, water levelrise was found in 5 wells while 35 wells have shown a decline. Out of these 35 wells, in 8 wells water level decreased between 0.0-2.0 mbgl, in 20 wells it decreased between 2.1-5.0 mbgl and in 5 wells it decreased between 5.1-10.0 mbgl. During the post-monsoon season, groundwater level rise was observed in 4 wells and a fall was observed in 36 wells. Out of these 36, 13 wells shown have decrease of 0.0-2.0 mbgl; 15 wells have shown decrease of 2.1-5.0 mbgl; 5 wells shown decrease of 5.1-10.0 mbgl and more than 10.0 mbgl decrease were observed in 1 well. The rate of decline in shallow well is faster than the deeper wells as decrease of 50% and 84.6% in pre-monsoon and post-monsoon seasons, respectively was found in well having minimum water level and the well having maximum water level has decrease by 26.3% and 53.6% in pre-monsoon and post-monsoon seasons, respectively.

Table 4: Percent seasonal change in groundwater level during 2011-15 in Mewat (n = 40)

S.No.

 

Pre-monsoon

Post-monsoon

Difference in water level during 2011-15

% decrease in water level

Difference in water level during 2011-15

% decrease in water level

1.

Min

1.0

50.0

1.1

84.6

2.

Max

6.8

26.3

13.3

53.6

3.

Average

2.4

29.0

2.7

35.2

*readings are in ‘meter below ground level’ (mbgl).

Table 5: Quantification of groundwater level data (n = 40)

S.No.

 

No. of wells showing increased GW level

No. of wells showing decreased GW level

No. of wells under different declining limits (mbgl)

0.0-2.0

 

2.1-5.0

5.1-10

> 10

1

Overall Status of wells

4

36

12

19

3

1

2

Pre-Monsoon decrease in groundwater level

5

35

8

20

5

0

3

Post-Monsoon decrease in groundwater level

4

 

36

13

15

5

1

4

Pre-Monsoon annual rate of decrease in groundwater level

5

35

35

0

0

0

5

Post-Monsoon annual decrease in groundwater level

4

36

36

0

0

0

 

Total Dissolved Solid (TDS)


The results obtained for Total Dissolved solids (TDS) data of 40 wells in Mewat, Haryana during period of 2011-15 for pre-monsoon and post-monsoon season is given in Fig. 4 and Tables 5-8. As evident from the figure 4, TDS in most of wells is almost constant but decline is also observed in some wells. The TDS is found to decrease after the rainfall events. In pre-monsoon season, the rainfall is very less or negligible except in May 2014, where the level of the groundwater has also raised above due to recharge in aquifers. In post-monsoon season, decrease in TDS is observed for most of the wells.

Table 6: Statistical summary of TDS data (n = 40)

S.No.

 

Pre - Monsoon

Post - Monsoon

May 2011

May 2012

May 2013

May 2014

May 2015

Nov 2011

Nov 2012

Nov 2013

Nov 2014

Nov 2015

1.

Min

321

326

376

409

440

298

326

357

390

470

2.

Max

8170

8930

7480

7290

7170

8800

8880

7120

6920

7220

3.

Average

2019

2080

1875

1923

1952

2291

2470

1872

1835

1933

4.

Std. Dev

1820

2111

1550

1508

1476

2305

2363

1448

1408

1461

*readings are in ‘parts per million’ (ppm)
 

Fig. 4. Variations in TDS for pre & post monsoon seasons for the period 2011-15 


Figure 4: Variations in TDS for pre & post monsoon seasons for the period 2011-15
Click here to View figure


It is clearly indicated from figure 4 that during pre-monsoon season TDS is high but it comes down during the post-monsoon season. In 2014, TDS for all the wells was found near or below 3000 ppm, except 4 wells namely, Panchayati Dholposh Kua, kabristan well, Khalid well and Bari masjid well. In Kabristan well and Panchayati Dolposh Kua TDS is recorded more than 6000 ppm (Figure 4) in spite of high rains. Table 5 indicated that the minimum values of TDS for pre-monsoon and post-monsoon seasons which shown an increase of 37.7 and 57.7, respectively but the maximum and average values of TDS in groundwater has actually decreased. This may be due to the reason that the saline zone is increasing and intruding into fresh water zone1.

Table 7: Percent seasonal change in TDS during 2011-15 in Mewat (n = 40)

S.No.

Pre-monsoon

Post-monsoon

 

Difference in TDS between 2011-15

%  increase/decrease in TDS

Difference in TDS between 2011-15

%  increase/decrease in TDS

1.

Min

119

37.1

172

57.7

2.

Max

-1000

-12.2

-1580

-18.0

3.

Average

-67

-3.3

-358

-15.6

*readings are in ‘parts per million’ (ppm).

Table 8: Quantification of TDS data (n = 40)

S.No.

 

No. of wells showing decrease in TDS

No. of wells showing increase in TDS

No. of wells under different increment limits (ppm)

(0–200)

 

(201-500)

(501-1000)

> 1000

1

Overall Status of wells

11

29

7

14

3

5

2

Pre-Monsoon decrease in TDS

12

28

6

16

2

4

3

Post-Monsoon decrease in TDS

14

 

26

7

14

4

1

4

Pre-Monsoon annual rate of decrease in TDS

12

28

22

4

1

0

5

Post-Monsoon annual rate of decrease in TDS

14

26

25

0

1

0


As per the data presented in Table 8, overall decrease in TDS during years May, 2011 to November, 2015 found in 11 wells and an increase is observed in other 29 wells. Out of which these 29, 7 wells have shown an increase of 0-200 ppm in TDS; 14 wells have shown increase of 201-500 ppm, 3 wells have shown increase on 501-1000 ppm and more than 1000 ppm increase was observed in 5 wells. In pre-monsoon season, 12 wells have a decreased TDS in 2015 as compared to year 2011, while 28 wells have shown an increase in TDS in 2015 as compared to 2011. In 6 wells, TDS have increased between 0-200 ppm, in 16 wells it increased between 201-500 ppm, in 2 wells it increased between 501-1000 ppm and in 4 wells it increased more than 1000 ppm. In post-monsoon season, TDS decreased in 14 wells and it increased in remaining 26 wells. Increased TDS values have between 0-200 ppm found in 7 wells, between 201-500 ppm in 14 wells between 501-1000 ppm in 4 wells have and more than 1000 ppm in 1 well. Increase in salinity during the years 2011-2015 in about 12% of wells in not good for the groundwater quality. Detailed study may be carried out in this areas to find out the water quality index as developed by Singh et al. (2015)27; which was used by Krishan et al.28-33 for evaluating the groundwater quality in some parts of Uttar Pradesh, Gujarat and Punjab.

Conclusion

In the present study, it has been observed that the groundwater is declining in some wells due to high extraction, low rainfall, and variable geographical conditions as fresh water sources are mostly situated along the steeper Aravalli hills. High salinity is found in some areas and is reported to intrude the fresh water zones1. Over-exploitation is resulting in the intrusion of saline groundwater towards the fresh groundwater, speeding up the depletion fast by 300-500 mm every year34. The groundwater in many wells which previously contained freshwater has now salinized. The new innovative technique of creating a pool of fresh groundwater within a saline aquifer is developed by the Sehgal foundation at a school and they are further planning to replicate the model for expansion and utilizing benefit of the same35. This will require groundwater level and TDS data for estimation of physio-chemical parameters at Mewat district which lacks freshwater aquifers and few which are slowly moving towards turning saline. Since, the problems due to water scarcity and salinity in groundwater are more visible in the district; this study is fundamentally very useful for further investigations and research towards finding solutions of water issues at Mewat.

Acknowledgement

The authors would like to thank Director, National Institute of Hydrology, Roorkee for all support and encouragement. The support received from Sehgal Foundation, Gurgaon and IIT-Roorkee is highly acknowledged.

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