TECHNICAL REPORT SERIES: D
No.:
CENTRAL GROUND WATER BOARD MINISTRY OF WATER RESOURCES GOVERNMENT OF INDIA
REPORT ON SPECIAL STUDY ON ARSENIC CONTAMINATION IN GROUND WATER OF DHEMAJI DISTRICT, ASSAM ANNUAL ACTION PLAN (AAP) 2006 - 2007
BY
DR. INDRANIL ROY
CENTRAL GROUND WATER BOARD NORTH EASTERN REGION GUWAHATI 2010
For Official Use Only
CENTRAL GROUND WATER BOARD MINISTRY OF WATER RESOURCES GOVERNMENT OF INDIA
REPORT ON SPECIAL STUDY ON ARSENIC CONTAMINATION IN GROUND WATER OF DHEMAJI DISTRICT, ASSAM ANNUAL ACTION PLAN (AAP) 2006 - 2007
By DR. INDRANIL ROY SCIENTIST - B
CENTRAL GROUND WATER BOARD NORTH EASTERN REGION GUWAHATI 2010 ii
For Official Use Only
CENTRAL GROUND WATER BOARD MINISTRY OF WATER RESOURCES GOVERNMENT OF INDIA
REPORT ON SPECIAL STUDY ON ARSENIC CONTAMINATION IN GROUND WATER OF DHEMAJI DISTRICT, ASSAM ANNUAL ACTION PLAN (AAP) 2006 - 2007
By DR. INDRANIL ROY SCIENTIST - B
Central Ground Water Board North Eastern Region Tarun Nagar, 1st Bye Lane, Guwahati, Assam
Central Ground Water Board Central Headquarter Bhujal Bhawan, NH IV, Faridabad, Haryana
Tel: (0361) 2456276 Fax: (0361) 2455497 Email:
[email protected]
Tel: (0129) 2419074 Fax: (0129) 2412524, 2413050 Gram: Bhumijal iii
FOREWORD
i
EXECUTIVE SUMMARY Present study of Arsenic contamination in ground water of Dhemaji District was undertaken as part of AAP 2006-07. The theme of the work was to establish the presence of arsenic in ground water of Dhemaji District and to relate its distribution with hydro-geological set up of the area in the context of present and future ground water utilization. The investigation also aimed towards understanding the cause of arsenic contamination and its spatio-temporal variation and its effect on residing population. Study confirms about presence of arsenic in the Dhemaji district. However, distribution of arsenic is not uniform and con controlled by complex interaction of existing geologicalhydrogeological set up with climatic condition. Study of geology of the area indicates a complex depositional environment. It indicates variation in nature of aquifer both in lateral and vertical directions. In contrast to earlier conceived double-aquifer model, present study indicates about a mono-aquifer system with intermittent clay lenses/layers which may extend for considerable distance. A continuous separating layer is absent in the area. Ground water in the area occurs under water-table condition and locally under semiconfined condition. Water table contour maps indicate that ground water flows from north to south. Depth to water level varies from 0.01 m bgl to more than 9.4 m bgl during pre-monsoon period (April, 2006) and from 1.84 m bgl to more than 9.63 m bgl during post-monsoon period (November, 2006). The post-monsoon water level trends always show slightly rising trend, where as during pre-monsoon it is rising in some places and falling in some places. However, pre-monsoon falling trend is typically associated with more urban setup and rising trends are associated with rural setup. Arsenic concentration is high in the west-central part of the district. Along with earlier identified Dhemaji and Sisiborgaon blocks, Bordoloni block is also highly affected. On the other hand, Murkong Selek T.D. Block is list affected. Spatially arsenic values vary widely as well as seasonally. During pre-monsoon the range is BDL to 249 ppb and that during post monsoon is BDL to 109.5 ppb. Relation between Pre-monsoon and Post-monsoon concentrations of As is not well defined, though overall higher concentration during pre-monsoon season is indicated. However, for iron, the relation is well defined (correlation coefficient 0.78) with overall higher concentration during pre-monsoon season. Study also indicates that anomalous concentrations of As and Fe are not directly correlatable, however effect of pH on concentration may have significant bearing. Comparison of concentrations with depth of well for both pre- and post-monsoon seasons (Figure 3.4.1 and 3.4.2) shows that concentration of As and Fe is most at about 10 m depth. This is
ii
correlatable with geological model. Site-specific depth-wise comparison of As and Fe concentration using hand-pumps and deep tubewells of same location also indicate prevalence of As and Fe at shallower depth. Results of survey about food and drinking water use habit indicate that in both low and medium income groups, consciousness about drinking water is present. Use of hand-pump water and filtering is everybody’s practice. In food, high intake of green vegetable with moderate to high intake of fish and meat may prevent ill effects of arsenic. However, skin disease is common and present in about 10% people. Field eexperimental results show use of domestic filter effectively reducing arsenic level in water. These filters are in common use due to high concentration of iron in water. Study shows that for arsenic removal is about 90% and that for iron is about 98%, which is most probably result of co-precipitation of As with Fe under oxidizing environment.
iii
Acknowledgements I would like express my sincere gratitude to Shri G. C. Saha, Saha Regional Director, CGWB, NER, Guwahati for kindly accepting my report on Arsenic contamination in ground water of Dhemaji District for publication. I would also like express my sincere gratitude to Shri D. B. Saha, Saha the then Regional Director, CGWB, NER, Guwahati for being kind enough to allow me to complete the work and guiding me through out. My sincere gratitude also goes to Dr. P. N. Rao, Rao Sc. D who provided his able guidance and supervision towards the work. I would like to express my sincere appreciation to Sh. Sh. B. Roy, Roy field officer responsible for ground water exploration work and conducted earlier surveys on ground water situation of Dhemaji District, whose reports I have consulted most. I would also like to extend my appreciation to Staffs of Chemical laboratory of CGWB, SR, Hyderabad for providing analysis of Arsenic samples. I would like to extend my appreciation to Dr. S. S. Singh, Singh Ms. D. Rabha, Sh. N. Chusi, Chusi, Sh. R. K. Kalita, Sh. S. S. Hembrom, Hembrom, hydrogeologists, and Sh. K. S. Rawat, Rawat chemist who helped me throughout the work. Last but not the least I would like to express my sincere thanks to all the officers, drivers, and staffs of the North Eastern Region, Guwahati, who have extended their support for carrying out the work. Without the team effort and support, completion of the work would not have been possible.
(Dr. Dr. Indranil Roy) Roy
iv
CONTENTS Page No.
FOREWORD
I
EXECUTIVE SUMMARY
II-III
ACKNOWLEDGEMENTS
IV
CONTENTS
V-VIII
ABBREVIATIONS CHAPTER
IX
1
INTRODUCTION
1-8
1.1
Purpose and Scope
1
1.2
Background
1
1.3
Location and Extent of the Study Area
3
1.4
Nature and Composition of Affected Population
3
1.5
Drinking Water Scenario
5
CHAPTER
2
HYDROGEOLOGICAL SETUP 2.1
9-26
Geomorphology
9
2.1.1 Drainage System
10
2.1.2 Soil Type
14
2.2
Geology
15
2.3
Hydrogeology
16
2.4
2.3.1 Aquifer Geometry
16
2.3.2 Aquifer Parameters
17
2.3.3 Groundwater Occurrence and Movement
20
2.3.4 Groundwater Level Trend Analysis
20
Hydrometeorology
25
CHAPTER
3
CHEMICAL QUALITY OF GROUND WATER
27-45
3.1
Nature and distribution of Key Sampling Wells
27
3.2
Sampling Methodology
30
3.3
Distribution of Arsenic and Iron
31
3.4
Depth variation of Arsenic and Iron
39
3.5
Effect on Human Health
43
3.6
Effect of filtering on Arsenic and Iron
44
CHAPTER
4
SUMMARY AND RECOMMENDATIONS
46-49
4.1
Summary
46
4.2
Recommendations
47
BIBLIOGRAPHY
50
ANNEXURES
v
List of Tables Page No. Table 1.2.1 Table 1.3.1 Table 1.4.1 Table 1.4.2 Table 1.5.1 Table 1.5.2 Table 2.1.1 Table 2.1.2 Table 2.1.3 Table 2.3.1 Table 2.3.2 Table 2.4.1 Table 2.4.2 Table 3.1.1 Table 3.1.2 Table 3.1.3 Table 3.3.1 Table 3.3.2 Table 4.5.1
Summary of results of study conducted PHED, Govt. of Assam Administrative Setup Population Pattern (Census 2001) Block-wise population (Census 2001) Water supply schemes (Groundwater spot source) Drinking water source (Census 2001) Geomorphological classification of the area Soil types present in the area Soil texture of the area Summarized hydrogeological data of wells constructed by CGWB Trend of Water levels in GWMS Wells Block-wise average annual rainfall Monthly Rainfall (in mm) 1994 to 2006 Number of KSW based on well type Number of KSW based on location Number of KSW based on geology and geomorphology Block-wise range of Arsenic values (in ppb) Block-wise range of Iron values (in ppm) Summary of survey results
vi
2 3 5 5 5 8 9 14 14 17 20 25 25 27 27 27 31 31 43
List of Figures Page No. Fig. 1.3.1 Fig. 1.5.1 Fig. 2.1.1 Fig. 2.1.2 Fig. 2.1.3 Fig. 2.2.1 Fig. 2.3.1 Fig. 2.3.2 Fig. 2.3.3 Fig. 2.3.4 Fig. 2.3.5 Fig. 2.4.1 Fig. 2.4.2 Fig. 3.1.1 Fig. 3.1.2 Fig. 3.2.1 Fig. 3.3.1 Fig. 3.3.2 Fig. 3.3.3 Fig. 3.3.4 Fig. 3.3.5 Fig. 3.3.6 Fig. 3.3.7 Fig. 3.3.8 Fig. 3.4.1 Fig. 3.4.2 Fig. 3.4.3 Fig. 3.4.4 Fig. 3.4.5 Fig. 3.6.1 Fig. 3.6.2
Administrative Map of Dhemaji district, Assam Source of drinking water to households (Census 2001) Natural Colour Imagery of Dhemaji district, Assam (source: maps.google.com) Geological – Geomorphological map of Dhemaji district, Assam Drainage map of Dhemaji district, Assam Lithologs generated by drilling of CGWB at A) Tarajan and B) Uriumguri Fence diagram representing aquifer geometry of Dhemaji district, Assam Pre-Monsoon depth to water level Map Post-Monsoon depth to water level Map Hydrograph of GWMS Wells Hydrograph of GWMS Wells Distribution of monthly rainfall Variation in annual rainfall Key sampling wells locations Distribution of Key sampling Wells shown on Terrain map (Terrain map source: map.google.com) Comparison of analytical results of As Pre-monsoon distribution of Arsenic concentration Post-monsoon distribution of Arsenic concentration Pre-monsoon distribution of Iron concentration Post-monsoon distribution of Iron concentration Relationship between Pre-monsoon and Post-monsoon concentrations Scatter plot of As vs. Fe Scatter plot of pH vs. As (Pre-Monsoon) Scatter plot of pH vs. Fe (Pre-Monsoon) Depth vs. Concentration for As and Fe during Pre-monsoon Season Depth vs. Concentration for As and Fe during Post-monsoon Season East-west profile of hand-pump depth Comparison of As content in Deep and shallow wells Comparison of Fe content in Deep and shallow wells Schematic diagram of home-made filter Comparison of raw water sample and 24 hrs filtered water sample
vii
4 7 11 12 13 18 19 21 22 23 24 26 26 28 29 30 32 33 34 35 36 37 38 38 39 39 40 41 42 44 45
List of Annexure ANNEXURE I
Details of Key Sampling Wells established in Dhemaji District
ANNEXURE II
Details of Hydrograph Network Stations in Dhemaji District
ANNEXURE III
Lithologs of boreholes drilled in Dhemaji District by Central Ground Water Board
ANNEXURE IV
Selected lithologs of boreholes drilled in Dhemaji District by Private Agencies
ANNEXURE V
Results of chemical analysis of samples from key sampling wells
ANNEXURE VI
Results of chemical analysis of duplicate water samples
ANNEXURE VII
Results of chemical analysis of filtered water samples
ANNEXURE VIII
Results of survey on food habit and drinking water
ANNEXURE IX
Selected Standards for Physical, Chemical and Biological quality of Drinking Water
Abbreviations agl bdl bgl bmp CGWB CT CWC DTW GWMS IMD Km/km km2 LPCD M or m MCM MGD mg/l MLD nd NHNS PHED ppb ppm Sq. km.
: : : : : : : : : : : : : : : : : : : : : : : :
Above Ground Level Below Detection Limit Below Ground Level Below Measuring Point Central Ground Water Board, Govt. of India Census Town Central Water Commission Depth to Water Level Ground Water Monitoring Station Indian Meteorological Department Kilometer Square kilometer Litres Per Capita per Day Meter Million Cubic Meters Million Gallons per Day milligram per litre Million Litres per Day No Data National Hydrographic Monitoring Station Public Health Engineering Department, Govt. of Assam Parts per billion Parts per million Square Kilometer
viii
Chapter 1
INTRODUCTION 1.1
Purpose and Scope Arsenic contamination in the groundwater of the upper Brahmaputra plain in Assam was
reported In January 2004 by School of Environmental Studies, Jadavpur University. Public Health Engineering Department, Govt. of Assam (PHED) also confirmed the claim about the presence of Arsenic (As) in groundwater. Based on these reports, Central Ground Water Board, North Eastern Region (CGWB, NER) started their own studies. Present study of Arsenic contamination in ground water of Dhemaji District was undertaken as part of AAP 2006-07. The theme of the work was to establish the presence of arsenic in ground water of Dhemaji District and to relate its distribution with hydro-geological set up of the area in the context of present and future ground water utilization. The investigation also aimed towards understanding the cause of arsenic contamination and its spatio-temporal variation and its effect on residing population.
1.2 Background Arsenic can impact human health through the ingestion of contaminated ground water. Astolfi et al.(1981) showed that regular intake of drinking water containing more than 0.1 mg/l of As leads to clearly recognizable signs of arsenic toxicity and ultimately in some cases to skin cancer. The most commonly observed symptoms of chronic arsenic poisoning are melanosis, hyperkeratosis, anemia, respiratory diseases and hepatomegaly. In severe cases, gangrene in the limbs and malignant neoplasm occurs (Cebrian et al., 1983). The contamination of groundwater with arsenic is one of the serious problems encountered in developing countries. Bangladesh is one of the worst sufferers at present time; however India is also coming up in the world arsenic map. The source of geogenic arsenic in groundwater has always remained a debatable issue. Review of geochemistry of arsenic by Thornton (1996) indicates that As is main constituent of around 200 mineral species. Out of them, 60% are arsenates, 20% are sulphides and sulphosalts and the remaining 20% includes arsenides, oxides, and silicates. Hence, anomalous presence of any of these minerals in aquifer matrix can rise the As level of groundwater depending on oxidation level. Welch et al. (1999) summarized that widespread high arsenic concentrations in ground water most commonly result from a) up-flow of geothermal water, b) dissolution of, or desorption from, ironoxide, c) dissolution of sulfide minerals, and d) evaporative concentration. Arsenic release from 1
iron oxide appears to be the most common cause of widespread arsenic concentrations exceeding 10 mg/L in ground water. This can occur in response to different geochemical conditions, including release of arsenic to ground water through reaction of iron oxide with organic carbon. Iron oxide also can release arsenic to alkaline ground water (Welch et al., 1999). As mentioned earlier, arsenic contamination in the groundwater of Dhemaji district, Assam was first reported by School of Environmental Studies, Jadavpur University in 2004. The report showed that among 241 analyzed hand tubewell water samples from Dhemaji and Karimganj districts of Assam, 42.3% of the samples contained arsenic above 10 µg/l and 19.1% above 50 µg/l (http://www.soesju.org/arsenic/arsenicContents.htm as on 30/11/2008). Public Health Engineering Department, Govt. of Assam (PHED) also confirmed the claim. Result of their study has been summarized in Table 1.2.1. Based on this study, PHED declared Sisiborgaon as most affected block in the district. However, it is also worth mentioning that there existed some variation in results about severity of contamination level between the studies conducted by PHED and School of Environmental Studies. Table 1.2.1 Summary of results of study conducted by PHED, Govt. of Assam Block Name Sisiborgaon
Dhemaji
Bordoloni Murkong Selek
Number of As infected Habitation
Gaon Panchayat Sisiborgaon Akajan Kulajan Muktiar Silasuti Simenmukh Amguri Sripani Nilakh Moridhal Lakhipathar Moridhal Aridhal I Bishnupur Missamari Simenchapori Jonai Telem Bahir Jonai
21 6 4 9 11 11 2 2 1 2 6 4 5 2 1 1 1 1 1 District Total =
Total
69
46 1
24 140
Based on these reports, Central Ground Water Board, North Eastern Region (CGWB, NER) started their own studies. Roy (2005-06) conducted a preliminary survey in the district. However
2
the study remained inconclusive as the analytical results have showed wide variability. As a followup of the study, the present study of arsenic contamination in ground water of Dhemaji District was undertaken. However, earlier G. V. Reddy (1997-98) and B. Roy (2004-05) have carried out reappraisal surveys in the district for CGWB.
1.3 Location and extent of the study area Dhemaji district is the eastern-most district of Assam, bounded by East Siang and West Siang districts of Arunachal Pradesh in the north, by North Lakhimpur district in west and south and by mighty Brahmaputra River in west and southwest directions. Geographically the district extends within North latitude 27º15′ to 28º00′ and East longitude 94º15′ to 95º30′ and is represented by the Survey of India Degree-sheet 83 I and 83 M. The total geographical area of the district is 3237 sq. km. Two civil sub-divisions, namely 1) Dhemaji and 2) Jonai constitute Dhemaji district. The details of administrative set-up are given in the Table 1.3.1. Administrative map of the district is given in Figure 1.3.1. Table 1.3.1 Administrative set-up Sl. No.
Civil Subdivision
Circle Bordoloni
1.
2.
Dhemaji
Jonai
Block
Geographical area (sq. km)
Number of villages
Bordoloni
478.28
208
Dhemaji
409.49
280
Machkhowa
304.41
51
Sisiborgaon
Sisiborgaon
933.01
395
Jonai
Murkong Selek
1111.81
381
Dhemaji
1.4 Nature and Composition of affected population As per 1991 census, total population of the district is 478830 and that of as per 2001 census is 569971. Among this, S.T. & S.C. population (includes Mishings, Sonowal, Kacharis, Bodos, Deoris, Lalungs, Hazongs, etc.) is about 47.29% and 5.33% of the total population respectively. There is also a huge chunk of Other Backward Classes (OBC) population comprising of Ahoms, Chutiyas, Konches etc. Total population in rural area is 530138 and urban area is 39330. The urban population is only 1.85% of total, which highlights the predominantly rural character of the district. The rate of growth of population in the district between 1971 and 1991 was 104.48%, and between 1991 and 2001 was 64%. The annual rate of growth of population is 5.22% compared to the overall state growth of 2.62%. Average population density of the district is 176/km2. The status of the population for the district is given in Table 1.4.1 and 1.4.2.
3
4
Fig.1.3.1 Administrative Map of Dhemaji district, Assam
Table 1.4.1 Population pattern (Census 2001) Dhemaji Sub Division
Jonai Sub Division
District Total
Male
2,21,640
72,464
2,94,108
Female
2,09,565
65,798
2,75,363
Total
4,31,205
1,38,262
5,69,971
Particulars
Table 1.4.2 Block-wise population (Census 2001) Area
Total Population
Population Density
Dhemaji
409.49
111154
271.4
Machkhowa
304.41
26657
87.6
Bordoloni
478.28
94898
198.4
Sisiborgaon
933.01
161657
173.3
Murkong Selek
1111.81
143199
128.8
Block
Earlier studies by PHED indicated that arsenic contamination is mostly concentrated in Sisiborgaon and Dhemaji block. As about 272811 persons reside within the most affected area, this indicates that at least about 51% of district population is at risk.
1.5 Drinking water scenario With development of the district in the face of changing time, dominance of ponds and surface water bodies for domestic usage has changed to use of hand pumps and supply water by Public Health Engineering Department (PHED). Hence, the dependence pivoted from surface water to groundwater. At present major part of the water supply in the town areas and in parts of rural areas comes from the PHED water supplies. As per PHED reports, about 14.5% of total population is covered by piped water supply (PHED, 2003; Pers. Comm. 2006). A list of operating public water supply schemes under PHED Dhemaji and Jonai subdivisions with population covered are given in Table 1.5.1. However the supplies in rural areas are not reliable. Table 1.5.1 Water supply schemes (Groundwater spot source) Sl. No.
PHED Sub-division
Block
Name of scheme
Gaon panchayat
1
Dhemaji
Dhemaji
Dhemaji
Aradhal
2
Dhemaji
Dhemaji
Bokabil
Uttar Dhemaji
1968
3
Dhemaji
Dhemaji
Naroathan
Naroathan
1650
5
Population Covered 5277
Sl. No.
PHED Sub-division
Block
Name of scheme
4
Dhemaji
Dhemaji
Moridhol
Moridhol
2365
5
Dhemaji
Dhemaji
Batgharia
Batgharia
2275
6
Dhemaji
Dhemaji
Bherekichuck
Batgharia
1364
7
Dhemaji
Dhemaji
Panitola
Somorajan
1300
8
Dhemaji
Dhemaji
Chengalipathar
Hatigarh
1978
9
Dhemaji
Dhemaji
Dihingia Gaon
Aradhal
1400
10
Dhemaji
Dhemaji
Raichapori Dolopa
Uttar Dhemaji
1700
11
Dhemaji
Dhemaji
Matikhola
Dakshin Dhemaji
1594
12
Dhemaji
Dhemaji
Hatigarh
Hatigarh
1600
13
Dhemaji
Dhemaji
Dusutimukh Bongalmari
Khubulia
1628
14
Dhemaji
Dhemaji
Lakhipathar
Lakhipathar
2956
15
Dhemaji
Dhemaji
Norabil
Jiadhal
1798
16
Dhemaji
Dhemaji
Subahipathar
Lakhipathar
1200
17
Dhemaji
Dhemaji
Dhemaji (Civil Hospital)
Dakshin Dhemaji
-NA-
18
Jonai
Dhemaji
Nilakh
Nilakh
1700
19
Jonai
Murkong Selek
Jonai
Jonai
3500
20
Jonai
Murkong Selek
Chimenchapori
Chimenchapori
2400
21
Jonai
Murkong Selek
Ramdhan
Ramdhan
3600
22
Jonai
Murkong Selek
Laimekuri
Laimekuri
2500
23
Jonai
Murkong Selek
Round Miri
Somkang
1323
24
Jonai
Murkong Selek
Dekapam
Dekapam
2800
25
Jonai
Murkong Selek
Somkongpargo
Somkang
1700
26
Jonai
Murkong Selek
Dak Chapori
Dekapam
1400
27
Jonai
Murkong Selek
Telem
Telem
1730
28
Jonai
Murkong Selek
Borati
Dekapam
1500
29
Jonai
Murkong Selek
Majulipur
Majulipur
2314
30
Jonai
Murkong Selek
Luhit Kemera
-NA-
-NA-
31
Jonai
Murkong Selek
Royeng Kuli
-NA-
-NA-
32
Jonai
Murkong Selek
Bahir Chillai
Bahir Chillai
-NA-
33
Jonai
Murkong Selek
Bijoypur Namoni
Jonai (?)
-NA-
34
Jonai
Murkong Selek
Misamora
Chamkhang(?)
-NA-
35
Jonai
Sissiborgaon
Sissiborgaon
Sissiborgaon
1700
36
Jonai
Sissiborgaon
Bormukali Miri
Borlung
1500
37
Jonai
Sissiborgaon
Sripani
Sripani
1444
38
Jonai
Sissiborgaon
Dhunaguri
Borlung
1670
39
Jonai
Sissiborgaon
Chowkhamating
Sissiborgaon
1800
40
Jonai
Sissiborgaon
Silapathar
Silapathar
4240
41
Jonai
Sissiborgaon
Gelua
Kulajan
2127
42
Jonai
Sissiborgaon
Kulajan
Kulajan
1996
43
Jonai
Sissiborgaon
Bhagawan Borgorah
Dimow
1393
44
Jonai
Sissiborgaon
Chilla Block No1
Silasuti
1985
45
Jonai
Sissiborgaon
Chimenmukh
Chimenmukh
1273
46
Jonai
Sissiborgaon
Archi Borgorah
Dimow
1305
47
Jonai
Sissiborgaon
Chilly Assomiya
Dimow
1593
6
Gaon panchayat
Population Covered
Sl. No.
PHED Sub-division
Block
Name of scheme
Gaon panchayat
Population Covered
48
Jonai
Sissiborgaon
Chilla Block No2
Silasuti
-NA-
49
Jonai
Sissiborgaon
Akajan
Kulajan
-NATotal =
82,546
This indicate that PHED PWSS cover about 57779 persons in arsenic affected areas (i.e. Dhemaji and Sisiborgaon block) which is about 21% of total population of Dhemaji and Sisiborgaon block. However considering the operating condition and functionality, as observed in field during present study, only 10% of officially covered population are actually covered by those PWSS that also mainly restricted in urban setup.
Study of the Census 2001 (Table 1.5.2) data indicates that in Dhemaji district hand-pump is the most common source of drinking water to a household. In rural areas, the second most preferred source is tubewell followed by dugwells. In urban areas, tubewell and dugwells are nearly equally preferred. This indicates that irrigational tubewells are also used as drinking water source in rural areas. On the other hand availability of taps, which is indicative of supply water, is negligible. This also indicates about status of public water supply.
Urban Area
50,000
10,000
40,000
8,000 Household
Household
Rural A rea
30,000 20,000
6,000 4,000
10,000
2,000
0
0 Any other
Spring
7
River, Canal
Tank, Pond,
Well
Tubewell
Handpump
Tap
Any other
Spring
River, Canal
Tank, Pond,
Well
Tubewell
Handpump
Tap
Fig. 1.5.1 Source of drinking water to households (Census 2001)
Table 1.5.2 Drinking water source (Census 2001) Nature
Rural
Urban
Location
Total number of households
Source of drinking water Tap
Hand pump
Tubewell
Well
Tank, Pond, Lake
River, Canal
Spring
Any other
Total
89,385
1,072
38,328
17,916
14,122
6,494
10,051
359
1,043
Within Premises
25,448
316
13,243
5,598
3,707
2,542
0
0
42
Near Premises
40,267
504
17,424
8,218
6,723
2,384
4,776
106
132
Away
23,670
252
7,661
4,100
3,692
1,568
5,275
253
869
Total
8,120
193
6,097
956
788
18
18
1
49
Within Premises
3,475
112
2,707
360
288
5
0
0
3
Near Premises
4,141
63
3,067
538
446
12
3
1
11
504
18
323
58
54
1
15
0
35
Away
8
Chapter 2
HYDROGEOLOGICAL SETUP Dhemaji district represents the eastern-most part of the Brahmaputra Valley in northern bank. The area is bounded by the Himalayan mountain range in the north and east, by the Subansiri River in the west and the Brahmaputra River in the south. Geologically the area is a rift valley, which is filled up (up to 5000m thick) by Cretaceous, Tertiary and Recent sediments. The region is prone to earthquake. Relatively recent folding and uplift (Quaternary epoch) of the Brahmaputra sediments close to the intra-plate boundary redirected the course of the Brahmaputra to its present configuration (Lindsay et al., 1991).
2.1 Geomorphology Geomorphologically the district occupies a unique location, where steep slope of Eastern Himalayas abruptly drops to forming a narrow valley, which widens towards the western side. Marshy lands, swampy water bodies and floodwaters occupy about 300 sq. km. area of it. In general, slope of the area is from northeast to southwest. After the great earthquake in 1950 the Brahmaputra riverbed is rising continuously due to deposition of sand carried down from upstream. This has led to the formation of a saucer shaped low-lying zone in the plains of the district. A recent imagery of the area is given in Figure 2.1.1. Physiographically the study area can be broadly sub-divided into five generalized units as given in Table 2.1.1. The geological-geomorphological map is given in Figure 2.1.2.
Table 2.1.1 Geomorphological classification of the area Zone
Description
Geology
Hills
The hilly area in the northern part
Tipam Group (?) sandstone
Piedmont plane
The foothill zone in the northern and eastern parts
Older Alluvium
Alluvial plain
Covering the middle plain zone i.e. the saucer shaped built up zone. Innumerable beels and swampy areas are common features
Younger Alluvium
Active flood plain
Along the river Brahmaputra and other major tributaries
Recent Alluvium
Channel Bar
Loose sediments in the active channels
Bar Deposits/ Channel alluvium
9
Hills occur in the northern part of the district. The altitude of hills in the north of Subansiri Reserve Forest is about 950m, in north of Likabali is about 900m and at north of Depa is about 850m amsl. The altitude of similar hill ranges located north and northwest of Jonai is about 500m. Piedmont zones occur adjacent to these hills and also restricted in the northern part of the district. In this zone topography slopes towards southwest. Typically this zone always occurs below 122m amsl. On the other hand the alluvial plain, occurring between 105 and 96m amsl, gently rolls towards southwest in the eastern part of the area and towards south in the western part. The western part is characterized by courses of shifting streams with high rate of lateral erosion. The flood plain area is present along the Brahmaputra river bank and mainly restricted between 89m amsl and 96m amsl with gentle slope towards the river.
2.1.1 Drainage system Situated on the North Bank of the River Brahmaputra, the Dhemaji district is bounded by the Brahmaputra River in the South and Subansiri River in the West. In addition, a number of tributaries from the northern hill ranges join the Brahmaputra in this region. Drainage map of the district is given in Figure 2.1.3. Major tributaries of Brahmaputra are Silley, Sibia, Leko, Jonai Korong, Dikhari, Narod, Somkhong, Tongani, Burisuti, Simen,
Dimow, Gainadi,
Moridhal,
Jiadhal/Kumotia, Korha/Sila, Charikaria, Nonoi, Sampara Suti, Subansiri, etc. Of these, Jiadhal River originates in the hills of Subansiri Reserve Forest and flows through the eastern part of the district forming Barihul bill downstream and end at 5 km south of Ghilamora village; Kumotia River originates at Theckjori and flows through the eastern part of the district before culminating with Barihul bill. These two streams create water logged and marshy areas in Bordoloni block. Kanibill which is called Laipulia in down stream side and Sisi are two important rivers draining the central part of the district after originating in the hills near Gohaingaon and Baligaon respectively. Simen, Somkhong, Dikari, Royang and other major rivers that originate in the hills of East Siang district of Arunachal Pradesh, flow down through the eastern part of the district towards south ultimately joining the Brahmaputra.
Overall the drainage network of the area shows an anastomising pattern. Collectively, the rivers after coming down from hills show a marked tendency to move towards south-westerly direction. This tendency may indicate influence of underlying fracture pattern or this may due to paleochannels of the Brahmaputra river. This is also to be noted that Great Earthquake of 1950 severely disturbed the entire riverine system of the area and generated deranged drainage pattern. Individually, the rivers in the western part show dendritic drainage patterns and rivers of eastern part show parallel drainage pattern. However, river courses often change due to lateral erosion as well as successive changes in basement configuration due to earthquakes (Barman, 1981). 10
11
Fig. 2.1.1 Natural Colour Imagery of Dhemaji district, Assam (source: maps.google.com)
12
Fig. 2.1.2 Geological – Geomorphological map of Dhemaji district, Assam
13
Fig. 2.1.3 Drainage map of Dhemaji district, Assam
2.1.2 Soil Type General soil character of cultivable land in the district is mainly alluvial and composed of mixture of sand (coarse to fine) and clay of varying proportions. The soils of this district can be broadly classified into three different types viz. The foothill/Piedmont zone soils, active flood plain soils near the river Brahmaputra and the low-lying marshy land soils. A detailed taxonomic description is given in Table 2.1.2. Table 2.1.2 Soil types present in the area Geomorphic Zones
Old Type
Description
Taxonomic Name
Red Loamy
Deep, well drained, loamy sand/sandy loam soils occurring on very gently sloping piedmont plain having loamy surface with moderate erosion and slight flood hazard
Coarse loamy, typic fluvaquents,
Old Alluvial
Associated with deep, well drained, coarse silty soils occurring on very gently sloping concave plains having loamy surface with slight erosion and moderate flood hazard.
Coarse silty, Typic Haplaquents
New Alluvial
Deep, well drained, loamy sand/sandy loam soils occurring on very gently sloping flood plain, having loamy surface with moderate erosion and moderate flood hazard.
Coarse loamy, Aeric fluvaquents
New Alluvial
Associated with very deep, moderately well drained, clay loam or sandy clay loam soils occurring on level to nearly level flood plains with slight erosion and moderate flood hazard.
Fine loamy, Typic Haplaquepts
Piedmont
Alluvial plain/ Flood plain
Commonly foothill/Piedmont zone soil is highly acidic. However, new alluvial soils formed due to inundation of land by river contain more percentages of fine sand and fine silt and are less acidic. Such soils are often neutral and even alkaline. The rest large expanse of low-lying land is characterized by heavy clayish soil which shows high percentage of nitrogen. This soil is good for rice cultivation. The soil beside the Subansiri and Ranganadi rivers are sandy, coated with silt, which is good for cultivation of winter crops, such as raga, mustard, potato etc. Details of soil texture of cultivable land are given in Table 2.1.3. Table 2.1.3 Soil textures of the area Soil Texture
Area under cultivable land
Sandy loam
46% of the total cultivable land
Loamy
44% of the total cultivable land
Clayey
10% of the total cultivable land
14
In Brahmaputra Valley, the river current is swift and it is only the sandy portion that is mostly deposited instead of clays (Brahmaputra Board, 1964). This implies that the new alluvial soil (of SPL 1975 classification) is to be rich in fine sand content, which in turn indicates that this type of soil will have higher porosity.
2.2 Geology McLaren (1904) classified the Quaternary sediments of Brahmaputra valley into three major subdivisions, namely Bhangar (older alluvium), Khadar (newer alluvium), and Recent (deltaic deposits). Evans (1952) designated the high level alluvium and low-level alluvium with formation status and considered to be of Pleistocene and Recent age respectively (Mathur and Evans, 1964). Krishnan (1968) described the Pleistocene and Recent deposits to be composed of gravels, sands, and clays. The sands and gravels constitute the aquifers. Goswami (1960) opined that these Pleistocene deposits are commonly of fluviatile and occasionally sub-aerial in origin. However, later workers identified several cycles of deposition of Quaternary alluvium in Brahmaputra basin (Pathak, 2001; Rao & Pathak, 1989). In older alluvium, three cycles of deposition have been reported. Bounding surfaces have been deciphered mainly based on resistivity study. They are termed as terrace surface T5, T4, and T3. Oldest T5 unit is represented by reddish brown silty clay together with boulders, pebbles, gravels, and sand. T4 unit is primarily composed of orange brown silty clay and sand. On the other hand youngest T3 unit is composed of yellowish orange colour silty-clay and fine to medium sand. Similarly in younger alluvium also, three cycles of deposition has been identified namely as Alluvial fan deposit (T2), Terrace Alluvium (T1) and Channel alluvium (T0). However, in contrast to older alluvium, younger alluvium unit boundaries have been deciphered mainly based on morphometry. In the study area, alluvial formations may be broadly divided into four groups a) Older Alluvial Deposits; b) Younger Alluvial Deposits; c) Recent Alluvium; d) Channel Deposits/Bar Deposits. Morphologically older alluviums cover the piedmont plains and younger alluviums and recent alluviums forms younger alluvial plain and flood plain respectively. The older alluvial deposits mainly occupy northwestern part of the area with patchy occurrences in northern parts. It occurs in the north-west between Dirpai and Gobindapur village, west of Jiadhal River, in the north between Baruagaon and Silapathar and up to Depa in the northeast. These deposits are commonly found above 105 m amsl and continue up to foothill region. Older alluvial deposits comprise of boulders of sandstones and quartzites with cobbles, pebbles, gravel and sands. Department of Irrigation drilled few boreholes in these areas up to 30 m depths. These lithologs show that top 10 m comprises of boulders, cobbles, sands followed by coarse sand, pebbles, gravel and clays in the rest. The younger alluvial deposits are represented by unconsolidated sediments of gravel,
15
pebbles, fine to coarse sand and clays, occupying areas between 96 m and 105 m amsl elevations. The Recent alluviums covering flood plains exist below 96 m amsl elevations along the Brahmaputra riverbank which may extend up to 10 km inland and comprise of thick beds of alternating layers made up of gravels, pebbles, sands and clays. Two litholog generated by CGWB drilling is given in Figure 2.2.1. Geological map of the area is given earlier in Figure 2.1.1. Generalized geological succession of the area is given as below:
Neogene
Geological succession of the Study Area
┌ │ Recent │ │ │ │ │ │ │ │ Pleistocene │ │ │ │ Miocene └
┌ │ │ │ │ │ │ └
Channel Deposits/Bar Deposits
T0
Sand, Silt, Clay, Gravel
Recent Alluvium
T1
Clay, Fine to medium Sand
Younger Alluvial Deposits
T2
Clay, Coarse to Fine Sand, mixed with Gravels and Pebbles
---------Nonconformity------┌
│ Older Alluvial Deposits └
T4 – T6
Fine to Medium Sand, Clay, Gravel, and Boulder
---------Unconformity------Tipam Group (?)
Sandstone
2.3 Hydrogeology Hydrogeologically the area is covered by alluvial sediments of Quaternary age comprising of different grades coarse clastic sediments like sand, boulders, pebbles, cobbles, gravel of various origin locally differentiated by layers of clay and silt. All these formations act as good reservoir of ground water. In these formations ground water occurs under water table to semi-confined conditions. Depth to water level varies from 0.01 m bgl to more than 9.4 m bgl during pre-monsoon period (April, 2006) and from 1.84 m bgl to more than 9.63 m bgl during post-monsoon period (November, 2006).
2.3.1 Aquifer geometry The area so far has scantily been explored for groundwater. CGWB has constructed two exploratory well at the western peripheral part of the district. Details are given in Annexure III. Several deep tubewells has also been constructed by state governmental agencies like PHED for drinking water supply schemes, State Irrigational Directorate for irrigational purposes, etc. But in
16
these cases lithological data has been poorly preserved as exploration was not prime objective. Still attempt has been made to compile those data and given in Annexure – IV. A fence diagram of subsurface geology has been constructed with the help of those data (Figure 2.3.1). The study of the prepared fence diagram indicates a complex depositional environment. It indicates variation in nature of aquifer both in lateral and vertical directions. However in contrast to earlier conceived double-aquifer model, present study indicates about a mono-aquifer system with intermittent clay lenses/layers which may extend for considerable distance. A continuous separating layer is absent. At the eastern part of the area (Murkong Selek block) a clay layer (3-5m thick) is present at the top followed down by fine sand, coarse sand and boulder bed. This clay layer thin towards sisiborgaon-akajan area and towards north. At likabali, the clay is absent and fine sand is exposed. However, A second clay layer starts from akajan-kulajan area and thickens towards sisiborgaon-sripani area but again thins towards further west, moridhal area, and finally thins out at west of Dhemaji area. At deori-barbam area, graded sand starts from the surface. At the western extremity (Bordoloni block), clay lenses reappear which thins out towards north and goes at depth towards south. Interestingly, a boulder bed is present through out the district at various depths (20 to 30 m), which may be considered as a marker horizon. It has been observed that most of the water wells in the district end before reaching it.
2.3.2 Aquifer parameters As the area is scantily explored for groundwater, not much aquifer data is available. Summarized hydrogeological data of CGWB constructed exploratory wells at the western peripheral part of the district is given in Table 2.3.1.
Table 2.3.1 Summarized hydrogeological data of wells constructed by CGWB
Location
Depth (m)
Zone tapped (m bgl)
Slot Length (m)
SWL (m bgl)
Discharge (lpm)
Draw down (m)
T (m²/day)
P (m/day)
K (m/hr)
Borola Mirigaon
61.5
36-48 54-60
18
1.62
809.99
0.86
3283.20
74.62
126.9
59.5
26-29 32-38 42-46 49-54 58-59
19
1.25
745.64
2.45
9831.05
258.71
55.9
Mohori camp
T: Transmissivity; P: Permeability; K: Hydraulic conductivity;
17
Fig. 2.2.1 Lithologs generated by drilling of CGWB at A) Tarajan and B) Uriumguri
18
19
Fig. 2.3.1 Fence diagram representing aquifer geometry of Dhemaji district, Assam
2.3.3 Groundwater occurrence and movement Ground water in the area occurs under water-table condition and locally under semiconfined condition. Water table contour maps indicate that ground water flows from north to south. However, in the pediment area and Younger alluvial plain, occurrence and movement of ground water is controlled by local topography. Typically, depth-to-water table maps (Figure 2.3.2 and Figure 2.3.3) indicate about presence of a pocket of shallow groundwater zone (0-2m) in Sripani area within Younger alluvial plain matching a topographical depression. This zone reduces in post monsoon season.
2.3.4 Groundwater level trend analysis For analysis of long-term behaviour of ground water level, data from Ground Water Monitoring Stations (GWMS) are utilized. Historical depth-to-water level data (in m bgl) are plotted as individual hydrographs and are given in Figure 2.3.3 and 2.3.4. Table 2.3.2 shows the overall trend of water levels in GWMS wells. Table 2.3.2 Trend of Water levels in GWMS Wells Well No.
1
ASDM 15
Silapathar
8
Rise
Rise
Unchanged
2
ASDM 17
Sisiborgaon
4
Rise
Fall
Fall
3
ASDM 01
Akajan
4
Rise
Rise
Unchanged
4
ASDM 02
Bhagaban Chariali
5
Rise
Rise
Rise
5
ASDM 12
Gogamukh
8
Rise
Fall
Unchanged
6
ASDM 08
Dhemaji
7
Rise
Fall
Rise
Locality/Name
No. of Years
Overall Water Level Trend PostPreOverall Monsoon Monsoon
Sl. No.
The post-monsoon trends always show slightly rising trend, where as during premonsoon it is rising in some places and falling in some places. However, pre-monsoon falling trend is typically associated with more urban setup and rising trends are associated with rural setup. This may be due to more withdrawal of groundwater in urban setup. As overall trend, all the places are either unchanged or insignificantly rising or falling.
20
21
Fig. 2.3.2 Pre-Monsoon depth to water level map
22
Fig. 2.3.3 Post-Monsoon depth to water level map
Jan, 05
Jan, 06
Gogamukh
Dhemaji
Jan, 03
Jan, 02
Jan, 01
Jan, 02 Jan, 00
Jan, 03
Bhagban Chariali
Jan, 03
Jan, 04
Jan, 02
Jan, 01
Jan, 01
Jan, 99
2.0
1.0
0.0
-1.0
4.0
3.0
2.0
1.0
-1.0
5.0
3.0
0.0
DWL (m bgl)
1.0
Jan, 00
Jan, 98
DWL (m bgl)
DWL (m bgl)
-1.0
Jan, 00
23
Jan, 04
Jan, 05
Fig. 2.3.4 Hydrograph of GWMS Wells
Jan, 04
Nov, 06 Aug, 06
Aug, 06
Jan, 06
Jan, 06
Aug, 05
Aug, 05
Jan, 05
Jan, 05
Jan, 03 6.0
Jan, 03
4.0
Nov, 99
2.0
Aug, 03
0.0
Aug, 03
4.0
Nov, 00
2.0
Jan, 04
0.0
Jan, 04
24
Akajan
Aug, 04
Nov, 01
-2.0
8.0
5.0
2.0
Aug, 04
DWL (m bgl)
DWL (m bgl)
-1.0
Nov, 02
DWL (m bgl)
Silapathar
Nov, 03
Sisiborgaon
Nov, 04
Fig. 2.3.5 Hydrograph of GWMS Wells
Nov, 05
2.4 Hydrometeorology The climate of the district is Per-humid characterized by high rainfall, mild summer and winter and may be categorized under cool to warm per-humid thermic-agroecological sub zone. The annual rainfall of the district ranges from 2600 mm to 4600 mm and generally increases from south east to northeast. Rainy season begins from April and continues till end of September with July commonly be the wettest month. On an average there are about 200 days with 3.5 mm or more rain in a year. The relative humidity varies from 90 to 73 per cent. The temperature varies between 39.9°C in summer and 5.9°C in winter.
Table 2.4.1 Block-wise average annual rainfall Block
Average Annual Rainfall (mm)
Dhemaji
2748.3
Machkhowa
2700.4
Bordoloni
-No data-
Sissiborgaon
-No data-
Murkong Selek
3013.21
Source: Official website of Dhemaji District (as on August, 2008)
Table 2.4.2 Monthly rainfall (in mm) 1996 to 2006 Month
1996
1997
1998
1999
2000
2001
2002
2003
2004
2005
2006
January
28.17
26.07
24.05
9.02
62.14
12.03
27.15
9.04
39.00
77.00
24.15
February
37.14
65.28
107.14
4.02
37.05
72.05
23.10
54.33
24.04
160.00
87.26
March
123.24
196.26
177.43
39.05
57.17
34.13
53.20
79.58
169.00
226.00
41.55
April
180.14
61.20
144.16
283.26
227.42
147.25
355.30
126.24
228.00
289.00
159.21
May
724.49
212.18
499.22
462.24
233.18
195.26
220.04
270.46
1320.00
492.00
450.13
June
310.80
864.37
1102.47
562.38
362.00
562.32
291.33
560.47
567.05
892.70
617.50
July
546.42
587.48
671.44
633.51
596.38
471.40
744.26
996.49
878.00
708.84
575.83
August
603.33
552.28
780.44
865.49
428.54
598.33
584.05
409.12
151.00
559.67
566.26
September
201.30
507.44
276.20
437.20
702.32
564.31
270.27
456.12
606.00
162.96
209.14
October
263.19
42.05
149.14
312.19
18.16
218.20
99.04
313.00
534.00
80.2
173.46
November
-Nil-
44.05
7.08
18.07
33.04
26.06
63.03
10.00
-Nil-
45.70
77.91
December
-Nil-
44.02
-Nil-
0.04
-Nil-
10.06
-Nil-
7.00
68.00
-Nil-
13.56
Annual Total
3018.22
3202.68
3938.77
3626.47
2757.4
2911.4
2730.77
3291.85
4584.09
3694.07
2995.96
Station: Dhemaji E&D Divisional Office Compound
Source: Dept. of Water Resources
25
800.00
Monsoon Period
Average Annual Rainfall
700.00
Rainfall 2006
Rainfall (mm)
600.00 500.00 400.00 300.00 200.00 100.00
December
November
October
September
August
July
June
May
April
March
February
January
0.00
Fig. 2.4.1 Distribution of monthly rainfall
Annual Rainfall Variation
4000
3000
Year
Fig. 2.4.2 Variation in annual rainfall
26
2007
2006
2005
2004
2003
2002
2001
2000
1999
1998
1997
1996
2000 1995
Rainfall (in mm)
5000
Chapter 3
CHEMICAL QUALITY OF GROUNDWATER
3.1 Nature and distribution of key sampling wells In order to determine chemical quality of ground water of Dhemaji district with respect to arsenic contamination, ninety four (94) key sampling wells were established. Hand-pump, tubewell and dug-well being the most common spot source of drinking water, all these types were included for consideration as key sampling wells (KSW). Due consideration was given on geology and geomorphology of the area also. Type-wise numbers of key sampling wells are given in Table 3.1.1 to Table 3.1.3. Moreover wells are so selected that are in continuous use, well spread out and covers the entire area. Location map of key sampling wells is given in Figure 3.1.1. Table 3.1.1 Number of KSW based on well type Well Type
Number of Key Sampling Well
Hand pump
80
Tube well
11
Dug well
03
Table 3.1.2 Number of KSW based on location Block
Number of Key Sampling Well
Bordoloni
24
Dhemaji
28
Sisiborgaon
14
Muchkhowa
17
Murkong Selek
10
Table 3.1.3 Number of KSW based on geology and geomorphology Geology
Geomorphology
Number of Key Sampling Well
Older Alluvium
Piedmont Plain
06
Younger Alluvium
Younger Alluvial Plain
75
Recent Alluvium
Flood Plain
13
27
28
Fig. 3.1.1 Key sampling wells locations
29
Fig. 3.1.2 Distribution of Key sampling Wells shown on Terrain map (Terrain map source: map.google.com)
3.2 Sampling methodology Water samples were collected from key sampling wells established in the area. For this purpose, water samples (500 ml) were collected in clear polyethylene bottle (laboratory grade with cap and protective locks) from tubewells or deep-tubewells fitted with pumps after initial pumping for 10 minutes. Immediately after sampling, the samples are filtered through 0.45 millipore filters and then 8 ml of HCl (1:1) was added to each 500 ml of samples so that sample pH comes below 2. Additional 1lt of unfiltered, non-acidified samples were also collected for complete analyses. Field values of pH and EC was measured for each raw water sample before acidification, using portable digital pH and EC meters. Samples were then transferred to the laboratory and analyzed for As and Fe using Atomic Absorption Spectroscopy (AAS). Samples were analyzed for As and Fe in the Regional Chemical Laboratory of Central Ground Water Board, Hyderabad (CGWB, SR) and North Eastern Regional Institute of Water and Land Management (NERIWALM), Tezpur. Regional Chemical Laboratory of CGWB, Guwahati has done rest of the analyses. To check the reliability of analytical results, during pre-monsoon season, two identical sets of samples were collected and sent separately to CGWB, SR and NERIWALM. Comparison of results is given in Figure 3.2.1. The comparison shows that results are quite comparable with correlation coefficient of 0.74 with few outliers. To understand the repeatability of analysis, each set has also been given three duplicate samples with modified sample number and locality name. Results of repeat analyses are given in Annexure-VI. The results indicate that analyses of CGWB, SR are more reliable, hence for the present study, analytical values of CGWB, SR has been accepted.
Comparison of Analytical Results 200
NERIWALM As (ppb)
150
100
50
y = 1.2449x + 0.0501 R2 = 0.7359 0 0
50
100
150
200
As (ppb) CGWB, SR
Fig. 3.2.1 Comparison of analytical results of As 30
3.3 Distribution of Arsenic and Iron An attempt has been made to understand the spatial distribution of Arsenic and Iron in the area. Maps of As and Fe distribution has been prepared and represented using bubble diagram and given in Figure 3.3.1 to 3.3.4. The maps show that arsenic contamination is most severe in the Dhemaji and Bordoloni blocks. However, significant high values are also present in Sisiborgaon and Muchkhowa blocks. Murkong Selek T.D. Block is list affected. Arsenic values in the district ranges between –BDL- and 249 ppb during pre-monsoon season and between –BDL- and 109.5 ppb during post-monsoon season. Block-wise arsenic value ranges are given in Table 3.3.1. Table 3.3.1 Block-wise range of Arsenic values (in ppb) Pre-monsoon
Post-monsoon
Block Name Minimum
Maximum
SAPL
Minimum
Maximum
SAPL
Bordoloni
-BDL-
249
52.4%
-BDL-
75.8
50%
Dhemaji
-BDL-
108
60.9%
-BDL-
109.5
58.3%
Sisiborgaon
-BDL-
54
12.5%
-BDL-
50.2
66.7%
Muchkhowa
1
93
71.4%
-BDL-
66.5
70%
Murkong Selek
-BDL-
11
9.1%
-BDL-
43.9
30.8%
District Total
-BDL-
249
45.7%
-BDL-
109.5
53.9%
SAPL: % of samples above permissible limit
In case of iron concentration, the maps show that most severe cases exist in the Dhemaji and Bordoloni blocks. However, all other blocks are also severely affected. Iron concentration values in the district ranges between 0 and 69 ppm during pre-monsoon season and between –TRACE- and 49.2 ppm during post-monsoon season. Block-wise arsenic value ranges are given in Table 3.3.1. Table 3.3.2 Block-wise range of Iron values (in ppm) Pre-monsoon
Post-monsoon
Block Name Minimum
Maximum
SAPL
Minimum
Maximum
SAPL
1.5
42
100%
0.3
46.2
80%
Dhemaji
0
69
91.3%
-Trace-
49.2
79.2%
Sisiborgaon
0
38
75%
0.1
31
66.7%
Muchkhowa
0.8
40
85.7%
0.2
33.9
60%
Murkong Selek
0
32
72.7%
0.2
40
38.5%
District Total
0
69
87.1%
-Trace-
49.2
68.4%
Bordoloni
SAPL: % of samples above permissible limit
31
32
Fig. 3.3.1 Pre-monsoon distribution of Arsenic concentration
33
Fig. 3.3.2 Post-monsoon distribution of Arsenic concentration
34
Fig. 3.3.3 Pre-monsoon distribution of Iron concentration
35
Fig. 3.3.4 Post-monsoon distribution of Iron concentration
Relation between Pre-monsoon and Post-monsoon concentrations of As and Fe is graphically presented in Figure 3.3.5. For iron relation is well defined (correlation coefficient 0.78) with overall higher concentration during pre-monsoon season. However in case of arsenic the relationship is not so well defined with correlation coefficient (R2) of 0.32 only. Though the overall higher concentration during pre-monsoon season is indicated by the plot, the situation arises out of presence of few high value outliers. In actuality it is spread over a region.
As Concentrations (in ppb) 250 y = 0.3543x + 26.457 R2 = 0.3233
Post-Monsoon
200
150
100
50
0 0
50
100
150
200
250
Pre-Monsoon
Fe Conc entrations (in ppm) 80 y = 0.722x + 0.6119 R2 = 0.7837
Post-Monsoon
60
40
20
0 0
20
40
60
80
Pre-Monsoon
Fig. 3.3.5
Relationship between Pre-monsoon and Post-monsoon concentrations
36
Attempt has also been made to understand the correlation between arsenic and iron concentrations in the area. Scatter plots of arsenic vs. iron concentrations has been prepared and given in Figure 3.3.5 for both pre-monsoon and post monsoon seasons. However, the plots do not reveal any significant correlation with correlation coefficient (R2) being 0.07 and 0.12 for premonsoon and post-monsoon respectively. This indicate that anomalous concentrations of As and Fe are not directly correlatable.
y = 0.7977x + 17.483
Pre Monsoon
R2 = 0.0713
250
As (ppb)
200 150 100 50 0 0
20
40 Fe (ppm)
60
80
Post Monsoon
y = 0.735x + 24.014 2
R = 0.1265
125
As (ppb)
100 75 50 25 0 0
20
40 Fe (ppm)
Fig. 3.3.6 Scatter plot of As vs. Fe
37
60
Though As and Fe does not show any direct correlation it may be result of other controlling factors. Effect of pH on concentration may have significant bearing. Plots of pH vs. As (Figure 3.3.6) and pH vs. Fe (Figure 3.3.7) show that respective pH window is centered around 7.4 and 7.5. This indicates that As and Fe may be correlatable within the overlapping pH window and lack correlation outside.
7.8 7.6 7.4 pH
7.2 7.0 6.8 6.6 6.4 0
100
200
300
As (ppb)
Fig. 3.3.7 Scatter plot of pH vs. As (Pre-Monsoon)
7.8 7.6 7.4
pH
7.2 7.0 6.8 6.6 6.4 0.0
20.0
40.0
60.0
Fe (ppm)
Fig. 3.3.8 Scatter plot of pH vs. Fe (Pre-Monsoon)
38
80.0
3.4 Depth variation of Arsenic and Iron Variation of As and Fe concentrations with depth has been studied. Plots of arsenic concentration vs. depth of well and iron concentration vs. depth of well for both pre- and postmonsoon seasons (Figure 3.4.1 and 3.4.2) shows that concentration of As and Fe is most at about 10m depth. Discussions with local hand pump borers also indicated that zone of about 26' (~8m) is often highly iron-rich and should be avoided.
As (ppb) 0.0
100.0
200.0
Fe (ppm )
300.0
0.0 0.00
10.00
10.00
20.0
40.0
60.0
80.0
Depth (m)
Depth (m)
0.00
20.00
20.00
30.00
30.00
Fig. 3.4.1 Depth vs. Concentration for As and Fe during Pre-monsoon Season
Fe (ppm )
As (ppb) 0.0
50.0
100.0
0.0
150.0
0.00
10.00
10.00
40.0
Depth (m)
Depth (m)
0.00
20.0
20.00
20.00
30.00
30.00
Fig. 3.4.2 Depth vs. Concentration for As and Fe during Post-monsoon Season
39
60.0
However, the depth-wise analysis may get biased by pattern and nature of sampling. During this study mostly private hand pumps have been sampled. But economic condition of people often does not permit to go at any depth. After the first zone at about 8m, next zone is commonly encountered beyond 60' (~20m) depth. Tapping this zone will increase the cost of construction many fold. Hence, a east-west profile of hand-pump depth has been prepared (Figure 3.4.3). This indicate that maximum depth is commonly encountered in Dhemaji block where as in eastern extremity wells are shallow. This pattern is correlatable with prepared fence diagram (Figure 2.3.1). Hence, bias if any may be considered negligible.
Latitude West
94.20
East
94.40
94.60
94.80
95.00
95.20
95.40
0
Depth (m bgl)
5 10 15 20 25 30 Figure 3.4.3 East-west profile of hand-pump depth Site-specific depth-wise variation in As and Fe concentration has been studied by comparing the As and Fe content of hand-pumps and deep tubewells of same location. Only seven set of data was available. As and Fe concentration has been analyzed for both pre-monsoon and post monsoon seasons (Figure 3.4.4 and 3.4.5). Higher As content in deep tubewells has been observed only in Matikhola and Moridhal during pre-monsoon. At Moridhal situation again reversed during postmonsoon. Higher Fe content in deep tubewells has been observed only in Matikhola and Mohori Camp during pre-monsoon. During post-monsoon, at Jonai higher Fe content has been observed. This may indicate prevalence of As and Fe at shallower depth. On the other hand, these deep tubewells commonly tap several zones, hence a cumulative concentration may represent the well. However, a sharp contrast is commonly present between hand-pumps and deep tubewells concentrations.
40
Moridhol
Jonai II PWSS
Jonai II PWSS
Jonai
Jonai
Mohoricamp CGWB well 1
Mohoricamp CGWB well 1
Tarajan
Tarajan
Bishnupur PWSS
Bishnupur PWSS
Bishnupur II
Bishnupur II
Likhabali MES WSS
Likhabali MES WSS
Likhabali II
Likhabali II
Matikhola PWSS
20.0
40.0
80.0
100.0
120.0
0.0
10.0
20.0
30.0
50.0
40.0
As (ppb)
60.0
60.0
As (ppb)
70.0
Matikhola HP
Dhemaji I PWSS Dhemaji Matikhola PWSS Matikhola HP 0.0
Dhemaji
Max. P. Limit
Dhemaji I PWSS
41
Moridhol
Fig. 3.4.4 Comparison of As content in Deep and shallow wells
Moridhol II PWSS
Post-Monsoon
Maximum Permissible Limit
Pre-Monsoon
Moridhol II PWSS
Jonai
Jonai
Mohoricamp CGWB well 1
Mohoricamp CGWB well 1
Tarajan
Tarajan
Bishnupur PWSS
Bishnupur PWSS
Bishnupur II
Bishnupur II
Likhabali MES WSS
Likhabali MES WSS
Likhabali II
Likhabali II
Matikhola PWSS
0.0
5.0
10.0
15.0
20.0
Matikhola HP 25.0
50.0
0.0
5.0
10.0
15.0
25.0
20.0
Fe (ppm)
30.0
Matikhola HP
Dhemaji
30.0
Matikhola PWSS
Dhemaji I PWSS
35.0
Dhemaji
40.0
Dhemaji I PWSS
42
Jonai II PWSS
Fig. 3.4.5 Comparison of Fe content in Deep and shallow wells
Jonai II PWSS
Post-Monsoon
Moridhol
45.0
Pre-Monsoon
Moridhol II PWSS
Moridhol
Fe (ppm)
35.0
Moridhol II PWSS
4.5 Effect on Human Health Though Dhemaji district has been reported to be contaminated with As, a very few reports about As contamination came so far. This posed hindrance towards detection of As contamination and estimation of its severity. Hence a small survey was also taken up during the study to know about the food habit and drinking water consumption habits of the people of the area. The results of survey are compiled in Annexure-VIII. Summary of survey results is given in Table 4.5.1 Table 4.5.1 Summary of survey results Sl. No. 1 a) b) c) 2 a) b) 3 a) 4 a) b) c) d) e) f) g) h) i) 5 a) b) a) b) 6 a)
Number and percent of conforming respondents
Property Occupation Farmer Govt. Servant Village Head Income Group Low Medium Main food Rice Subsidiary Food Dal Potato Green Vegetables Fish (Less than once a week) Fish (Once a week) Fish (More than once a week) Meat (Less than once a month) Meat (Once a month) Meat (More than once a month) Drinking water Source Hand pump Filtered (Yes/No) Type of filter Home made Sand Filter Commercial Porcelain Candle Filter Any lingering Disease Skin Disease
16 2 1
80% 10% 5%
9 11
45% 55%
20
100%
5 5 15 4 6 10 8 2 10
25% 25% 75% 20% 30% 50% 40% 10% 50%
20 20
100% 100%
18 2
90% 10%
2
10%
The results indicate that in both low and medium income group, consciousness about drinking water is present. Use of hand-pump water and filtering is everybody’s practice. It is probable that high iron content of drinking water made it compulsory. In food, apart from rice,
43
green vegetable is very common with moderate to high fish and meat consumption. This typical food habit may explain the less manifestation of As related diseases among the residents of the area. However, skin disease is common and present in about 10% people. These skin diseases may be further tested by authorized medical practitioners.
3.6 Effect of filtering on Arsenic and Iron As discussed above, it has been observed that common people of Dhemaji is used to the process of filtering of drinking water, particularly due to presence of high iron in groundwater. The domestic filters are not necessarily expensive ones, but are mostly make-shift arrangements in the form of sand filters in the rural areas. These filters are commonly prepared using cans initially filled with broken brick fragments then covered by sands. Porcelain candle filters also are very much in use and commoner in urban to semi-urban areas.
Fig. 3.6.1 Schematic diagram of homemade filter To check, whether this common practice of filtering has any effect on As content of water, in field condition both raw water sample and 24 hrs filtered water sample was been collected from two highly As infested areas namely Teliajan and Jamuguri of Dhemaji block (Well no 12 and 6 respectively). Analytical results are given in Annexure-VII. Candle type filter was in use at Teliajan (well 12) and home made sand filter was in use at Jamuguri (well 6). Analytical results are plotted in Figure 3.6.1. The results show that domestic filtering has successfully reduced the As and Fe levels in drinking water. At Jamuguri, arsenic concentration level gone down to 8 ppb from initial level of 79 ppb and iron concentration level gone down to 0.35 ppm from initial level of 22 ppm. At Teliajan, arsenic concentration level gone down to 2 ppb from initial level of 26 ppb and iron concentration level gone down to 0.88 ppm from initial level of 69 ppm. Thus filtering effectively reduced concentration levels of both the elements within maximum permissible limit of BIS (2003) standard. For arsenic the removal is about 90% and that for iron is about 98%. This is most probably result of co-precipitation of As with Fe under oxidizing environment.
44
Arsenic
Iron 80
100
Raw Water Sample 79 80
Max. Permissible Limit : 1 ppm
Raw Water Sample
24hr Filtered Sample
60
69
60
Fe (ppm)
As (ppb)
24hr Filtered Sample
40
40
26 20 20 10
8
22
Max Per. Limit 0.35
2
0.88
0
0 Jamuguri
Teliajan
Jamuguri
Teliajan
Fig. 3.6.2 Comparison of raw water sample and 24 hrs filtered water sample
45
Chapter 4
SUMMARY AND RECOMMEDATIONS 4.1 Summary The present study has been carried out to establish the presence of arsenic in ground water of Dhemaji District and to relate its distribution with existing hydro-geological set up of the area by understanding the regional hydrogeology and spatiotemporal variation of arsenic contamination. The results and findings of the study are summarized as below: a)
Study confirms about presence of arsenic in the Dhemaji district;
b)
However, distribution of arsenic is not uniform and con controlled by complex interaction of existing geological-hydrogeological set up with climatic condition;
c)
The study of the geology of the area indicates a complex depositional environment. It indicates variation in nature of aquifer both in lateral and vertical directions. However in contrast to earlier conceived double-aquifer model, present study indicates about a mono-aquifer system with intermittent clay lenses/layers which may extend for considerable distance. A continuous separating layer is absent;
d)
Ground water in the area occurs under water-table condition and locally under semiconfined condition. Water table contour maps indicate that ground water flows from north to south. Depth to water level varies from 0.01 m bgl to more than 9.4 m bgl during pre-monsoon period (April, 2006) and from 1.84 m bgl to more than 9.63 m bgl during post-monsoon period (November, 2006);
e)
The post-monsoon water level trends always show slightly rising trend, where as during pre-monsoon it is rising in some places and falling in some places. However, pre-monsoon falling trend is typically associated with more urban setup and rising trends are associated with rural setup;
f)
Arsenic concentration is high in the west-central part of the district;
g)
Along with earlier identified Dhemaji and Sisiborgaon blocks, Bordoloni block is also highly affected. On the other hand, Murkong Selek T.D. Block is list affected;
46
h)
Spatially arsenic values vary widely as well as seasonally. During pre-monsoon the range is BDL to 249 ppb and that during post monsoon is BDL to 109.5 ppb;
i)
Relation between Pre-monsoon and Post-monsoon concentrations of As is not well defined, though overall higher concentration during pre-monsoon season is indicated. However, for iron, the relation is well defined (correlation coefficient 0.78) with overall higher concentration during pre-monsoon season;
j)
Study indicates that anomalous concentrations of As and Fe are not directly correlatable. However, effect of pH on concentration may have significant bearing;
k)
Comparison of
concentrations with depth of well for both pre- and post-monsoon
seasons (Figure 3.4.1 and 3.4.2) shows that concentration of As and Fe is most at about 10 m depth. This is correlatable with geological model; l)
Site-specific depth-wise comparison of As and Fe concentration using hand-pumps and deep tubewells of same location also indicate prevalence of As and Fe at shallower depth;
m)
Results of survey about food and drinking water use habit indicate that in both low and medium income groups, consciousness about drinking water is present. Use of handpump water and filtering is everybody’s practice. In food, high intake of green vegetable with moderate to high intake of fish and meat may prevent ill effects of arsenic. However, skin disease is common and present in about 10% people;
n)
Use of domestic filter effectively reducing arsenic level in water. These filters are in common use due to high concentration of iron in water. Field eexperimental results show that for arsenic the removal is about 90% and that for iron is about 98%, which is most probably result of co-precipitation of As with Fe under oxidizing environment.
4.2 Recommendations Solution to such a problem like mitigation of Arsenic contamination hazard lies in understanding the intricate relationship between the various socio-economic factors associated with it. Consumed arsenic may be excreted from the body through methylation (often termed as detoxification) mostly through urine. But methylation reaction needs methyl source coming from a balanced nutritional methionine-rich food sources like green vegetables and meat (Basu and Sil, 2003). Thus economic condition of the population affected also plays a key to the solution.
47
In view of rural nature and demographic setup of the area, the following recommendations may be considered: a)
Though present study confirms about presence of arsenic in the area, more detailed study is required to understand detailed aquifer geometry and characterization of aquifer matrix. Chemical equilibrium system has to be thoroughly understood, so that proper remediation technique may be devised;
b)
A well census for ground water abstraction structures may be carried out in the area for more precise identification of As contamination and its severity and further hazard mitigation. Water well registration may be made mandatory;
c)
Arsenic removal plants may not be very effective as they create on-site sludge disposal problems;
d)
In-situ removal has been successful in decreasing arsenic concentrations from ground water containing high concentrations of both arsenic and iron. Pumping water from one well into a second well after adding atmospheric oxygen can result in arsenic removal from the ground water (Rott and Friedle, 1999). The recharged well can then be used for water supply. Advantage of this approach is that more than ten units of low-arsenic water may be obtained for each unit recharged. Also, removal efficiency increases with successive cycles of recharge and withdrawal. Injection of water containing dissolved oxygen can lead to rapid exchange of Fe2+ for cations in the injected water with subsequent Fe2+ oxidation to form hydrous ferric oxide (HFO). Upon reversing the flow direction, the injected water has lower iron concentration. Continued pumping can produce water with a lower iron concentration because Fe2+ is removed by exchange. Arsenic can co-precipitate with the HFO during injection and adsorption onto the HFO during withdrawal (Welch and Stollenwerk, 2001);
e)
Conjunctive use may be preferred, instead of consumptive use;
f)
Even if alternate sources of water for potable purposes are identified, continued agricultural activity by As contaminated ground water will pose significant risk to animal and human health through water-soil-crop transfer of As. Food crops such as vegetables and cereals can become a path by which As may enter the food chain. Recent studies by Meharg et al. (2002) and Huq et al. (2001) demonstrated significant uptake of Arsenic by rice and a
range of vegetable crops;
48
g)
In the face of As contamination hazard, an umbrella of legal framework with relevant and strict water related laws should be erected with vigilant implementations in place, to achieve sustainability. Agencies responsible for such look-after should be sufficiently empowered legally as well as organizationally.
49
BIBLIOGRAPHY Astolfi, E., Maccagno, A., Fernandez, J.C.G., Vaccara, R. and Stimola, R., (1981) Relation between arsenic in drinking water and skin cancer. Biological Trace Element Research, 3, pp. 133- 143. Basu, B., and Sil, S., (2003) Arsenic mapping for North 24- Pargana District of West Bengal – using GIS and Remote Sensing technology; Proc. Map India Conference; Borgono, J.M. and Greiber, R. (1971) Epidemiological study of arsenicism in the city of Antofagasta. Trace Substances in Environmental Health, 5, pp. 13-24. Cebrian, M.E., Albores, A., Aguilar, M. and Blakely, E. (1983) Chronic arsenic poisoning in the north of Mexico. Human Toxicology, 2, pp. 121-133. Dept. of Agriculture (2005) Basic Information Booklet on Agriculture in Dhemaji District, District Agriculture Office, Dept. of Agriculture; Govt. of Assam; Dhemaji; 17P. Huq, S.M.I., Quazi Afroz Jahan Ara, Khaleda Islam, Abduz Zaher and Ravi Naidu (2001) The possible contamination from Arsenic through food chain. in: Groundwater Arsenic Contamination in the Bengal Delta Plain of Bangladesh. Proceedings of the KTH-Dhaka University Seminar, University of Dhaka, Bangladesh. Jacks, G., Bhattacharya, P. and Khan, A.A. (Eds.). KTH Special Publication, TRITA-AMI Report 3084, KTH, pp. 91-96. Meharg, A.A. and Rahman, M.M. (2002) Arsenic Contamination of Bangladesh Paddy Field Soils: Implications for Rice Contribution to Arsenic Consumption. Environ. Sci. Technol., ASAP Article 10.1021/es0259842 S0013-936X(02); pp. 05984-9. Official Website of Dhemaji District at http://assamdistricts.nic.in/dhemaji/dhemaji.htm Official Website of School /arsenicContents.htm
of
Environmental
Studies
(SOES)
http://www.soesju.org/arsenic
PHED (2003) Dhemaji District Public Health Engineering Department at a glance, Office of the Public Health Engineering Department; Govt. of Assam; Dhemaji, November 2003, 23P. Reddy, G. V. (1999) Reapprisal Hydrogeological Surveys in Dhemaji district, Assam State; CGWB; NER. Rott, U. and M. Friedle (1999) Subterranean removal of arsenic from groundwater; in Arsenic exposure and health effects. C.O. Abernathy, W.R. Chappell, and R.L. Calderon eds., Oxford, UK, Elsevier Science Ltd., pp. 389-396. Roy, B. (2006) Report on District ground water development and management studies Dhemaji district, Assam; CGWB; NER. Welch, A.H., Helsel, D.R., Focazio, M.J., and Watkins, S.A. (1999) Arsenic in ground water supplies of the United States, in: Arsenic exposure and health effects, W.R. Chappell, C.O. Abernathy and R.L. Calderon, Eds., Elsevier Science, New York, pp. 9-17. Welch, A.H., and Stollenwerk, K.G., (2001) In-situ remediation of arsenic in ground water: In Arsenic in the Asia-Pacific Region, Adelaide, Australia, Nov. 20-23; pp.67-68.
50
ANNEXURES
Annexure I
DETAILS OF KEY SAMPLING WELLS ESTABLISHED IN DHEMAJI DISTRICT RL
MP
Depth
Age
(m amsl)
(m agl)
(m)
(Yr)
27°30'08.00"
88
0.30
13.72
Younger Alluvium
Younger Alluvial Plain
At Goalchapori middle school. About 4 km from Dhemaji on way to Moridhol.
94°35'50.22"
27°32'15.03"
85
0.30
10.97
Younger Alluvium
Younger Alluvial Plain
At Moridhol chariali. Backside of Hotel Joya. Owner of the hotel is Sh. Satish Gogoi.
Hand pump
94°35'19.55"
27°33'00.56"
89
0.30
13.72
Younger Alluvium
Younger Alluvial Plain
2 km from Moridhol chariali towards north, before reaching Raichapori Lachom gaon. Well is in the residence of Kakoi Hatimuria.
Dhemaji
Hand pump
94°31'55.77"
27°31'56.18"
93
1.52
6.40
Younger Alluvium
Younger Alluvial Plain
Beside Raichpori Lachomgaon L.P. school. Backside of Sh. Baidyanath Taye.
High Fe; Sand pumping.
Jamuguri
Dhemaji
Hand pump
94°31'34.38"
27°30'33.13"
98
0.30
7.62
Younger Alluvium
Younger Alluvial Plain
At Jamuguri Panchali. In the residence of Sh. Damodar Kaptak.
High Fe, Used after filtering
8
Santipur Konch Gaon
Dhemaji
Hand pump
94°30'04.66"
27°33'05.31"
107
0.30
18.29
Younger Alluvium
Younger Alluvial Plain
Santipur Konchgaon is 5 km from Jamuguri Panchali. Well is at Jamuguri Panchali L.P school.
9
Theckjuri
Dhemaji
Hand pump
94°29'27.41"
27°30'37.16"
99
0.15
13.72
Younger Alluvium
Younger Alluvial Plain
3 km from Jamuguri panchali/ 10 km from Jiyadhol
Sl. No.
Well No.
1
Locality
Block
Type
Latitude
Longitude
1
Goalchapori
Dhemaji
Hand pump
94°34'55.60"
2
2
Moridhol
Dhemaji
Hand pump
3
3
Moridhol Hachwa
Dhemaji
4
5
Raichapori Lachomgaon
5
6
6
7
52
Geology
Geomorph -ology
Location Details
Remarks
Sl. No.
Well No.
Locality
Block
Type
Latitude
Longitude
RL
MP
Depth
Age
(m amsl)
(m agl)
(m)
(Yr)
Geology
Geomorph -ology
Location Details
Remarks
chariali. Well is at Theckjuri 5 No. L.P. school. Opposite to Mukul Medical Hall. 8
10
Jiyadhol Tingharia
Dhemaji
Hand pump
94°30'20.20"
27°27'12.12"
80
0.30
10.67
9
12
Teliajan
Dhemaji
Hand pump
94°32'40.74"
27°26'57.35"
86
0.61
7.32
10
13
Dhemaji I
Dhemaji
Hand pump
94°33'53.40"
27°28'49.44"
89
0.30
7.62
11
14
Dhemaji PWSS
Dhemaji
Deep Tubewell
94°34'06.76"
27°28'49.26"
87
0.91
28.96
12
15
Matikhola PWSS
Machkhowa
Deep Tubewell
94°35'23.85"
27°27'05.94"
83
0.91
13
16
Matikhola
Machkhowa
Hand pump
94°35'34.83"
27°26'56.12"
84
0.30
53
Younger Alluvium
Younger Alluvial Plain
At railstation chariali. About 2 km from Jiyadhol chariali, in the residence of Sh. Harison Pegu.
Younger Alluvium
Younger Alluvial Plain
25 km from Gogamukh chariali towards Dhemaji. Well is at Teliajan tiniali, in the residence of Sh. Jogen Gogoi.
Younger Alluvium
Younger Alluvial Plain
In the campus of Office of the Director of Health Service, Dhemaji. Well is in the house of Nandalal Basfor, Sweeper.
Younger Alluvium
Younger Alluvial Plain
Dhemaji PHED Public Water Supply System.
60.96
Younger Alluvium
Younger Alluvial Plain
Matikhola PHED Public Water Supply System.
13.72
Younger Alluvium
Younger Alluvial Plain
3 Km from Dhemaji town towards south. Well is at Matikhola L.P. school, beside Namghar.
26
22
Arsenic Symptoms?
Low Fe, with out Filtering also. Arsenic Symptom(?) For nearby well
RL
MP
Depth
Age
(m amsl)
(m agl)
(m)
(Yr)
27°26'27.76"
97
0.30
13.72
19
Younger Alluvium
Younger Alluvial Plain
6 km from Dhemaji, opposite to medical sub-centre. In the house of Kumveswar Bora.
94°28'15.85"
27°25'24.55"
77
0.30
7.62
5
Younger Alluvium
Younger Alluvial Plain
17 km from Gogamukh chariali towards Dhemaji. Well beside Samajan Namghar and in the residence of Sh. Samanta Chutia.
Hand pump
94°25'38.17"
27°29'06.67"
106
0.18
13.41
4
Younger Alluvium
Younger Alluvial Plain
At 621 No. Borbila L.P school. About 9 km from Moromi tiniali beside Namghar.
Bordolani
Hand pump
94°26'43.70"
27°31'06.13"
103
0.30
7.62
Older Alluvium
Piedmont Plain
From Barbali chariali/ Baligaon chariali 10 km approx. Well is at Lalukijan Majgaon. In the residence of Sh. Ram Bahadur Thapa Chetri.
Kamalpur (Lalukijan Dharmapur)
Bordolani
Hand pump
94°27'02.52"
27°29'27.21"
91
0.61
13.41
Younger Alluvium
Younger Alluvial Plain
Beside Lalukijan Dharmapur L.P school. Owner Rina Sonwal.
22
Dihingia Barbam
Bordolani
Hand pump
94°25'14.85"
27°27'57.15"
85
0.46
10.67
Younger Alluvium
Younger Alluvial Plain
In the residence of Sh. Sisuram Sonwal.
23
Deuri Barbam
Bordolani
Hand pump
94°25'51.44"
27°26'51.45"
101
0.15
21.34
Younger Alluvium
Younger Alluvial Plain
At Barbam L.P. school.
Sl. No.
Well No.
14
Locality
Block
Type
Latitude
Longitude
17
Chengalipath ar
Dhemaji
Hand pump
94°31'42.34"
15
18
Samajan
Bordolani
Hand pump
16
19
Borbila Chutakia
Bordolani
17
20
Majgaon (Lalukjan)
18
21
19
20
54
Geology
Geomorph -ology
Location Details
Deuri
Remarks
High Fe, Used after filtering
RL
MP
Depth
Age
(m amsl)
(m agl)
(m)
(Yr)
27°24'44.96"
69
0.61
10.36
94°22'13.81"
27°25'15.20"
78
0.46
20.12
Hand pump
94°21'51.88"
27°28'04.32"
98
0.37
Bordolani
Hand pump
94°22'09.04"
27°29'23.11"
85
Mohoricamp Tiniali
Bordolani
Hand pump
94°18'30.90"
27°28'17.07"
29
Dirpai
Bordolani
Hand pump
94°17'53.47"
30
Borolagaon
Bordolani
Hand pump
94°19'48.69"
Sl. No.
Well No.
21
Locality
Block
Type
Latitude
Longitude
24
Bordoloni
Bordolani
Hand pump
94°25'23.24"
22
25
Bhebali
Bordolani
Hand pump
23
26
Betbari
Bordolani
24
27
Bhekali
25
28
26
27
Geology
Geomorph -ology
Location Details
Younger Alluvium
Younger Alluvial Plain
In the residence of Sh. Laxmi Munda, beside Bordoloni police station.
Recent Alluvium
Flood Plain
6 km from Gogamukh chariali on way to Dhemaji. At Bhebeli H.S. school campus.
19.81
Younger Alluvium
Younger Alluvial Plain
4 km from Moromi tiniali at Betbari. Opposite Betbari H.S. school in the house of Sh. Premsagar Boro.
0.30
5.18
Younger Alluvium
Younger Alluvial Plain
7 km from Moromi tiniali at Bhekeli gaon (in between Betbari and Krishnapur). In the residence of Sh. Krishna Doley.
72
0.30
7.62
Younger Alluvium
Younger Alluvial Plain
4 km from Gogamukh chariali towards north on way to Dirpai. Backside of the shop of Sh. Hemraj Sarma. Beside M/s Horizon stores.
27°29'53.65"
93
0.30
4.57
Older Alluvium
Piedmont Plain
In the residence of Sh. Lankeswar Doley. Beside Dirpai PHED PWSS.
27°31'13.24"
92
0.46
7.62
Older Alluvium
Piedmont Plain
At Borola chariali, 11 km from Gogamukh towards north. In the
55
9
1.5
Remarks
High Fe
Sl. No.
Well No.
Locality
Block
Type
Latitude
Longitude
RL
MP
Depth
Age
(m amsl)
(m agl)
(m)
(Yr)
Geology
Geomorph -ology
Location Details
Remarks
residence of Sh. Ashini Saikia, Opp. Rubi Drugs House.
28
31
Gogamukh
Bordolani
Hand pump
94°18'57.91"
27°26'04.58"
87
0.46
8.84
29
32
Bherikichuk
Dhemaji
Hand pump
94°31'31.67"
27°24'36.40"
88
0.61
11.58
30
33
Botipur
Dhemaji
Hand pump
94°31'39.53"
27°23'19.17"
86
0.61
7.32
31
34
Latakgaon
Bordolani
Hand pump
94°19'49.72"
27°23'21.88"
84
0.61
10.36
32
35
Bordoibum
North Lakhimpur District
Hand pump
94°20'47.00"
27°21'13.68"
93
0.61
7.01
56
9
4
Younger Alluvium
Younger Alluvial Plain
At Gogamukh chariali. Opposite Santosh Bastralaya, backside of the shop of Sh. Babul Barman.
Younger Alluvium
Younger Alluvial Plain
Opposite Bherikichuk L.P. school in the residence of Sh. Rudreswar Changmai.
Recent Alluvium
Flood Plain
At Botipur chariali, backside of the shop of Sh. Deben Bora.
Younger Alluvium
Younger Alluvial Plain
5 km from Gogamukh chariali towards south on Gogamukh – Ghilamora road. In the residence of Sh. Udesh Pegu.
Recent Alluvium
Flood Plain
11 km from Gogamukh chariali towards south on Gogamukh – Ghilamora road. In front of Shiva Temple, beside shop of Sh. Dharmeswar Bora.
Contaminated(?)
RL
MP
Depth
Age
(m amsl)
(m agl)
(m)
(Yr)
27°31'49.54"
95
0.46
7.47
5
Younger Alluvium
94°43'43.24"
27°31'29.85"
91
0.61
7.32
6
Hand pump
94°44'15.64"
27°33'23.40"
101
0.30
7.62
10
Sisiborgaon
Hand pump
94°43'37.70"
27°34'56.40"
100
0.30
10.36
Madhuri pathar
Sisiborgaon
Hand pump
94°42'36.30"
27°38'20.30"
124
0.46
7.92
A41
Likhabali MES WSS
Sisiborgaon
Deep Tubewell
94°41'49.00"
27°38'51.89"
129
0.91
91.44
39
A44
Shripani
Machkhowa
Hand pump
94°38'24.04"
27°34'02.61"
104
0.30
40
46
Amguri
Machkhowa
Hand pump
94°38'25.73"
27°26'48.40"
83
0.30
Sl. No.
Well No.
33
Locality
Block
Type
Latitude
Longitude
36
Sisiborgaon
Sisiborgaon
Hand pump
94°40'48.35"
34
37
Kulajan
Machkhowa
Hand pump
35
38
Akajan
Sisiborgaon
36
A39
Silapathar
37
A40
38
57
Geomorph -ology
Location Details
Remarks
Younger Alluvial Plain
Well is at Sisiborgaon chariali, beside NH. Infront of the shop of Sh. Keshab Ch. Bhuian.
High Fe, Used after filtering
Younger Alluvium
Younger Alluvial Plain
Well is at Kulajan chariali beside NH.
Low Fe, without Filter
Younger Alluvium
Younger Alluvial Plain
At Akajan tiniali, in the residence of Smt. Nilima Pait.
High Fe, Used after filtering
Younger Alluvium
Younger Alluvial Plain
In front of Residential Public School, about 3 km from Akajan towards north.
3
Younger Alluvium
Younger Alluvial Plain
Silapathar – Likhabali road. On the backside of Pradhan Medical stores. Owner Sh. Brishnu Pradhan.
4
Younger Alluvium
Younger Alluvial Plain
Within Likhabali army camp. MES WSS.
10.97
Younger Alluvium
Younger Alluvial Plain
Well is at Shripani Janakalyan chariali and backside of the shop of Sh. Kulo Saikya.
0.00
Younger Alluvium
Younger Alluvial Plain
At Amguri Tribal High School. About 12 km from Dhemaji through Bangalmara.
Geology
Sl. No.
Well No.
41
RL
MP
Depth
Age
(m amsl)
(m agl)
(m)
(Yr)
27°39'30.37"
111
0.30
7.92
Younger Alluvium
Younger Alluvial Plain
13 km from Akajan towards Jonai. Beside NH & backside of M/s Sabita Industry.
94°51'08.15"
27°42'13.48"
119
0.46
10.97
Younger Alluvium
Younger Alluvial Plain
At Depa village, 1 km before Simen river. In the residence of Sh. Haladhar Paul.
Hand pump
94°52'53.80"
27°43'02.60"
121
0.30
10.97
Younger Alluvium
Younger Alluvial Plain
At the trijunction of Simenchapori college road. Owner Sh. Shriram Chutia.
Murkong Selek
Hand pump
95°00'34.60"
27°45'49.90"
107
0.61
10.67
Younger Alluvium
Younger Alluvial Plain
41 km from Akajan on way to Jonai. Beside Telem GWMS. In the residence of sh. Sarath Ch. Mili.
High Fe. Nearby defunct PWSS encountered Bouldery fm.at 78ft.
Limekuri
Murkong Selek
Hand pump
95°04'44.35"
27°44'47.30"
102
0.30
7.92
Younger Alluvium
Younger Alluvial Plain
49 km from Akajan. At Laimekuri PHED PWS station.
Also 35' TW in the area. Nearby defunct PWSS 41m. Bouldery fm. at 100'.
Gali
Murkong Selek
Hand pump
95°07'21.80"
27°45'16.80"
105
0.30
7.62
Younger Alluvium
Younger Alluvial Plain
54 km from Akajan. At Gali bazaar tiniali. Backside of the shop of Sh. Doni Pegu.
Locality
Block
Type
Latitude
Longitude
47
Bhagaban Chariali
Murkong Selek
Hand pump
94°47'03.89"
42
48
Depa
Murkong Selek
Hand pump
43
49
Simenchapori
Murkong Selek
44
51
Telem (Kaman Selek)
45
52
46
53
58
Geology
Geomorph -ology
Location Details
Remarks
Low Fe, without Filter
RL
MP
Depth
Age
(m amsl)
(m agl)
(m)
(Yr)
27°46'51.40"
108
0.30
4.57
Younger Alluvium
Younger Alluvial Plain
Near Bijoypur GWMS. In the residence of Manchili Basumatari, owner of Jamuna medical stores.
95°13'36.90"
27°49'33.20"
117
0.30
8.84
Younger Alluvium
Younger Alluvial Plain
In front of the school beside Jonai PHED PWSS.
Deep Tubewell
95°13'36.90"
27°49'33.20"
0.91
18.29
Younger Alluvium
Younger Alluvial Plain
Jonai town PHED PWSS. Back side of the Court.
Murkong Selek
Hand pump
95°14'57.40"
27°47'56.20"
110
0.46
3.66
Recent Alluvium
Flood Plain
4 km from Jonai bazaar towards south. Beside shop of Sh. Rajkumar Doley.
Kachari Baligaon
Dhemaji
Hand pump
94°32'22.85"
27°29'35.47"
113
0.46
13.56
Younger Alluvium
Younger Alluvial Plain
From Dhemaji railway station ½ km towards North approaching Jamuguri Panchali. In the residence of Sh. Bolin Kochari.
59
Naharbari
Dhemaji
Hand pump
94°30'44.07"
27°29'25.25"
98
0.30
25.91
Younger Alluvium
Younger Alluvial Plain
Approchable from Jamuguri Panchali towards west. In the residence of Sh. Makan Ching Chinte, at Naharbar.
60
Lachitnagar (Khubulia)
Machkhowa
Tube well
94°34'32.96"
27°27'31.09"
92
0.30
27.43
Younger Alluvium
Younger Alluvial Plain
At Dhemaji Civil Hospital water supply campus.
Sl. No.
Well No.
Locality
Block
Type
Latitude
Longitude
47
54
Bijoypur
Murkong Selek
Hand pump
95°09'59.40"
48
55
Jonai
Murkong Selek
Hand pump
49
56
Jonai II PWSS
Murkong Selek
50
57
Bahir Jonai
51
58
52
53
59
Geology
Geomorph -ology
Location Details
Remarks
High Fe, Used after filtering. Also 20' TW in the area.
RL
MP
Depth
Age
(m amsl)
(m agl)
(m)
(Yr)
27°30'43.90"
94
0.15
15.24
94°36'34.88"
27°31'22.10"
91
0.91
Hand pump
94°22'06.99"
27°29'24.95"
85
Bordolani
Hand pump
94°27'03.77"
27°29'27.66"
Lalukijan Majgaon (II)
Bordolani
Hand pump
94°26'42.47"
27°30'31.45"
66
Barbam Garubandha
Bordolani
Hand pump
94°25'16.57"
27°27'53.68"
67
Dhemaji (II)
Dhemaji
Hand pump
94°33'29.13"
27°28'35.81"
Sl. No.
Well No.
54
Locality
Block
Type
Latitude
Longitude
61
Juktali
Dhemaji
Hand pump
94°34'02.62"
55
62
Jamuguri (Moridhol)
Machkhowa
Hand pump
56
63
Bhekeli (II)
Bordolani
57
64
Lalukijan Dharmapur (II)
58
65
59
60
Geomorph -ology
Location Details
Younger Alluvium
Younger Alluvial Plain
At Juktali L.P school. About 2 km from Goalchapori.
13.11
Younger Alluvium
Younger Alluvial Plain
From Moridhol chariali towards south-east. In the residence of Sh. Gopal Lahon.
0.30
7.62
Younger Alluvium
Younger Alluvial Plain
7 km from Moromi tiniali at Bhekeli gaon (in between Betbari and Krishnapur).
77
0.46
7.92
Younger Alluvium
Younger Alluvial Plain
Approachable from Baligaon chariali, in between Moromi tiniali and Barbila Chutiakari, towards west. Beside school, in the residence of Sh. Rabindra Barman.
99
0.30
7.62
Older Alluvium
Piedmont Plain
From Barbali chariali/ Baligaon chariali 10 km approx. Well is at Lalukijan Majgaon. In the school campus.
0.30
10.67
Younger Alluvium
Younger Alluvial Plain
Before reaching Bali-gaon towards west. At Barbam Garubandha L.P school.
0.30
10.67
Younger Alluvium
Younger Alluvial Plain
At Hotel Shikha & Restaurent, Station road.
87
60
Geology
Remarks
Arsenic Symptom (?)
Sl. No.
Well No.
61
RL
MP
Depth
Age
(m amsl)
(m agl)
(m)
(Yr)
27°30'40.52"
88
0.37
13.72
94°31'04.10"
27°31'18.17"
97
0.91
187.45
Hand pump
94°31'04.10"
27°31'18.17"
97
0.30
3.66
Dhemaji
Hand pump
94°28'51.25"
27°23'30.11"
87
0.61
24.38
Ghogua
Bordolani
Hand pump
94°27'30.59"
27°21'40.08"
77
0.30
Barmuthani gaon
Bordolani
Hand pump
94°25'18.62"
27°20'36.58"
96
0.30
Locality
Block
Type
Latitude
Longitude
68
Chaporigaon (Goalchapori)
Dhemaji
Hand pump
94°34'28.94"
62
69
Bishnupur PWSS
Dhemaji
Deep Tubewell
63
69A
Bishnupur II
Dhemaji
64
70
Naroathan
65
71
66
72
61
Geology
Geomorph -ology
Location Details
Younger Alluvium
Younger Alluvial Plain
Approchable from Goalchapori tiniali. Opposite residence of Sh. Bimal Chetia, before reaching Juktali L.P. school, beside road.
Younger Alluvium
Younger Alluvial Plain
Approachable from Jamuguri panchali towards north. At Jawhar Navodaya Vidyalaya, Bishnupur.
Younger Alluvium
Younger Alluvial Plain
Hand pump just beside the PWSS
Younger Alluvium
Younger Alluvial Plain
5 km from Botipur on way to Ghilamara. Well is at 3 No. L.P. school, which is about 200m from Naroathan chowk towards north.
10.36
Recent Alluvium
Flood Plain
In front of Ghogua Shiv dole Temple, beside Ghogua Panchyat office/ Girls High school – 3km approx. from Naroathan & approx 4km before Kahikuchi.
7.92
Recent Alluvium
Flood Plain
In the Barmuthani Gaon Ma Moni Aye Than whie approaching from Ghilamara towards Goagamukh.
6
4
Remarks
High Fe, Used after filtering
RL
MP
Depth
Age
(m amsl)
(m agl)
(m)
(Yr)
27°32'02.50"
89
0.91
33.53
Younger Alluvium
Younger Alluvial Plain
8 km from Dhemaji on way to Sisiborgaon. Near Moridhol chariali. At Moridhol PHED PWSS.
94°41'50.70"
27°38'00.73"
129
0.46
9.75
Younger Alluvium
Younger Alluvial Plain
Hand pump inside ammunition Depot.
Deep Tubewell
94°18'37.61"
27°28'45.67"
85
0.80
59.50
Older Alluvium
Piedmont Plain
The site is located in the PHED campus at Tarajan. About 5 km from Gogamukh towards north on NEC road after Mohori Camp.
Bordolani
Hand pump
94°18'37.29"
27°28'45.16"
83
0.30
3.66
Older Alluvium
Piedmont Plain
Near Mohori Camp. Hand pump beside CGWB well.
Lalungaon
Machkhowa
Hand pump
94°37'54.11"
27°32'40.75"
86
0.30
4.88
Younger Alluvium
Younger Alluvial Plain
Between Moridhol and Sisiborgaon. In the residence of Sh. Rambihari Singh
111
Chengalipath ar DTW
Dhemaji
Deep Tubewell
94°31'31.31"
27°26'22.16"
89
0.91
27.43
Younger Alluvium
Younger Alluvial Plain
About 2 km from Telijan tiniali to Gogamukh. Chengali-pathar PHED water supply station.
Low Fe
73
112
Hatigarh PWSS
Dhemaji
Deep Tubewell
94°32'06.46"
27°26'04.15"
90
0.91
27.43
Younger Alluvium
Younger Alluvial Plain
At Hatigarh on Teliajan - Botipur Road. About 2 km from Telijan tiniali.
Very low Fe
74
113
Bherikichuk PWSS (II)
Dhemaji
Deep Tubewell
94°31'29.87"
27°24'23.79"
84
0.91
27.43
Younger Alluvium
Younger Alluvial Plain
At Bherikichuk on Teliajan - Botipur Road. About 400m from the other key well.
Low Fe
Sl. No.
Well No.
67
Locality
Block
Type
Latitude
Longitude
73
Moridhol PWSS (II)
Dhemaji
Deep Tubewell
94°35'46.80"
68
A75
Likhabali II
Sisiborgaon
Hand pump
69
81
Mohoricamp CGWB well 1
Bordolani
70
82
Tarajan
71
99
72
62
16
Geology
Geomorph -ology
Location Details
Remarks
High Fe, Used after filtering
RL
MP
Depth
Age
(m amsl)
(m agl)
(m)
(Yr)
27°23'18.53"
85
0.91
24.38
94°25'01.48"
27°23'12.99"
72
0.37
6.10
Hand pump
94°55'40.67"
27°45'02.96"
112
0.30
Murkong Selek
Hand pump
95°09'03.02"
27°44'42.74"
97
Dali Moromi
Murkong Selek
Hand pump
95°07'02.75"
27°44'15.95"
119
Barmuria Tiniali
Machkhowa
Hand pump
94°44'13.35"
81
120
Kandulijan
Machkhowa
Hand pump
82
121
Pia
Machkhowa
83
122
Gelua
Sisiborgaon
Sl. No.
Well No.
75
Geology
Geomorph -ology
2
Recent Alluvium
5
Location Details
Remarks
Flood Plain
5 km from Botipur on way to Ghilamara. PWSS is about 200m from Naroathan chowk towards south.
Low Fe
Recent Alluvium
Flood Plain
About 5 km south of Bordoloni. Residence of Debidas Hazarika.
High Fe
7.92
Younger Alluvium
Younger Alluvial Plain
Opposite to NH52 Milestone 473. Residence of Krishna Boro.
0.30
7.92
Recent Alluvium
Flood Plain
Near Bandhana Tiniali. Residence of Muniram Doley.
96
0.30
7.92
Recent Alluvium
Flood Plain
Near Barbali Tiniali. Residence of Jatin Doley.
27°32'42.08"
86
0.30
7.62
Younger Alluvium
Younger Alluvial Plain
Near Akajan. Behind Hotel and Residence of Dibakar Pegu.
94°43'56.84"
27°31'13.09"
83
0.30
7.92
Younger Alluvium
Younger Alluvial Plain
South of Kulajan. In the residence of Neheru Kuli.
Hand pump
94°42'48.03"
27°29'58.96"
87
0.61
7.62
Recent Alluvium
Flood Plain
About 6 km south of Kulajan. In the residence of Sharmakanta Pegu.
Hand pump
94°42'35.31"
27°32'15.59"
84
0.30
7.92
Younger Alluvium
Younger Alluvial Plain
On SisiborgaonKulajan Road. Beside GeluaSilkhaguri Primary School.
Locality
Block
Type
Latitude
Longitude
114
Naroathan PWSS (II)
Dhemaji
Deep Tubewell
94°29'02.99"
76
115
Maralchuk
Bordolani
Hand pump
77
116
Dekapam
Murkong Selek
78
117
Naharbijuli
79
118
80
63
3
RL
MP
Depth
Age
(m amsl)
(m agl)
(m)
(Yr)
27°29'43.18"
84
0.30
7.92
Younger Alluvium
Younger Alluvial Plain
On the way to Amguri through Sisiborgaon. Just Beside Gahmara Bazar.
94°40'55.71"
27°33'27.88"
83
0.46
7.47
Younger Alluvium
Younger Alluvial Plain
In the residence of Manak Chutia. Opp. to Sisiborgaon Primary Health Centre.
Hand pump
94°42'01.39"
27°34'42.63"
90
0.61
8.23
Younger Alluvium
Younger Alluvial Plain
Sisipukia Silapathar road. In the residence of Hemanta Konwar.
Murkong Selek
Hand pump
94°57'25.24"
27°41'58.17"
0.15
9.14
1
Younger Alluvium
Younger Alluvial Plain
In Misamora L.P. school, which is about 10 km from Dekapam towards south.
Chamkang
Murkong Selek
Hand pump
94°54'24.49"
27°39'47.03"
93
0.15
9.14
2
Younger Alluvium
Younger Alluvial Plain
In Chamkang govt. primary school, which is about 10 km from Simenchapori towards south.
Tara pump
133
Chamkang Narayanpur
Murkong Selek
Hand pump
94°53'19.78"
27°38'56.83"
100
0.15
9.14
2
Younger Alluvium
Younger Alluvial Plain
In Chamkang Narayan-pur primary school, which is about 12 km from Simenchapori towards south.
Tara pump
134
Kuligaon
Murkong Selek
Hand pump
94°50'40.86"
27°36'32.50"
101
0.61
9.14
1
Recent Alluvium
Flood Plain
In Napam Kuli primary school, which is about 8 km from Bhagwan Charali towards south.
Tara pump
Sl. No.
Well No.
Locality
Block
Type
Latitude
Longitude
84
123
Gahmara
Machkhowa
Hand pump
94°40'02.16"
85
124
Sisipukia
Sisiborgaon
Hand pump
86
125
Kenduguri
Sisiborgaon
87
131
Misamora
88
132
89
90
64
Geology
Geomorph -ology
Location Details
Remarks
Sl. No.
Well No.
Locality
Block
Type
91
135
Dhemaji CH
Dhemaji
Latitude
Longitude
Tube well
94°50'40.86"
27°36'32.50"
RL
MP
Depth
Age
(m amsl)
(m agl)
(m)
(Yr)
90
0.15
9.14
10
Geology
Geomorph -ology
Location Details
Younger Alluvium
Younger Alluvial Plain
Inside Dhemaji Circuit House.
Remarks
92
74
Bijaypur
Murkong Selek
Dug well
95°09'49.32"
27°46'38.64"
122.29
1.00
Younger Alluvium
Younger Alluvial Plain
18 km from 3rd Railcum-Road bridge towards Jonai. 50m east of road in the State Dispensary campus
HNS Well ASDM 04
93
75
Siripani
Machkhowa
Dug well
94°38'23.80"
27°34'03.00"
104.21
0.97
Younger Alluvium
Younger Alluvial Plain
In the campus of Siripani HS school. 23 km from Dhemaji towards Jonai on NH52.
HNS Well ASDM16
94
76
Silapathar
Sisiborgaon
Dug well
94°43'37.56"
27°34'31.80"
114.68
0.98
Younger Alluvium
Younger Alluvial Plain
In the campus of Silapathar Forest IB
HNS Well ASDM15
65
Annexure – II
DETAILS OF HYDROGRAPH NETWORK STATIONS IN DHEMAJI DISTRICT
Well No
Well Type
Latitude
Longitude
M.P. (m agl)
R.L. (m amsl)
Geology
Akajan
ASDM 01
Dug well
27°33'28.80"
94°44'13.56"
1.10
105.66
Alluvium
Bhagaban Ch.
ASDM 02
Dug well
27°39'11.52"
94°47'01.32"
1.05
-NA-
Alluvium
Bijoypur
ASDM 04
Dug well
27°46'38.64"
95°09'49.32"
1.00
122.29
Alluvium
Bordoloni
ASDM 05
Dug well
27°24'48.96"
94°26'26.88"
1.25
95.12
Alluvium
Dhemaji
ASDM 08
Dug well
27°28'50.16"
94°33'46.08"
0.99
102.41
Alluvium
Ghilamara
ASDM 11
Dug well
27°18'23.40"
94°24'23.40"
0.86
93.06
Alluvium
Gogamukh
ASDM 12
Dug well
27°25'52.32"
94°19'06.24"
0.80
96.98
Alluvium
Jonai
ASDM 13
Dug well
27°49'31.80"
95°13'39.72"
0.80
124.36
Alluvium
Siripani
ASDM 16
Dug well
27°34'03.00"
94°38'23.80"
0.45
104.21
Alluvium
Silapathar
ASDM 15
Dug well
27°34'31.80"
94°43'37.56"
0.98
114.68
Alluvium
Sisiborgaon
ASDM 17
Dug well
27°32'11.04"
94°39'34.20"
0.97
108.21
Alluvium
Telem
ASDM 18
Dug well
27°45'57.60"
95°00'39.60"
1.01
126.98
Alluvium
Botipur
8313C3
Dug well
27°23'12.12"
94°31'44.40"
0.84
99.64
Alluvium
Depa
8312D3
Dug well
27°42'10.08"
94°51'20.88"
0.95
-NA-
Alluvium
Dirpai
8313B7
Dug well
27°29'41.64"
94°17'51.72"
0.57
104.69
Alluvium
Machkhowa
8313C2
Dug well
27°23'42.72"
94°37'59.88"
1.10
95.43
Alluvium
Village Present wells
Old Wells
66
Annexure – III
LITHOLOGS OF BOREHOLES DRILLED IN DHEMAJI DISTRICT BY CENTRAL GROUND WATER BOARD
Location: Uriamguri (Borola Mirigaon) From(m)
To(m)
Thickness(m)
Clay with sand
0
3
3
Clayey sand, clay yellowish sticky, sand, yellowish brown , fine grained
3
5
2
Sand, fine grained with little mica flakes, yellowish brown
5
12
7
Lithology
Clay , sticky and plastic , gray
12
18
6
Sand, fine grained ,yellowish brown and gray
18
20
2
Cutting of pebble/boulder of Quartzite, rounded, mixed with sand, medium grained, gray
20
25
5
Sand with mica flakes , medium to fine grained , gray
25
29
4
Sand with clay, in equal proportion, sand fine grained mainly mixed with pebbles, clay sticky
29
30
1
Sand , medium grained , gray
30
32
2
Sand mixed with mica flakes , coarse grained , gray
32
38
6
Coarse sand, gray
38
39
1
Coarse sand, gravel with mica
39
40
1
Coarse sand with mica and cuttings of pebbles, quartzite
40
42
2
From(m)
To(m)
Thickness(m)
Surface soil (clay mixed sand)
0
3
3
Sand, fine, yellow to white with gravel, pebble and pieces of wood
3
6
3
Sand, fine, yellowish mixed with clay and gravel
6
7
1
Sand, white, medium mixed with gravel and pebble with occasional cuttings of boulder
7
11
4
Sand, coarse, mixed with gravel and pebble
11
13
2
Sand, medium, mixed with gravel and pebble and chips of boulders
13
14
1
Sand, medium to coarse, with gravel, pebble and cuttings of boulders
14
20
6
Sand, yellow, fine, mixed with clay, gravel, pebbles and cutting of boulders.
20
22
2
Location: Tarajan, Near Mohori Camp Lithology
67
Sand, fine to coarse, with gravel, pebble and chips of boulders
22
32
10
Gravel, pebble and cutting of boulders
32
34
2
Sand, medium to coarse with gravel and pebble and cutting of boulders
34
40
6
Sand, medium to coarse with gravel and pebble
40
42
2
Sand, fine to medium, brown
42
44
2
Clay, yellow and sticky
44
45
1
Gravel, pebble, cobble and boulder
45
46
1
68
Annexure – IV
SELECTED LITHOLOGS OF BOREHOLES DRILLED IN DHEMAJI DISTRICT BY PRIVATE AGENCIES
Location: Arsia Majhabari Lithology
From
To
Thickness
Gravel
0.00
2.44
2.44
Clay mixed with sand
2.44
4.57
2.13
From (m)
To (m)
Thickness (m)
0.00
7.32
7.32
Clay mixed with sand
7.32
12.50
5.18
Boulder encountered
> 12.5
From (m)
To (m)
Thickness (m)
0.00
7.32
7.32
From (m)
To (m)
Thickness (m)
Clay
0.00
1.52
1.52
Coarse sand with pebble, cobble
1.52
2.13
0.61
Medium to coarse sand (sometimes 1-2 inch clay layer in between)
2.13
15.24
13.11
From (m)
To (m)
Thickness (m)
Top hard soil
0.00
3.05
3.05
Coarse sand
3.05
4.57
1.52
Sticky clay
4.57
6.40
1.83
Coarse sand
6.40
8.84
2.44
Sand mixed with cobble and pebble
8.84
22.86
14.02
Location: Takegitung (PHED Well) Lithology Sand
Location: Gogamukh (Beside Subansiri River, Rupaimukh Village) Lithology Coarse sand Clay
> 7.32
Location: Dhemaji Town (Near College) Lithology
Boulder encounter
> 15.24
Location: Moridhal (Just before reaching bridge) Lithology
69
Location: Kamchi (West of Sripani) Lithology Top hard soil
From (m)
To (m)
Thickness (m)
0.00
3.05
3.05
Clay
3.05
7.62
4.57
Sand mixed with pebble and cobble
7.62
10.67
3.05
From (m)
To (m)
Thickness (m)
Top hard soil
0.00
3.05
3.05
Sand, medium to coarse
3.05
6.10
3.05
Location: Bargaya Deurigaon (Bokajan School) Lithology
Medium sand
6.10
15.24
9.14
Sand mixed with pebble and cobble
15.24
16.15
0.91
Sand, coarse to medium
16.15
22.86
6.71
Location: Mathura gaon Lithology
From (m)
To (m)
Thickness (m)
Top soil
0.00
1.52
1.52
Coarse sand
1.52
15.24
13.72
From (m)
To (m)
Thickness (m)
Topsoil
0.00
3.05
3.05
Sand
3.05
5.49
2.44
Sticky clay
5.49
7.01
1.52
Coarse sand
7.01
15.24
8.23
From (m)
To (m)
Thickness (m)
Coarse sand
0.00
1.52
1.52
Sand with cobble and pebble
1.52
4.57
3.05
Coarse sand
4.57
7.62
3.05
From (m)
To (m)
Thickness (m)
Sticky clay
0.00
6.10
6.10
Sand with cobble and pebble
6.10
9.14
3.05
Sand, coarse grained
9.14
24.38
15.24
Boulder encountered
> 15.24
Location: Akajan Lithology
Boulder encountered
> 15.24
Location: Likhabali Lithology
Location: Naroathan (Kechukhanagaon) Lithology
70
Location: Barmuthanigaon Lithology
From (m)
To (m)
Thickness (m)
Sticky clay, blackish
0.00
12.19
12.19
Sand, coarse grained
12.19
24.38
12.19
Location: Deuri Barbam Lithology
From (m)
To (m)
Thickness (m)
Sand, fine grained
0.00
15.24
15.24
Boulder encounter
> 15.24
From (m)
To (m)
Thickness (m)
Clay, sticky
0.00
6.10
6.10
Sand, coarse and fine mixed
6.10
18.29
12.19
From (m)
To (m)
Thickness (m)
0.00
24.38
24.38
From (m)
To (m)
Thickness (m)
0.00
15.24
15.24
Location: Goalchapori Lithology
Pebbles and cobbles encountered
> 18.29
Location: Kendugurigaon Lithology Sand Pebbles and cobbles encountered
> 24.38
Location: Barmuthanigaon Lithology Sand, fine grained Pebbles and cobbles encountered
> 15.24
Location: Jamuguri Lithology
From (m)
To (m)
Thickness (m)
Clay
0.00
6.10
6.10
Sand
6.10
21.34
15.24
From (m)
To (m)
Thickness (m)
0.00
12.19
12.19
12.19
15.24
3.05
From (m)
To (m)
Thickness (m)
Sand, fine grained
0.00
1.52
1.52
Clay, sticky
1.52
6.10
4.57
Sand, fine grained
6.10
12.19
6.10
Location: Shripani (Near Gai Deori) Lithology Clay, sticky Sand, fine grained Boulder encountered
> 15.24
Location: Dhemaji Town Lithology
71
Sand, coarse grained
12.19
21.34
9.14
From (m)
To (m)
Thickness (m)
Clay
0.00
6.10
6.10
Sand
6.10
15.24
9.14
15.24
24.38
9.14
From (m)
To (m)
Thickness (m)
Surface soil
0.00
3.00
3.00
Surface soil mixed with sand
3.00
6.50
3.50
Sand, fine grained
6.50
9.50
3.00
Sand
9.50
17.80
8.30
From (m)
To (m)
Thickness (m)
Surface soil
0.00
7.50
7.50
Sand, fine grained
7.50
10.20
2.70
Sand, coarse grained, mixed with gravel
10.20
19.80
9.60
Boulder encountered
> 19.8
From (m)
To (m)
Thickness (m)
Surface soil
0.00
8.20
8.20
Sand, fine grained
8.20
13.50
5.30
Sand, coarse grained
13.50
29.70
16.20
Boulder encountered
> 29.7
From (m)
To (m)
Thickness (m)
Suface soil
0.00
4.10
4.10
Sand, fine grained
4.10
7.15
3.05
Sand, coarse grained
7.15
23.05
15.90
From (m)
To (m)
Thickness (m)
Clay, sticky
0.00
0.61
0.61
Pebbles, cobbles
0.61
3.05
2.44
Sand, coarse grained, whitish
3.05
6.10
3.05
6.10
7.92
1.83
Location: Chowkhamgaon Lithology
Sand, Pebble, cobble Location: Limekuri Lithology
Location: Round Miri Lithology
Location: Dekapam Lithology
Location: Telem Lithology
Location: Laipulia Lithology
Sand mixed with pebble Boulder encountered
> 7.92
72
Location: Santipur Ranganadi Lithology Sand, fine to medium grained, reddish
From (m)
To (m)
Thickness (m)
0.00
12.19
12.19
12.19
18.29
6.10
From (m)
To (m)
Thickness (m)
Clay, sticky, blackish
0.00
6.10
6.10
Sand, coarse grained
6.10
6.71
0.61
Clay, sticky, blackish
6.71
7.32
0.61
Sand, fine to medium grained, blackish
7.32
10.67
3.35
From (m)
To (m)
Thickness (m)
Sand, coarse grained
0.00
1.52
1.52
Clay, sticky, redish
1.52
2.44
0.91
Sand, coarse grained
2.44
4.88
2.44
Clay, sticky, grayish
4.88
6.10
1.22
Sand, fine mixed with coarse
6.10
7.62
1.52
Sand, coarse grained, whitish Location: Dhemaji Town (In the bus stand) Lithology
Location: Nalbari Lithology
Clay, sticky, bluish
7.62
10.67
3.05
10.67
11.89
1.22
From (m)
To (m)
Thickness (m)
Sand, fine grained
0.00
4.57
4.57
Clay, sticky
4.57
9.14
4.57
Sand, coarse grained
9.14
10.67
1.52
Clay, sticky, blackish
10.67
12.19
1.52
Sand, coarse grained
12.19
13.72
1.52
Clay, sticky, blackish
13.72
18.29
4.57
Sand, coarse grained
18.29
19.81
1.52
From (m)
To (m)
Thickness (m)
Sand, fine grained, whitish
0.00
4.88
4.88
Sandy clay, whitish
4.88
6.40
1.52
Sand, coarse grained, whitish
6.40
9.14
2.74
Sand, coarse grained, whitish Location: Kothalguri (PHED well) Lithology
Location: Borgaon (Bogori Baligaon) Lithology
73
Location: Goalchapori Lithology
From (m)
To (m)
Thickness (m)
Sand, fine grained, reddish
0.00
6.10
6.10
Clay, sticky, blackish
6.10
6.71
0.61
Sand, fine grained, yellowish
6.71
9.75
3.05
Sand, coarse grained
9.75
19.81
10.06
From (m)
To (m)
Thickness (m)
Clayey sand, light yellowish
0.00
1.83
1.83
Clay, sticky, blackish
1.83
3.05
1.22
Sand, coarse grained, yellowish
3.05
4.57
1.52
Clay, sticky, blackish
4.57
7.62
3.05
Sand, coarse grained, light yellowish
7.62
13.72
6.10
From (m)
To (m)
Thickness (m)
Sandy clay, grayish
0.00
3.05
3.05
Sand, medium to fine grained, light yellowish
3.05
4.57
1.52
Sand, coarse grained, light yellowish
4.57
15.24
10.67
From (m)
To (m)
Thickness (m)
Location: Koyakhola Lithology
Location: Naoali Bhojugaon Lithology
Location: Dhemaji Town (SP office quarter) Lithology Sand, coarse grained, whitish
0.00
3.66
3.66
Clay, sticky, blackish
3.66
12.19
8.53
12.19
15.24
3.05
From (m)
To (m)
Thickness (m)
Clay, sticky, blackish
0.00
2.44
2.44
Sand, coarse grained, reddish
2.44
4.57
2.13
From (m)
To (m)
Thickness (m)
Clay, sticky, blackish
0.00
4.57
4.57
Sand, very fine grained, reddish
4.57
6.10
1.52
Sand, coarse grained, reddish
6.10
14.02
7.92
From (m)
To (m)
Thickness (m)
0.00
18.29
18.29
Sand, fine grained, blackish Location: Nagakhelia Lithology
Location: Lachit Nagar (Beside hospital) Lithology
Location: Nalanipam Lithology Clay, sticky, blackish
74
Location: Bongalmari Lithology
From (m)
To (m)
Thickness (m)
Sand, fine grained, reddish
0.00
2.44
2.44
Clay, sticky, blackish
2.44
3.05
0.61
Sand, medium grained, whitish
3.05
6.10
3.05
Sand, medium grained, reddish
6.10
7.01
0.91
Sand, coarse grained, blackish
7.01
14.02
7.01
From (m)
To (m)
Thickness (m)
Sand, medium grained, reddish
0.00
1.52
1.52
Clay, sticky, blackish
1.52
3.66
2.13
Sand, coarse grained, whitish
3.66
4.27
0.61
Clay, sticky, blackish
4.27
12.19
7.92
12.19
18.29
6.10
From (m)
To (m)
Thickness (m)
Sand, fine grained, reddish
0.00
3.05
3.05
Clay, sticky
3.05
3.66
0.61
Location: Sisiborgaon (Police Thana campus) Lithology
Sand, coarse grained, whitish Location: Raitingaon Lithology
Sand, coarse grained, whitish
3.66
13.72
10.06
Pebbles, cobbles
13.72
14.33
0.61
Sand, coarse grained, whitish
14.33
18.29
3.96
Location: Takobari Lithology
From (m)
To (m)
Thickness (m)
Clay, sticky, blackish
0.00
5.49
5.49
Pebbles, cobbles
5.49
6.10
0.61
Sand, coarse grained, whitish
6.10
23.16
17.07
From (m)
To (m)
Thickness (m)
Clay with fine sand
0.00
3.00
3.00
Grey fine sand
3.00
6.00
3.00
Location: Hatipara (Irrigation DTW) Lithology
Fine sand
6.00
12.20
6.20
Fine to medium sand
12.20
15.20
3.00
Medium sand
15.20
24.30
9.10
Sand with gravel
24.30
27.40
3.10
Sand with gravel and boulder
27.40
30.50
3.10
Boulder cutting
30.50
42.70
12.20
Sand with gravel and boulder cuttings
42.70
54.90
12.20
75
Boulder cutting
54.90
57.90
3.00
Large boulder cutting
57.90
64.00
6.10
Sand with gravel
64.00
67.10
3.10
Sand with gravel and boulder cuttings
67.10
76.20
9.10
Medium sand with gravel
76.20
82.30
6.10
From (m)
To (m)
Thickness (m)
Fine sand and silt
0.00
3.04
3.04
Fine to medium sand
3.04
9.12
6.08
Coarse sand with pebbles
9.12
15.20
6.08
Boulder cutting
15.20
21.28
6.08
Gravel cutting
21.28
24.32
3.04
Boulder cutting
24.32
27.36
3.04
Large boulder cutting
27.36
30.40
3.04
Large boulder cuttings with coal
30.40
33.50
3.10
Large boulder cutting with pebbles
33.50
45.72
12.22
Boulder cutting with pebbles
45.72
48.76
3.04
Large boulder cutting
48.76
51.80
3.04
From (m)
To (m)
Thickness (m)
Location: Gogamukh (Irrigation DTW) Lithology
Location: Bishnupur (Jawahar Navodaya Vidyalaya DTW) Lithology Fine sand
0.00
15.20
15.20
Medium sand
15.20
24.32
9.12
Medium to coarse sand with boulder
24.32
57.36
33.44
Clay
57.76
66.88
9.12
Medium sand
66.88
69.92
3.04
Clay
69.92
94.24
24.32
Medium sand
94.24
97.28
3.04
Clay
97.28
124.64
27.36
124.64
130.72
6.08
Clay
130.72
155.34
24.62
Coarse sand with boulder
155.34
171.46
16.11
Medium sand with boulder
171.46
187.45
15.99
Medium sand with boulder
76
Annexure – V
RESULTS OF CHEMICAL ANALYSIS OF SAMPLES FROM KEY SAMPLING WELLS
Sam. No.
Locality
PreMonsoon
PostMonsoon
Pre-Monsoon
Pre-Monsoon
PreMonsoon
Post-Monsoon
Field values
Field values
Analyzed by CGWB-NER
Analyzed by CGWB, Hyderabad
Analyzed by NERIWALM
Analyzed by CGWB, Hyderabad
pH
EC
pH
EC
pH
EC
TDS (ppm)
Cl (ppm)
F (ppm)
Fe (ppm)
As (ppm)
As (ppb)
As (ppb)
Fe (ppm)
As (ppb)
1
Goalchapori
-
309
6.6
321
7.3
183
113
11.0
0.51
31.0
0.044
44
48.08
31.0
54.3
2
Moridhol
-
378
6.3
512
7.5
277
172
21.0
0.34
32.0
0.022
22
108.40
47.5
109.6
3
Moridhol Hachwa
-
325
6.5
337
7.5
283
175
7.1
0.07
14.0
0.018
18
11.18
16.7
17.3
5
Raichapori Lachomgaon
-
376
-
-
7.4
212
131
21.0
0.23
65.0
0.029
29
18.40
39.3
31.8
6
Jamuguri
-
385
-
-
7.5
301
187
18.0
0.50
22.0
0.079
79
65.64
17.8
108.5
8
Santipur Konch Gaon
-
239
6.7
-
7.5
222
137
7.1
0.38
3.3
0.082
82
76.95
6.7
100.1
9
Theckjuri
-
148
-
-
7.6
228
141
25.0
0.14
13.0
0.026
26
14.97
-
-
10
Jiyadhol Tingharia
-
255
6.4
324
7.6
178
110
21.0
0.19
48.0
0.018
18
7.79
49.2
15.7
12
Teliajan
-
394
6.6
442
7.5
324
201
53.0
0.04
69.0
0.026
26
17.74
40.2
52.4
13
Dhemaji
-
305
6.8
379
7.5
320
198
43.0
-BDL-
1.0
0.002
2
0.00
0.4
-BDL-
14
Dhemaji I PWSS
-
281
6.5
240
7.7
265
164
14.0
0.08
4.7
0.008
8
4.66
8.7
-BDL-
15
Matikhola PWSS
-
256
-
-
7.5
201
125
11.0
0.38
18.0
0.064
64
62.02
-
-
16
Matikhola HP
-
205
6.6
222
7.6
244
151
18.0
0.05
1.1
0.001
1
10.00
0.4
-BDL-
77
Sam. No.
Locality
PreMonsoon
PostMonsoon
Pre-Monsoon
Pre-Monsoon
PreMonsoon
Post-Monsoon
Field values
Field values
Analyzed by CGWB-NER
Analyzed by CGWB, Hyderabad
Analyzed by NERIWALM
Analyzed by CGWB, Hyderabad
pH
EC
pH
EC
pH
EC
TDS (ppm)
Cl (ppm)
F (ppm)
Fe (ppm)
As (ppm)
As (ppb)
As (ppb)
Fe (ppm)
As (ppb)
17
Chengalipathar
-
60
6.2
314
7.5
81
50
14.0
-BDL-
2.8
-BDL-
-BDL-
0.00
0.8
-BDL-
18
Samajan
-
603
6.8
525
7.6
414
257
14.0
-BDL-
42.0
0.009
9
12.28
46.2
-BDL-
19
Borbila Chutakia
6.3
54
5.8
61
7.5
78
48
7.1
-BDL-
2.3
0.003
3
0.00
0.3
-BDL-
20
Majgaon (Lalukjan)
-
216
6.3
172
7.5
220
136
11.0
-BDL-
2.7
0.017
17
33.00
2.7
17.2
21
Kamalpur (Lalukijan Dharmapur)
6.3
293
-
-
7.6
194
120
7.1
0.23
31.0
0.147
147
194.50
-
-
22
Dihingia Barbam
-
202
-
-
7.6
168
104
14.0
-BDL-
21.0
0.006
6
0.00
-
-
23
Deuri Barbam
6.9
185
6.4
128
7.4
197
122
18.0
-BDL-
2.5
0.003
3
0.76
0.3
5.4
24
Bordoloni
-
345
6.4
347
7.6
336
208
21.0
-BDL-
2.1
0.013
13
6.39
7.9
11.4
25
Bhebali
-
340
6.6
178
7.6
285
177
14.0
0.06
22.0
0.015
15
9.00
14.7
10.0
26
Betbari
7.2
301
6.6
252
6.6
240
149
14.0
0.13
24.0
0.023
23
38.23
19.5
40.3
27
Bhekali
7.1
131
6.2
180
7.6
125
78
14.0
0.01
2.1
0.016
16
13.09
4.6
14.7
28
Mohoricamp Tiniali
-
299
6.4
328
7.5
256
159
25.0
0.07
15.0
0.02
20
13.59
15.7
11.2
29
Dirpai
-
272
6.4
178
7.4
250
155
39.0
-BDL-
30.0
0.002
2
3.84
10.0
-BDL-
30
Borolagaon
-
180
6.3
196
7.4
155
96
25.0
-BDL-
17.0
0.009
9
2.76
12.7
-BDL-
31
Gogamukh
-
845
6.4
804
7.6
700
434
96.0
-BDL-
36.0
0.059
59
85.62
28.8
29.8
32
Bherikichuk
-
185
6.5
128
7.6
201
125
14.0
0.09
3.5
0.001
1
0.73
2.2
-BDL-
33
Botipur
-
305
6.3
537
7.7
317
197
18.0
-BDL-
0.7
-BDL-
-BDL-
0.00
0.5
-BDL-
78
Sam. No.
Locality
PreMonsoon
PostMonsoon
Pre-Monsoon
Pre-Monsoon
PreMonsoon
Post-Monsoon
Field values
Field values
Analyzed by CGWB-NER
Analyzed by CGWB, Hyderabad
Analyzed by NERIWALM
Analyzed by CGWB, Hyderabad
pH
EC
pH
EC
pH
EC
TDS (ppm)
Cl (ppm)
F (ppm)
Fe (ppm)
As (ppm)
As (ppb)
As (ppb)
Fe (ppm)
As (ppb)
34
Latakgaon
-
270
6.7
237
7.7
272
169
18.0
-BDL-
1.5
0.0005
0.5
0.00
0.6
-BDL-
35
Bordoibum
-
168
6.6
387
7.7
143
89
7.1
0.32
6.7
0.102
102
93.86
12.3
86.2
36
Sisiborgaon
-
295
6.4
286
7.6
179
111
14.0
0.16
36.0
0.001
1
35.91
26.4
29.9
37
Kulajan
-
295
6.5
297
7.6
316
196
21.0
0.15
0.8
0.002
2
5.66
0.8
11.3
38
Akajan
-
166
6.5
374
7.6
124
77
7.1
-BDL-
18.0
-BDL-
-BDL-
6.11
16.7
38.9
A39
Silapathar
-
334
6.4
329
7.5
210
130
21.0
0.14
38.0
-BDL-
-BDL-
32.00
31.0
-BDL-
A40
Madhuripathar
-
449
6.5
406
7.5
375
233
35.0
0.05
3.9
-BDL-
-BDL-
0.06
0.4
-BDL-
A41
Likhabali MES WSS
-
172
6.3
171
7.5
174
109
7.1
0.08
0.3
-BDL-
-BDL-
0.00
0.1
29.1
A44
Shripani
7.10
228
6.5
238
7.5
132
82
7.1
0.08
29.0
0.02
20
43.18
25.5
57.8
47
Bhagaban Chariali
-
111
6.3
128
7.5
108
67
7.1
-BDL-
4.6
0.0008
0.8
0.00
0.7
-BDL-
48
Depa
-
48
6.3
48
7.0
53
33
7.1
-BDL-
0.7
-BDL-
-BDL-
0.00
0.4
-BDL-
49
Simenchapori
-
187
6.3
155
7.1
115
71
18.0
0.24
31.0
0.011
11
4.42
13.3
-BDL-
51
Telem (Kaman Selek)
-
101
6.1
71
7.1
69
43
7.1
-BDL-
1.1
-BDL-
-BDL-
0.00
0.4
13.4
52
Limekuri
-
79
6.0
49
7.1
81
50
7.1
-BDL-
2.3
-BDL-
-BDL-
0.00
0.2
-BDL-
53
Gali
-
231
6.1
221
7.0
256
159
43.0
-BDL-
3.9
-BDL-
-BDL-
0.00
0.4
-BDL-
54
Bijoypur
-
89
6.3
67
7.2
81
50
3.5
-BDL-
10.0
-BDL-
-BDL-
0.00
4.4
-BDL-
55
Jonai
-
-
6.2
156
7.3
148
92
20.0
-BDL-
32.0
-BDL-
-BDL-
0.00
2.3
-BDL-
79
Sam. No.
PreMonsoon
PostMonsoon
Pre-Monsoon
Pre-Monsoon
PreMonsoon
Post-Monsoon
Field values
Field values
Analyzed by CGWB-NER
Analyzed by CGWB, Hyderabad
Analyzed by NERIWALM
Analyzed by CGWB, Hyderabad
Locality
pH
EC
pH
EC
pH
EC
TDS (ppm)
Cl (ppm)
F (ppm)
Fe (ppm)
As (ppm)
As (ppb)
As (ppb)
Fe (ppm)
As (ppb)
56
Jonai II PWSS
-
-
6.2
194
7.3
160
99
11.0
-BDL-
18.0
0.007
7
0.00
9.5
10.6
57
Bahir Jonai
-
230
6.8
226
7.6
237
147
7.1
-BDL-
0.0
0.002
2
0.00
0.6
-BDL-
58
Kachari Baligaon
-
381
5.7
-
7.4
262
162
11.0
0.38
39.0
0.108
108
51.07
32.1
59.4
59
Naharbari
-
313
5.8
367
7.6
318
197
14.0
0.07
26.0
0.016
16
3.95
17.6
-BDL-
60
Lachitnagar (Khubulia)
-
233
6.3
233
7.5
222
138
14.0
0.12
11.0
0.011
11
0.00
5.8
12.1
61
Juktali
-
371
6.4
380
7.5
275
171
11.0
0.29
33.0
0.024
24
20.65
24.9
28.8
62
Jamuguri (Moridhol)
-
269
6.4
328
7.5
202
125
7.1
0.27
23.0
0.022
22
145.30
22.7
66.5
63
Bhekeli (II)
7.0
328
6.3
302
7.4
221
137
7.1
0.26
37.0
0.249
249
417.20
23.6
75.8
64
Lalukijan Dharmapur (II)
6.0
288
-
-
7.5
232
144
7.1
0.50
24.0
0.178
178
199.90
-
-
65
Lalukijan Majgaon (II)
-
138
6.6
162
7.4
146
91
11.0
0.23
5.2
-BDL-
-BDL-
0.00
2.3
-BDL-
66
Barbam Garubandha
-
200
6.5
128
7.3
149
92
11.0
0.29
20.0
0.02
20
13.55
10.6
34.1
67
Dhemaji (II)
-
375
6.8
382
7.4
290
180
46.0
-BDL-
35.0
0.008
8
153.00
22.2
36.0
68
Chaporigaon (Goalchapori)
-
240
6.6
238
7.4
172
107
0.2
0.23
28.0
0.015
15
1.09
17.5
18.8
69
Brishnupur PWSS
-
400
5.8
-
7.5
352
218
11.0
-BDL-
23.0
0.008
8
0.00
15.0
16.7
Brishnupur II
-
240
-
-
7.5
131
81
7.1
-BDL-
30.0
0.009
9
0.00
-
-
70
Naroathan
-
179
6.7
218
7.4
204
126
18.0
-BDL-
0.0
0.007
7
0.00
Tr
-BDL-
73
Moridhol PWSS (II)
-
315
-
-
7.5
251
156
18.0
0.07
24.0
0.054
54
20.23
-
-
69A
80
Sam. No.
PreMonsoon
PostMonsoon
Pre-Monsoon
Pre-Monsoon
PreMonsoon
Post-Monsoon
Field values
Field values
Analyzed by CGWB-NER
Analyzed by CGWB, Hyderabad
Analyzed by NERIWALM
Analyzed by CGWB, Hyderabad
Locality
TDS (ppm)
Cl (ppm)
F (ppm)
Fe (ppm)
As (ppm)
As (ppb)
Fe (ppm)
As (ppb)
303
180
7.1
0.55
13.0
0.054
54
29.28
8.6
50.2
7.6
339
210
21.0
0.13
22.0
-BDL-
-BDL-
19.64
-
-
328
7.6
326
202
21.0
0.09
7.0
-BDL-
-BDL-
0.00
3.8
-BDL-
6.3
753
7.6
598
371
60.0
0.27
40.0
0.093
93
69.06
33.9
57.8
-
6.5
128
-
-
-
-
-
-
-
-
-
7.8
-BDL-
-
-
6.6
93
-
-
-
-
-
-
-
-
-
0.9
-BDL-
Chengalipathar DTW
-
-
6.1
178
-
-
-
-
-
-
-
-
-
2.3
-BDL-
112
Hatigarh PWSS
-
-
6.6
322
-
-
-
-
-
-
-
-
-
3.3
-BDL-
113
Bherikichuk PWSS (II)
-
-
6.3
316
-
-
-
-
-
-
-
-
-
8.5
19.8
114
Naroathan PWSS (II)
-
-
6.8
125
-
-
-
-
-
-
-
-
-
0.7
-BDL-
115
Maralchuk
-
-
6.5
344
-
-
-
-
-
-
-
-
-
32.2
19.9
116
Dekapam
-
-
6.1
256
-
-
-
-
-
-
-
-
-
0.6
11.0
117
Naharbijuli
-
-
6.3
126
-
-
-
-
-
-
-
-
-
0.8
-BDL-
118
Dali Moromi
-
-
6.5
318
-
-
-
-
-
-
-
-
-
40.0
43.9
119
Barmurai Tiniali
-
-
6.5
328
-
-
-
-
-
-
-
-
-
23.5
35.9
120
Kandulijan
-
-
6.4
381
-
-
-
-
-
-
-
-
-
0.3
-BDL-
121
Pia
-
-
6.5
221
-
-
-
-
-
-
-
-
-
0.2
-BDL-
pH
EC
pH
EC
pH
EC
Likhabali II
-
364
6.5
368
7.5
81
Mohoricamp CGWB Well
-
371
-
-
82
Tarajan
-
308
6.4
99
Lalunggaon
6.9
801
71
Ghogua
-
72
Barmuthanigaon
111
A75
81
As (ppb)
Sam. No.
Locality
PreMonsoon
PostMonsoon
Pre-Monsoon
Pre-Monsoon
PreMonsoon
Post-Monsoon
Field values
Field values
Analyzed by CGWB-NER
Analyzed by CGWB, Hyderabad
Analyzed by NERIWALM
Analyzed by CGWB, Hyderabad
pH
EC
pH
EC
pH
EC
TDS (ppm)
Cl (ppm)
F (ppm)
Fe (ppm)
As (ppm)
As (ppb)
As (ppb)
Fe (ppm)
As (ppb)
122
Gelua
-
-
6.4
215
-
-
-
-
-
-
-
-
-
11.1
43.6
123
Gahmara
-
-
6.4
202
-
-
-
-
-
-
-
-
-
9.7
51.6
124
Sisipukia
-
-
6.1
62
-
-
-
-
-
-
-
-
-
0.2
-BDL-
125
Kenduguri
-
-
6.3
162
-
-
-
-
-
-
-
-
-
12.7
24.1
74
Bijoypur
-
-
-
-
-
-
-
-
-
0.0
0.000
-
0.00
-
-
75
Siripani
-
-
-
-
-
-
-
-
-
0.0
0.001
-
0.00
-
-
76
Silapathar
-
311
6.8
-
-
-
-
-
-
1.2
0.000
-
0.00
-
-
131
Misamora
-
-
6.8
-
-
-
-
-
-
-
-
-
-
-
-
132
Chamkang
-
-
6.6
-
-
-
-
-
-
-
-
-
-
-
-
82
Annexure – VI
RESULTS OF CHEMICAL ANALYSIS OF DUPLICATE WATER SAMPLES Locality
Goalchapori
Jamuguri
Well No.
1
6
Modified Key Well No
39
CGWB, SR
Sample st
NERIWALM
Fe (ppm)
As (ppb)
As (ppb)
1
Goalchapori
1 sample
31
44
48
76
Goalgaon
2nd sample
41
39
26
22
79
66
sample
25
78
0
1 sample
38
0
32
31
1
29
6 6A
Silapathar
Modified Location
39 75
Jamuguri Jamuguri II Silapathar Silajan
st
1 sample nd
2
st
nd
2
83
sample
Annexure – VII
RESULTS OF CHEMICAL ANALYSIS OF FILTERED WATER SAMPLES Pre-Monsoon Sam. No.
Well No.
Locality
Analyzed by NERIWALM
Analyzed by CGWB, Hyderabad
Analyzed by CGWB-NER
pH
EC
TDS (ppm)
Cl (ppm)
F (ppm)
Fe (ppm)
As (ppm)
As (ppb)
As (ppb)
6A
6
Jamuguri
7.6
359
223
18
0.64
0.35
0.008
8
-Nil-
12A
12
Teliajan
7.5
357
221
60
-BDL-
0.88
0.002
2
-Nil-
84
Annexure – VIII
RESULTS OF SURVEY ON FOOD HABIT AND DRINKING WATER Sl. No.
Name/Sex /Age
1
Gopinath Boro /M /42
2
Bhaba Saikia /M /39
3
Padasingh Bora /M /28
Key well No.
Locality
Occupation
Income group
Drinking water Source
Filtered (Yes/No)
Betel nut
Hand pump
Yes
Home made Sand Filter
-
Dal, Potato
Fish once in a week, Meat once in 5-6 months
Betel nut
Hand pump
Yes
Home made Sand Filter
-
Rice
Dal, Potato
Fish once in a week, Meat once in 5-6 months, Dry Fish
Betel nut
Hand pump
Yes
Home made Sand Filter
-
Rice
Green Vegetables mainly
Fish 2-3 times in a week, Meat once in a month.
Betel nut, Tea
Hand pump
Yes
Commercial Porcelain Candle Filter
Fish once in a week, Meat twice in a month.
Betel nut
Hand pump
Yes
Home made Sand Filter
-
Fish once in a week, Meat twice in a month.
Betel nut
Hand pump
Yes
Home made Sand Filter
-
Main food
Subsidiary Food
Consumption of Non-veg food
Dal, Potato
Fish once in a week, Meat once in 5-6 months
8
Shantipur Konchgaon
8
Shantipur Konchgaon
Farmer
8
Shantipur Konchgaon
Agricultural labour
Teliajan
Retd. Govt. Servant
Medium
Rice
Green vegetables mainly
Medium
Rice
Dal, Potato
Farmer
4
Arun Baruah /M /67
5
Chandra Bora /M /46
17
Chengalipathar
Village Head
6
Nakul Chetia /M / 32
17
Chengalipathar
Farmer
12
Low
Low
Low
Medium
Rice
Rice
85
Other
Type of filter
Any lingering Disease
Skin Disease
Other
Drinking water Source
Filtered (Yes/No)
Type of filter
Any lingering Disease
Dal, Potato
Fish 3-4 times in a week, Meat once in a month.
Betel nut, Tea
Hand pump
Yes
Commercial Porcelain Candle Filter
-
Rice
Green vegetables
Fish & Meat maximum
Betel nut
Hand pump
Yes
Home made Sand Filter
-
Medium
Rice
Green vegetables
Fish & Meat maximum
Betel nut
Hand pump
Yes
Home made Sand Filter
-
Farmer
Low
Rice
Green vegetables mainly
Fish / Meat not much
Betel nut
Hand pump
Yes
Home made Sand Filter
-
Jamukguri
Farmer
Low
Rice
Green vegetables mainly
Fish / Meat not much
Betel nut
Hand pump
Yes
Home made Sand Filter
-
3
Moridhal Hachwa
Farmer
Low
Rice
Green vegetables mainly
Fish / Meat not much
Betel nut
Hand pump
Yes
Home made Sand Filter
-
58
Kachari Baligaon
Rice
Green vegetables mainly
Fish / Meat once or twice a week
Betel nut
Hand pump
Yes
Home made Sand Filter
-
14
Numal Taye /M /42
5
Raichapori Lachumgaon
Farmer
Medium
Rice
Green vegetables mainly
Fish / Meat once or twice a week
Betel nut
Hand pump
Yes
Home made Sand Filter
15
Shibut Das /M /49
6
Jamuguri
Farmer
Medium
Rice
Green vegetables
Fish / Meat once / twice
Betel nut
Hand pump
Yes
Home made Sand Filter
Sl. No.
Name/Sex /Age
7
Bhadreswar Ghosh /M /43
8
Key well No.
Subsidiary Food
Consumption of Non-veg food
Rice
Medium
Farmer
Juktali
62
Locality
Occupation
10
Jiadhol
Govt. servant
Medium
Donai Naro /M /36
59
Naharbari
Farmer
9
Gobinda Sonwal /M /53
59
Naharbari
10
Kumar Chinte /M /21
61
11
Gopal Lahon /M /36
12
Kakoi Hatimuria /M /35
13
Bolin Kochari /M /37
Farmer
Income group
Low
Main food
86
Skin Disease
-
Sl. No.
Name/Sex /Age
Key well No.
Locality
Occupation
Income group
Subsidiary Food
Consumption of Non-veg food
Drinking water Source
Filtered (Yes/No)
mainly
a week
Rice
Green vegetables mainly
Fish / Meat once or twice a week
Betel nut
Hand pump
Yes
Home made Sand Filter
-
Rice
Green vegetables mainly
Fish regular. Meat once or twice a week
Betel nut
Hand pump
Yes
Home made Sand Filter
-
Rice
Green vegetables mainly
Fish / Meat once or twice a week
Betel nut
Hand pump
Yes
Home made Sand Filter
-
Fish once in a week, Meat once in 2-3 months
Betel nut
Hand pump
Yes
Home made Sand Filter
-
Fish rarely, Meat once in 2-3 months
Betel nut, Occasiona l Tea
Hand pump
Yes
Home made Sand Filter
-
Main food
16
Ananda Kalita /M /26
17
Cheniram Barpatra /M /55
18
Baneswar Dihingia /M /48
19
Bhabanipras ad Rijal /M /43
65
Lakukijan
Farmer
Low
Rice
Green vegetables mainly
20
Brishnu Deori /M /39
23
Deuri Barbam
Farmer
Low
Rice
Green vegetables mainly
6
32
32
Jamuguri
Bherikichuk
Bherikichuk
Farmer
Farmer
Farmer
Medium
Medium
Medium
87
Other
Type of filter
Any lingering Disease
Annexure –IX
SELECTED STANDARDS FOR PHYSICAL, CHEMICAL AND BIOLOGICAL QUALITY OF DRINKING WATER
Quality Parameters
Bureau of Indian Standards (2003) (BIS: IS: 10500, 2003) Highest desirable
Maximum permissible
WHO Guideline value (2004)
Physical Turbidity (JTU)
2.5
10
-
5
25
-
Unobjectionable
Unobjectionable
-
6.5-8.5
6.5-9.2
6.5-8.5
Total hardness (as CaCO3 in mg/l)
300
600
500
TDS
500
1500
1000
Calcium (mg/l)
75
200
-
Magnesium (mg/l)
30
100
-
0.3
1
0.3
Manganese (mg/l)
0.05
0.5
0.4
Copper (mg/l)
0.05
1.5
2
Sodium (mg/l)
-No standard-
-No standard-
-No standard-
Potassium (mg/l)
-No standard-
-No standard-
-No standard-
200
400
400
Nitrate (mg/l)
45
No relaxation
50
Chloride (mg/l)
250
1000
250
Fluoride (mg/l)
1
1.5
1.5
Cadmium (mg/l)
0.01
No relaxation
0.003
Lead (mg/l)
0.05
No relaxation
0.01
Zinc (mg/l)
5
15
-No standard-
Chromium (mg/l)
0.05
0.1
0.05
Arsenic (mg/l)
0.01
No relaxation
0.01
Antimony (mg/l)
0.006
No relaxation
0.005
Aluminium (mg/l)
0.03
0.2
-No standard-
2
No relaxation
0.7
Absent
0.0002
-No standard-
Colour (Hazen unit) Taste and Odour pH
Chemical
Iron (mg/l)
Sulphate (mg/l)
Barium (mg/l) Beryllium (mg/l)
88
Cyanide (mg/l)
0.05
0.05
0.07
Mercury (mg/l)
0.001
No relaxation
0.001
Selenium (mg/l)
0.01
0.1
0.01
1
5
0.3
200
600
Absent
0.001
1
10
0
α Particle
0-4 ρC/yr
No relaxation
1 Bq/I
β Particle
0-15 ρC/yr
No relaxation
0.1 Bq/I
0-5 ρC/yr
No relaxation
-
Boron (mg/l) Alkalinity (as CaCO3 in mg/l) Pesticides (µg/l)
Species Specific
Biological Pathogens (Coliform) Radiological
Radium
89