Arsenic Problem
in Ballia District, A Road Map for Mitigation of Problem
Arsenic in the ground water is a
worldwide problem as about 150 million people are at risk and more than 70
countries are suffering from this havoc. Arsenic is a carcinogen and
responsible of various types of cancers. This problem is more wide spread in
middle and lower Ganga Basin, as the source of arsenic is the
Himalayas and arsenic will be found in all those areas, in varying quantities,
where Himalaya-fed rivers flow. Ballia District of UP is also
suffering with this problem. A report by Prof Dipanker Chakraborty,
director at the School of Environment Studies at Jadavpur University who has
carried out extensive work in the arsenic affected parts of UP, Bihar and Bangladesh,
has said that in places where there is large-scale withdrawal , groundwater
gets aerated and the arsenic compounds present in the water get degraded by the
oxygen. Arsenic also has an affinity for iron, so arsenic- laced water will
usually have a yellow tinge due to the presence of iron. In Ballia district
during 1994-2009, there has been an increase of 40%
in tubewell irrigated area which indicate the extent of withdrawal of ground
water. A team of Imran Ali, Atiqur Rahman, Tabrez Alam Khan, Syed Dilshad Alam,
Joheb Khan, of Jamia Millia Islamia, New Delhi, conducted a study in 2010 to study the extent of arsenic contamination by using chemical
data and GIS application (Ali et al., 2012). 100 samples were collected from deep, medium
and shallow aquifer twice in pre-monsoon (April, 2010) and post-monsoon seasons
(December, 2010). The samples were analyzed by atomic absorption spectrometer
and correlated with geological features. The correlation between arsenic
contamination with geological features and seasonal variation were analyzed by GIS.
An analysis of their results indicated following:
1.
The arsenic
contamination increases as the width of Doab is decreasing i.e. from west to
east.
2.
The blocks which
have zero irrigated area from canal have more arsenic contamination.
3.
The arsenic level
is lower in deeper aquifer.
4.
No much seasonal
variation has been observed in that year but this may be due to poor rainfall
during monsoon 2010, only 511 mm against normal of 983 mm. Due to this no
recharge could have taken place.
In view of this,
following short term, medium term and long term measures are suggested:
Short term
1.
Arsenic filter
developed by Jadavpur University should be provided to villages with priority
to blocks located in eastern part of district.
2.
All hand pumps
should be deepened to extract water only from deep aquifer. This will take care
of arsenic problem in western and central part to a good extent.
Medium term
1.
As the
non-presence of canal has shown higher arsenic concentration which indicates
that the recharge to ground water reduces the concentration. Due to non
maintenance of village ponds, most of them have silted up and thus the recharge
capacity of these have reduced significantly. Thus all ponds should be desilted
and their original capacity should be restored. This will facilitate recharge
of ground water and subsequent reduction in arsenic concentration. The MANAREGA
funds can be used for this purpose.
Long term
1.
Since the deep
aquifer will be tapped for both drinking as well as irrigation purposes, there
is need to develop a ground water recharge plan to this aquifer. The water
balance of the ground water aquifer should be studied and the amount of water
withdrawn every year should be recharged back. This will improve the quality in
long run and will reverse the deterioration process of water quality.
Ref.: Imran Ali, A. Rahman,
T. A. Khan, S. D. Alam, J. Khan. 2012. Recent
Trends of Arsenic Contamination in Groundwater of Ballia District, Uttar
Pradesh, India Gazi
University Journal of Science GU J Sci 25(4):
853-861
Table 1 Arsenic levels in ground water in different blocks
of Ballia district
Sl. No.
|
Block
|
Pre-monsoon 2010
|
Post monsoon 2010
|
||||
Shallow
|
Medium
|
Deep
|
Shallow
|
Medium
|
Deep
|
||
1.
|
Belthra Road
|
14-180
|
30-120
|
6-60
|
23-180
|
10-130
|
2-102
|
2.
|
Nagra
|
14-180
|
30-120
|
6-60
|
23-180
|
10-130
|
2-102
|
3.
|
Rasra
|
14-180
|
30-120
|
6-60
|
23-180
|
10-130
|
2-102
|
4.
|
Chilkahar
|
14-180
|
30-120
|
6-60
|
23-180
|
10-130
|
2-102
|
5.
|
Pandah
|
14-180
|
30-120
|
6-60
|
23-180
|
10-130
|
2-102
|
6.
|
Navanagar
|
180-360
|
121-310
|
61-155
|
181-360
|
131-250
|
103-203
|
7.
|
Maniyar
|
361-540
|
211-300
|
116-176
|
361-540
|
251-370
|
204-304
|
8.
|
Gadhwar
|
181-360
|
121-310
|
61-115
|
181-360
|
121-310
|
61-115
|
9.
|
Beruarbari
|
181-360
|
121-310
|
61-115
|
181-360
|
121-310
|
61-115
|
10.
|
Hanumanganj
|
181-360
|
121-310
|
61-115
|
181-360
|
121-310
|
61-115
|
11.
|
Sohaon
|
361-540
|
211-300
|
116-176
|
361-540
|
211-300
|
116-176
|
12.
|
Bansdih
|
541-720
|
301-390
|
177-237
|
541-720
|
301-390
|
177-237
|
13.
|
Dubhad
|
541-720
|
301-390
|
177-237
|
541-720
|
301-390
|
177-237
|
14.
|
Belhari
|
721-820
|
391-450
|
238-300
|
721-820
|
391-450
|
238-300
|
15.
|
Reoti
|
541-720
|
301-390
|
177-237
|
541-720
|
301-390
|
177-237
|
16.
|
Baria
|
721-820
|
391-450
|
238-300
|
721-820
|
391-450
|
238-300
|
17.
|
Murli chapra
|
721-820
|
391-450
|
238-300
|
721-820
|
391-450
|
238-300
|
(1) Shallow (0-80 feet), (2) Medium (81-120 feet), and (3) Deep
aquifer (above 120 feet).
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