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FINAL REPORT
MADHYA PRADESH
WATER RESOURCES DEPARTEMENT
HYDROLOGY PROJECT PHASE – II
WORLD BANK AIDED
FINAL REPORT
OF
Ground Water Purpose Driven Study by Applying
Aquifer Modification Technique Hydrofracking, in the
existing Ground Water Abstraction Structures built on
Hydrogeological Unit in Part of Rohini Watershed of
Dhasan Basin
SEPTEMBER – 2013
Chief Engineer (BODHI)
(Water Resources Department )
Bhopal (M.P.)
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Hydrofracking Unit
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Supervised by Shri. C. S. Ramteke
Superintending Geohydrologist
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Hydofracking Work Operation
Guided by
Shri R N SHARMA
Retired Director
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Content:-
Part 1
(a) Executive Summary
(b) Acknowledgement
(c) Location and approachability
Part – II
Pre investigation activity
(a) Introduction
(b) Geo morphology
(c) Drainage
(d) Soil
(e) Geological Setup
(f) Hydrological condition
(f.1) History of ground water level
(f.2) Ground water contour
(g) Basic Problems
(h) Diagnosis
(i) Inferences
(j) Basic Objectives
Part – III Methodology
(a) Introduction of Hydrofrecking
(b) Principal of Hydrofrecking
(c) Procedure and field operations
(d) Slug test
(e) Yield test (Before and After Hydrofrecking)
(f) Hydrofrecking work
(g) Factors controlling failure / success of Hydrofrecking
(h) Results
(i) Chemical analysis
(j) Tecno-Economic Evalution of Hydrofracking
(k) Recommendation and Conclusions
Part – IV
Annexure:-
1. Tables 3 To 46
2. Slug test datas and curve
3. Yield test datas
4. VES analyzed before and after
5. Chemical Analysis Sheet
6. Photos & Maps
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Table No. 1 – Hydrofracking project work at a Glance:-
Sr.
No.
Description of Items Details
1 Work started on 11 Dec.2012
2 Date of completion 29 Dec. 2012
3 Study area Rohini water shad in parts of blocks
Palera, Baldev Garh and
Tickmagarh District Tickmagarh
(M.P.) covering area 1144 sq. Km.
4 Implementing agency State ground water survey water
resources department M.P.`
5 Project Coordinator Mr. S.K. Khare (Chief Engineer)
Bodhi, Bhopal
6 Nodal Officer Mr. C.S. Ramteke (Superintending
Geohydrologist ) Bhopal
7 Principal investigator Mr. R.K. Sahu (SGH) Sagar
8 Field Officer Mr. S.C. Khare (AGH)
Mr. S.K. Namdeo (GA)
9 Consultant and Guide Mr. R.N. Sharma, Retd. Director
(CGWB)
10 Contractor of Hydrofrecking Project Mr. O.P. Dashora, Drilling company
with Hdyrofrecking Unit
11 Geological formation Bundelkhand Granite
12 Location with coordinates Longitude78º 58’20”-79º17’00”
Latitude 24º34’00”-25º00’25”
13 Toposheet 54-O/8,O/9
54-P/1,P/2,P/5,P/6,P/7,P/8,& P/14
14 Experimental old defunct tube well 15 Nos in different village of project
area
1. Padua, 2. Murrababa, 3.Pureniya,
4. Ramnagar Bujurg, 5. Dhanera, 6.
Deri, 7. Kudila,
8.Malguan, 9. Lar Banjariya, 10.
Parakhas (Darguan), 11. Antoura,
12. Mokhara, 13. Kharila,
14. Hattak, 15. Lamera
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EXEXUTIVE SUMMARY:-
Govt. of M.P. with the financial support from the
World Bank under Hydrological project embarked
upon Purpose Driven Studies for the study of Aquifer
Modification Technique Hydrofracking in the existing
Ground Water abstraction structures constructed on
Granitic Hydrogeological units of Dhassan basin. This PDS
work have been completed covering 1144 Sq. Km. area of
Rohini water shed of Dhassan basin in Tikamgarh District
within one month . The main Hydrogeological unit being
Granite spread over the entire water shed area covering
block area of Tikamarh Baldevgarh and Palera in part.
The field study started under the guidance of Shri. C.S.
Ramteke Superintending Geohydrologist and supervision of
Shri. R.K. Sahu SGH Sagar . The experimental study of
hydrofracking commence from date 13.12.2012. Contractor
Shri O.P. Dashora with his rig. Machine and crew reached
the site on date 13.12.2012 at Padua. Fifteen numbers
village have been covered under this PDS which ended in the
last village Lamera on date 29.12.2012. The actual field
operations the techniques of operations were guided and
supervised by the consultant Shri. R.N. Sharma Retd.
Director from Central Ground Water Board. Before and after
the hydrofrecking process in a tube well the data collected
were systematically and scientifically analyzed interpreted
and results were collected under the guidance of the
consultant.
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ACKNOWLADGEMENT
We the project officers are highly greatful to Shri S.K.
Khare Chief Enginear (Bodhi) for giving opportunity to
handle the Purpose Driven Study of Aqifer modification by
the uses of Hydrofracking Technique.
We are also deeply obliged to shri C.S. Ramtake
(Superintending Geohydrologist) for deploying us to
compleate field experiment. We are also extremely grateful
to Shri Ramtake for taking great interest in the field study,
data collection interest in the field study by actually coming
to field to encourage us. He evinced in the scrutinising the
project report. We are thankful to shri Ajay Sharma (S.G.H.)
and P.S. Thakur (A.G.H.) Bhopal for initiate Hydrofracking
Project Work & Site Selection.
We are equally thankful to the shri Gaurav Sahu
(Chemist) and whole staff for their coopration in giving the
analysis of water sample timely. we are thankful to our
driver Sadik Ali, Who took pains in moving the vehicles
even in the odd hour of the nights and timely completion of
the project which otherwise could not have been possible
without his cooperation.
Last but not the least we would like to thank shri H.S.
Sengar ,Senior Joint Commissioner Ministry of Water
Resources and shri Steve Parson,Technical Advisor of
Hydrological Project World Bank and his team for giving us
opportunity to present our study before them. We would fail
in our moral duty if we do not acknowledge the great and
gracious advices & vital supervision for the consultant Shri
R. N. Sharma.
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Location and Approachability:-
Location of PDS working area is in Rohni water shed of
Dhasan River Basin in Distt. Tikamgarh of M.P.
Geographycally the area located in Toposheet number 54 O
and 54 P Extension of area is approximatly 1144sq.km
Dhasan River is perennial river being effluent in nature, It
receives Base flow of ground water round the year. The
study area is approachable by all means of transport. By air
the landing station will be khajuraho from where the study
area is approachably by road roughly 90 Kilo meter. The
railway head is at Jhansi from where the area of study is 60
KM. and approachable by road.
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PART – II
PRE INVESTIGATION
ACTIVITIES
Introduction:-
In Madhya Pradesh Dhasan basin is comprises by
different rock formations like Granite ,Granite - gneisses
and Deccan Trap Basalt. The study area falls in survey of
India toposheets 54-0/8, 0/9, 54P/1,2,5,6,7,8&14, and
occupies approximate area of 1144 sq.km. in between
longitude: 78º.58’.20”-79º.17’00” lattitude 24º.34’.00”-
25º.00’25”.
The study area has a Granitic terrain and
topographically it is categorised as pediplain, Flood plains
and Residual hills. The basin is characterized by gentle to
moderate slope with dendritic drainage pattern. Dhasan
river with it various tributaries is flowing South to North
direction.
The Granite rock of Bundelkhand region is traversed
by numerous quartz reef, dolerite and dykes. The
Bundelkhand country rock is structurally disturbed and
large numbers of significant lineaments are present which
are carriers of water. The large numbers of dug wells
supported by perenial tanks of Bundelas & Parmar kings are
only the water sources of this sandy Granitic soil region.
The existing ground water conditions is poor to
moderate and potential is not sufficient to fulfill water
requirement of the area.
GEOMORPHOLOGY:-
The land scape of area is granite area pediplane and
structural hill in Tikmaragh District. The present
topography is mainly the product of differential erosion of
the rock. As a whole it is characterized by gentle to moderate
slope with dendritic drainage by pattern. Dhassan and other
tributaries are flowing South to North Direction.
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The area comprises three units (a) river alluvium as
narrow strips running parallel to river. (b) The midland area
comprises weathered granite overlying fresh granite and
traversed by quartz veins , quartzite and dolerite dykes. (c)
Upland area comprising thin weathered granite overlying
fresh granite rock.
Drainage:
The drainage pattern in the study area is dendritic and
sub- dendritic and sub-rectangular drainage is common in
the plateau and hill range.
Soil:-
Soil is the most important feature of physiography, the
formation of which largely depends upon the topography,
rock type and drainage. The soils are derived from the
grainitic gneiss parent materials and have been classified as
granitic sandy soil.
Geological Setup:-
The project area falls in the peninsular India. Towards
North Site Bundelkhand granite and in southern side
Bijawars, Vindhayan sandstone, Deccan traps and Lametas
are exposed and few parts are covered by Alluvium in basin.
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Table:- 2
The stratigraphic succession of the area is as follows.
Pleistocene
to Recent
Alluvium Sand silt, Gravels clay
etc.
Cretaceous
to Eocene
Unconformity
Deccan trap
Basaltic flow
Upper
cretaceous
Unconformity
Lametas
Impure Limestone sand
stone and conglomerate
Pre-
Cambrain
Vindhyan
Group
Unconformity
Upper Lower
Bhander series Sand
stone
RewaSeries
Orthoquarzite
Kaimor Series Lime
stone
Semri Series Shale
flag stone
Bijawar Series etc.
Archaean Unconformity
Bundelkhand
Super group
Granite & Gneisses
Hydrogeological conditions:-
Hydrological condition of area has been assessed on the
basis of water bearing formation of the area and inventoried
ground water structures. Ground water in hard rock occurs
in joint, fractured planes and mostly in weathered zone
under water table condition. The ground water is controlled
by degree of weathering and interconnectivity of joint which
varies from place to place.
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Ground Water Table Contour Maps Of Pre And Post Monsoon
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Basic Problem:-
Most of existing dug wells invariably dry up during
summer season. Only during monsoon and post monsoon the
dug well sustain discharge for irrigation of small acreage.
The progressive farmers preferred towards construction of
bore wells .
The basic problem has been to rejuvenate the bored
well are even failed tube wells . Some of the well –to- do
farmers attempted bore blasting to enhance yield of the well
but spoiled the tube well due to lack of expertise .
Hydrofracking is not known to the farmers as a
technique of rejuvenating the sick tube wells and enhancing
the quantity of well –discharge.
Diagnosis:-
Most of bored/tube wells in the watershed area initially
sustained yield 2000 to 3000 Litters per hour . Gradually
over the time the discharge dwindled and presently the
range of yield is between 180 lph. to 1500 lph. The purpose of
utility of bored well for irrigation small acreage got defeated.
Inference:-
The productive aquifer in hard rock comprises
fractured Granite overlain by weathered granite . Either the
fractures get clogged by detrital Material there by decrease
in the rate of inflow of ground water, or the fracture pattern
and /or orientation of fractures have been unfavorable .
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OBJECTIVES:-
1. To assess the applicability of aquifer modification
technique through Hydrofracking in other areas with
similar hydro geological conditions.
2. To develop a methodology for achievment of the optimum
abstraction region for the study of project area.
3. The officers of the organizations should develop and gain
hand on knowledge of hydrofracking technique so as to
become departmental expert to take up studies in future.
4. “Seeing is believing” to believe that hydrofracking is the
most economical method of rejuvenating bore wells.
5. The aquifer modification experiment by using
hydrofracking technique need to be tasted in the field
condition.
6. To make the farmers (beneficiary) aware of this
technique, 15 nos. of bore wells in different village had
been subjected to this experiment.
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Part – III
Hydrofracking:
Introduction :
Actually fracturing is a water well development process
designed to increase the efficiency of water well in hard rock
areas. The primary focus of the fracturing is laid on the
enlargement of existing fractures and fissures in a bore well
and thus introducing new and enlarged net-work of fractures
that can enhance the existing well-discharge. Generally
information on specific section that should be subjected to
hydro fracturing is obtained from the well –drillers log or
what is known as strata log. However private drillers and
the owners of the bore-wells do not maintain systematic
well- drilling log. In absence of this information canvassing
of water well inventorying and geo-electrical resistivity
vertical sounding gives fairly reliable information about the
water bearing zones depth to water of saturated zone vis-a –
vis depth to water table in adjacent area. Depth to existing
water level in the bore-well is actually measured. The
discrete section of water - bearing zones or aquifers are
deciphered from the geo-electrical resistivity sounding. This
processing enables to decide whether single packer is to be
used in hydrofracturing or double packer system is required.
Applying pressure would influence the weakest
fracture or fractures of least resistance and the resultant
observation is made by pumping out the well water and
measuring its quantity to compare with the pump discharge
before starting the hydrofracking. Majority of the bore-well
in the area required double packer system in which the
packers are situated on a pipe called drill –string6-10m.
apart. Deflated packers on the drill string are lowered at
selected zone and then inflated and pressure is applied for
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certain duration (detailed procedure under hydrofracking
technique). When the hydrofracking is completed the
packers are deflated and moved elsewhere in the bore to
pressure another section for hydrofracking. Finally the
hydrofracking assembly is pulled out. The well is then
subjected to pumpage and discharge is measured in a 200
liters capacity drum over the time. The final discharge was
much higher than the initial discharge which helps to certify
the success of the experiment. The water-sample is then
collected for chemical analysis. Slug injection is repeated
after hydrofracking.
Principle of Hydrofracking:
The basic principle behind (HFT) Technique is
PASCAL’S Law which in short states that when
hydrofracturing pressure is applied in any closed system or
body , it acts uniformly in all the direction in equal
proportions. Thus in a bore well when the packer is set below
the water table and the injected high pressure water acts in
closed system Pascal Law starts working in all directions
with equal proportion. The injected water with pressure
follows the least resistance path and therefore the initiation
of fracture or opening of closed or clogged fractures takes
place in the fractured granite rock.
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Procedure And Field Operations:-
Hydro geological canvassing of open wells and bored wells
in the vicinity of the bore well to be experimented for
hydrofracking to decipher.
Approximate demarcation of weathered and fracture zone
with regard to its depth and thickness.
Depth to water level and its fluctuation range between
Pre-monsoon (May month)and Post monsoon (November)
We Conducted geo-electrical vertical sounding near the
experimental bore-well. Field–plotting of apparent
resistivity readings against AB/2 distance in double log
paper to decipher depth of saturated zone and thickness
of fractured zones (aquifer)and bed rock depth.
Slug Test:-
Ferris and knowles(1962) and cooper Brode hoeft and
Papadopulos(1967) describe slug test to estimate
hydraulic properties of aquifer like transmissibility and
storage coefficient or specific yield. The slug test are
useful when no facility exists for carrying out pump test.
These test provide preliminary information on the aquifer
characteristics.
We have taken the static water level(SWL) in the bored
well and record in data –sheet. Then slug of 15 liters of
water is injected in the well and record the decrease in
the head of water. The rate of dissipation of the water
head in relation to time is recorded till the original SWL
is reached.
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Yield Test Before Hydrofracking:-
After the slug test we run the pump for certain
duration till it sustains discharge and at every one minute
interval record the draw down and discharge measured in
a drum of 200liters capacity and recorded the time when
the drum if full to its capacity. This enabled the rate of
quantity of discharge per minute and Shut off the pump.
Hydrofracking Work:-
Allowed the machine operator of hydro-fracturing
equipment to lower the deflated packer-set at the pre
determined section of the bore-well.
The deflated packer is then inflated and the High
pressure water injection pump is allowed to run which
injects the water stored in the water tanker mounted on
the truck.
Water injection pump plays primary role in the
hydrofracking process that is intended to initiate
fractures overcoming the in situ stress of the rock
formation.
The Packer –assembly is set against the desired zone such
that the top packer is at least 5-7m below the casing pipe
and at least 10-12 m below ground surface so as to
prevent any possible break –out of water under pressure
and surface water entering the well.
Opening the booster pump and injection pump will
facilitate the injection of water through the drill-string on
which packers are placed at a rate of 100 to 200 liter per
minute for a duration of 10-30.minutes Measure water
intake during operation at different interval.
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The injected water flow inside the well enters the desired
fractured formation and since the fractured zone will
resist this injected flow obviously the pressure will go on
increasing continuously as can be read on gauge.
The maximum pressure is recorded by pressure gauge
fitted in the equipment. The maximum working pressure
of the equipment is 210kg/cm2.
The maximum pressure developed suddenly drop off to
minimum pressure which is again read and recorded.
The sudden drop in the pressure is an indication of the
success of hydrofracking experiment. It also indicates
increased “in – flow” of water in the well through
reconditioned fracture network in the well formation has
been initiated.
When the injection pressure is released then a strong
back flow of cloudy water in the well occurs which is
pumped out of the well.
When water is clean we have taken water sample for
chemical analysis and slug test and measured the
discharge of the well after Hydrofracking.
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FACTORS CONTROLLING FAILURE/SUCCESS OF
HYDROFRACKING:
It is a matter of great interest to know the
relationship of fractures to the yield of ground water.
Fractures are the only way ground water can be stored
in hard rocks like granite, granite-gneiss , other
metamorphic and hard sedimentary rocks like
Vindhyan sandstone. In volcanic rocks area like basalt
vesicles (Lava tubes), Solution openings and cavities in
Lime stone terrain are other storage areas apart from
fractures. The quantity of ground water yield through
various abstraction structures depends on-
Size and Location of fractures.
Inter connection of the fractures.
Number of fractures (density).
Fracture System orientation vis-a-vis
characteristics.
Source water need to be created which can
continuously reach the fracture system down below
the soil and weathered mantle.
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FACTORS CONTROLLING FAILURE/SUCCESS OF
HYDROFRACKING:
From the perusal of above figures, the most
favorable characteristics are opening size, density,
inter-connections, orientation and good soil cover over
the hard rocks fracture network at different depth.
The soil cover and weathered rock facilitate high
storage of source water for infiltration of water to the
underlying System of fractures.
The attitudes and intensities of fracture
determine whether the ground water in these fracture
occur under water table conditions. Strictly water table
conditions are to be expected when the fractures are
vertical or when the rocks is severely fractured in
several directions.
In view of lateral and vertical discontinuity in the
weathered and fractured zones as is the conditions
prevailing in the Dhasan Basin as a whole, virtually all
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the recharge to ground water System is of local origin
and not supplied by distant sources. Thus what little
infiltration in the upland is arrested by basal
impervious massive rock is allowed to move downward
laterally towards valley bottoms. Low laying areas thus
recovers recharge not only through direct rainfall
infiltration but also by lateral movement of ground
water from the upland areas surrounding the micro-
watershed of tube wells.
Since there always occurs reduction in the yield
of the well in fractured rock as the pumped water level
goes deeper, depletion in discharge depth wise with
certain rate of decline in water level has a significant
relevance in the context of assessment of groundwater
resources vis-a-vis need for construction of artificial
recharge structure in the vicinity of pumped well.
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RESULTS:-
Table No.:- 3
Discharge Result of 15 nos
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Table No. 4
Details of the tube well and Hydrofrecking and its
yield performance test:-
Sr.
No.
Name of
Village
Block Altitude
(in m.)
Depth
of Tube
well
Rate of discharge in LPM
Before
H.F.
After
H.F.
Success
result in
percentage
1 Padua Palera <200-250 61.50m. 40.00 47.06 85.00
2 Murrab
aba
Palera <200-250 60.00m. 28.57 33.33 85.71
3 Pureniy
a
Palera <200-250 60.00m. 40.00 44.44 90.00
4 Ramnag
ar
Baldeo
Garh
250-300 68.35m. 10.42 11.76 88.54
5 Dhaner
a
Baldeo
Garh
<200-250 72.00m. 06.73 10.00 67.31
6 Deri Baldeo
Garh
250-300 91.50m. 11.11 30.77 36.11
7 Kudila Baldeo
Garh
300-400 90.00m. 3.33 11.11 30.00
8 Malgua
n
Baldeo
Garh
250-300 34.10m. 10.53 11.76 89.47
9 Larbanj
ariya
Tickmaga
rh
300-400 60.00m. 12.90 16.39 78.71
10 Parakha
s
Tickmaga
rh
300-400 55.00m. 10.00 70.50 57.14
11 Antoura Tickmaga
rh
300-400 48.00m. 16.67 32.00 52.08
12 Mokhra Tickmaga
rh
300-400 45.00m. 19.23 36.36 52.88
13 Khareel
a
Baldeo
Garh
250-300 61.50m. 10.00 16.67 60.00
14 Hatta Baldeo
Garh
300-400 92.65m. 2.94 8.70 33.82
15 Lamera Baldeo
Garh
250-300 64.50m. 30.77 42.11 73.08
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Chemicals Analysis of water sample:-
Majority of water samples after chemical analysis show
the TDS range is 8.3 and over with high contamination of
sulphate ions, sodium ions alongwith calcium ions. The
percentage of sodium varies from 11 to 30 percentage.
Though the SAR value is not more than 2, which indicates
its suitability for irrigation purposes.
Most of the defunct tube well with less discharge were
not in use for long time, that is why Total Dissolved Solids
of ground water appears temporarily polluted but in due
course of time the chemical quality of ground water will
improve due to its development through running of Tube
Well.
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Tecno-economic Evalution of Hydrofracking:-
The old defunct tube well is rejuvenating by Hydrofracking
method Because this method is technically easy besides very
cheap in cost instead of bore blasting and inwell boring which
are not only costly but involve many problem at accessing. The
construction of new Tube well in place of old defunct tube well is
always hazardous more over spacing of Tube well which may
indanger the ground water resources.
The economics of the new Tube well construction at the
avg. depth 250 ft / 75 m. is as below :
(A) Resistivity survey work: 1845 AS/CSR- 2009
(B) Drilling charges (VES)
1. Over burden Avg.18m depth : 10476 ……do------
( with 200 mm dia)
2. Hard rock Avg. depth 57 m. 64182 -----..do------
(with 150 mmdai)
(C) (1) Casing pipe (PVC) 60 ft. 15000
AS/Market rate
(D) (1) Yield test (min. 6 hrs) charges 6000
(E) Total Rs. 97503=00
Tax. 5% 4875=00
102378=00
Say Rs. 1.02 Lac.
The economics of the Hydrofracking as per market rates is as below
(a) Cleaning of Tube well: 2500=00
(b) Yield test charges(before H.F.) : 6000=00
(min 6hrs)
(c) Hydrofracking charges: 18000=00
(b) Yield test charges(after H.F.):-
6000=00
(min. 6 hrs)
Total Rs. 32500=00
Tax charges 5% 1625=00
34125=00
Say Rs. 0.35 lac.
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Form the above comparative economics the cost of
Tube well subjected to Hydrofracking and rejuvenating
yield is almost one third (33%) of the construction of new
Tube well in place of old tube well.
But since the Technology of Hydrofracturing is not
well known to the farmers. They are left with no option
other than construction of New Tube wells or the simply bore
blasting or inclined boring in the defunct tube well for
rejuvenating discharge boring is also costly and uncertain of
the rejuvenating of the yield ,Their ( farmers) Experience
with regard to bore blasting and inclined boring in very bad.
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Recommendation and Conclusions :-
1. The success percentage of increased discharge result of
experimented tube well in Rohini water shad area is
categorized in to three groups – (As shown in T. no. 3 and 4)
(1) 70% and above (2) 50% but < 70 % (3) < 50 %
These results indicates the success of discharge
enhancement and its sustainability depends upon the
existence of water body, Its distance from the tube well to
receive water as recharge water.
The historical ground water level data from departmental
permanent observation wells (POWs) have been collected
and show in (T. no.5,6, and 7).
2. Based upon the results and observations made under this
experiment of hydrofracking, it is concluded that the VES
which gives feasible locations of fractured zone is not very
dependable. Therefore it has not been very adequate to
place the packer and the application of hydrofracking
pressure to the desired fractured zone remains insufficient
and inadequate. That is the reason why in some of the tube
well hydrofracking could not produce the desired discharge.
Therefore it is recommended by our consultant to procure
Bore Hole Logger , which can be used before taking hydro
fracturing to exactly decipher the depth and thickness of
fractured zone. So that proper packer can be placed.
After the hydrofracking the bore hole logger can be again
used to see the improvement in the aquifer modification
process around the fractured horizon.
Bore hole camera with the facility to project the image of
the fractured zone and its improvement on the surface and
the image can be transferred in to picture. Which can be
seen by everybody. It is therefore recommended for the
procurement of such camera by the Ground Water
Organization to enable it function as a lead agency to take
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up hydrofracking of defunct tube wells in any area within
the state.
Before starting hydrofracking it is very essential to bailout
the detrital deposit from the tube well and make it clean and
ready for putting hydrofracking process in to operation.
3. Cost comparison of Hydrofraking verses Construction of
new tube well by drilling. This has been papered in details
under the heading Techno-Economic evaluation of
Hydrofracking and drilling of new tube well.
4. We have firm belief that the organization can take up the
Hydrofrecking of the low yielding as wells as dry or defunct
tube wells in various Hydro-geological units like massive
granite, Basaltic terrain and other sedimentary terrain. In a
large extent of area by adopting following measures and
equipments, training of the officials & officers.
Measures:-
It is essential to put at least three field hydro
geologist to take up the Assignment.
1. First field officer- will be deployed for taking up geo
hydrological field canvassing in the surrounding area of
the targeted tube well within the vicinity of 10Km. He
would be preparing base map showing the recharge &
discharge area of the well, prepare the litho logs of
convaseed well, Ground water contour map with the help
of G.P.S. collection of water samples,.
2. The second field officers- will take the V.E.S. around the
tube well recharge area & discharge area with respect to
the tube well. He would also be trained in the operation of
bore hole logger so that he takes the bore hole logging of
the tube well before & after Hydrofrecking.
3. Third officer- will be over all in charge of the
Hydrofrecking unit and the process of hydrofrecking in its
commission and completion. He would also conduct the
yield draw down test with the help of pump if discharge is
Page 34
sufficient. Otherwise he would conduct slug injection test
for the stipulated time one hour or the time taken to
reach the original static water level before slug test. After
the completion of hydrofrecking the discharge draw down
test must be conducted and compared with the discharge
improvement in terms of percentage increment. Water
sample should be collected before and after hydrofrecking
to study the geochemical environment and pollution level
if any.
Equipments:-
1. At least three truck mounted hydrofrecking units had to
be arranged from the available components in
organization of available or procure the equipments.
2. Procurement of bore hole electrical logger with the
facilities of short normal, long normal and lateral
resistivity and self potential measurements for a depth of
300 ft.
3. New computer based resistivity survey equipment at least
two units with printer facility.
4. Bore hole camera – with T.V. should be procured to
take the inside image of and the picture of bore hole.
Training:-
Fifteen officers need for the training. These officers /
officials need to be recruited and put under training to take
up the field job of hydrofrecking in a large area. Where
hydrofrecking project can be taken up department should
organized two types of training – one at Bhopal Head
Quarter, where department officers as well as other officers
from other department like PHE, Agriculture Engineering
etc. or any department, NGO who wish to get trained in the
technology of hydrofrecking.
Second type of training will be village level at the
Panchayat where farmers will be invited to participate in
this awareness campaign of hydrofrecking. Its benefits,
Utility and other associated tips for ground
water irrigation will be imparted.
Page 36
TABLE -6 : WATER LEVEL OF 30 M. DEEP TUBE WELL IN
ROHNI WATERSHED AREA(bmp IN.METER)
S.NO. NAME OF VILLAGE NOV.2010 MAY.2011 NOV.2011
1 BADAGAON 7.10 DRY 6.10
2 UMRI 9.15 DRY 7.60
3 BHENSWARI 8.65 9.20 5.50
4 RAMPURA 5.25 5.60 3.15
5 KODERA 7.40 8.45 4.20
6 DIKOLI 7.20 9.15 5.35
7 HATTA 7.90 8.60 6.20
8 PATORI 8.90 DRY 8.65
9 IMALIYA 11.95 DRY 8.50
10 SURAJPURA 12.85 12.80 7.35
Page 37
TABLE -7 : WATER LEVEL OF EXPERIMENTED TUBE WELL IN ROHNI WATERSHED AREA( bmp IN.METER)
S.NO. NAME OF VILLAGE DEC.2012
BEFORE AFTER
1 PADUA 6.96 7.00
2 MURRABABA 2.76 3.77
3 PURAINIYA 2.86 2.53
4 RAMNAGAR 8.37 4.13
5 DHANERA 4.96 4.96
6 DERI 2.06 2.06
7 KUDILA 1.39 1.00
8 MALGUAN 4.80 4.79
9 HATTA 30.10 30.14
10 KHARILA 7.18 5.10
11 LAMERA 5.96 5.91
12 LAR BANJARIYA 11.17 11.40
13 PARAKHAS 8.09 8.09
14 MOKHRA 7.83 7.83
15 ANTOURA 7.97 7.97
FIELD DATA OF SLUG TEST IN TABULAR FORM T. NO 8
11 MALGAWAN 11.00 11.40 8.65
12 JANAKPUR 8.80 10.00 6.40
13 BHANPURA 9.65 DRY 7.55
14 BHADARRA 9.10 9.55 8.00
15 BANNEBUJURG 7.25 DRY 6.40
16 KAROLLA 9.00 9.45 7.25
Page 38
S. No
.
Name of village
Time Depth to w.
l.(m.)
Residual Head
"H"(m.)
Elapsed Time "t"(in sec.)
H/Hs
Reciprocal of time
(1/t) H min. sec.
1 Malguan 10 24 0.0 4.79 1.223 slug of 15
litres injected
before h.f. 10 25 0.0 3.86 0.930 60 0.760 0.017
10 26 0.0 4.1 0.690 120 0.564 0.008
10 27 0.0 4.29 0.500 180 0.409 0.006
10 28 0.0 4.45 0.340 240 0.278 0.004
10 29 0.0 4.57 0.220 300 0.180 0.003
10 30 0.0 4.65 0.140 360 0.114 0.003
10 31 0.0 4.684 0.106 420 0.087 0.002
10 32 0.0 4.718 0.072 480 0.059 0.002
10 33 0.0 4.736 0.054 540 0.044 0.002
10 34 0.0 4.758 0.032 600 0.026 0.002
10 35 0.0 4.766 0.024 660 0.020 0.002
10 36 0.0 4.772 0.018 720 0.015 0.001
10 37 0.0 4.778 0.012 780 0.010 0.001
10 38 0.0 4.78 0.010 840 0.008 0.001
10 39 0.0 4.782 0.008 900 0.007 0.001
10 40 0.0 4.784 0.006 960 0.005 0.001
10 41 0.0 4.788 0.002 1020 0.002 0.001
formula
:
Hs= V÷Pie*(r*r)
Hs=Residual Head with injection of slug
V=volume of water(15lit) Or 0.015m3
Pie=22/7 or (3.14)
r= inner radious of well (dia. 5") or 0.0625m.1.223Hs=0.015/3.14(0.0625*0.0625)=
Page 39
FIELD DATA OF SLUG TEST IN TABULAR FORM T. 9
S. Name of Time Depth Residual Elapsed Time H/Hs Reciproca
Page 40
No. village H
min.
sec.
to w. l.(m.)
Head "H"(m.)
"t"(in sec.) l of time (1/t)
Malguan 17 10 0 4.8 1.223 slug of 15 ltr
injected
After HF 17 11 0 3.71 1.09 60 0.891 0.017
17 12 0 3.89 0.91 120 0.744 0.008
17 13 0 4.116 0.684 180 0.559 0.006
17 14 0 4.29 0.51 240 0.417 0.004
17 15 0 4.42 0.38 300 0.311 0.003
17 16 0 4.53 0.27 360 0.221 0.003
17 17 0 4.6 0.2 420 0.164 0.002
17 18 0 4.66 0.14 480 0.114 0.002
17 19 0 4.702 0.098 540 0.080 0.002
17 20 0 4.738 0.062 600 0.051 0.002
17 21 0 4.76 0.04 660 0.033 0.002
17 22 0 4.78 0.02 720 0.016 0.001
17 23 0 4.794 0.006 780 0.005 0.001
formula:
Hs= V÷Pie*(r*r)
Hs=Residual Head with injection of slug
V=volume of water(15lit) Or 0.015m3
Pie=22/7 or (3.14)
r= inner radious of well (dia. 5") or 0.0625m.
Hs=0.015/3.14(0.0625*0.0625)= 1.223
Page 44
FIELD DATA OF SLUG TEST IN TABULAR FORM T. NO 10
H min.sec.
1 8 15 0 5.96 0.850
8 16 0 5.4 0.560 60 0.659 0.017
8 17 0 5.62 0.340 120 0.400 0.008
8 18 0 5.73 0.230 180 0.271 0.006
8 19 0 5.84 0.120 240 0.141 0.004
8 20 0 5.894 0.066 300 0.078 0.003
8 21 0 5.924 0.036 360 0.042 0.003
8 22 0 5.932 0.028 420 0.033 0.002
8 23 0 5.94 0.020 480 0.024 0.002
8 24 0 5.942 0.018 540 0.021 0.002
8 25 0 5.946 0.014 600 0.016 0.002
8 26 0 5.948 0.012 660 0.014 0.002
8 27 0 5.952 0.008 720 0.009 0.001
8 28 0 5.96 0.000 780 0.000 0.001
Formula:
Hs= V÷Pie*(r*r)
Hs=Residual Head with injection of slug
V=volume of water(15lit) Or 0.015m3
Pie=22/7 or (3.14)
r= inner radious of well (dia. 6") or 0.075m.
H/Hs
LAMERA
before h.f.
TimeS. No. Name of village
Depth
to w.
l.(m.)
Residual
Head
"H"(m.)
Elapsed
Time
"t"(in sec.)
slug of 15 litres injected
reciprocal
of time
(1/t) in
sec.
H = 0.85
Page 45
H min.sec.
15 45 0 5.91 0.85 slug of 15 litres injected
15 46 0 5.45 0.46 60 0.541 0.017
15 47 0 5.64 0.27 120 0.318 0.008
15 48 0 5.85 0.06 180 0.071 0.006
15 49 0 5.86 0.05 240 0.059 0.004
15 50 0 5.888 0.022 300 0.026 0.003
15 51 0 5.892 0.018 360 0.021 0.003
15 52 0 5.896 0.014 420 0.016 0.002
15 53 0 5.9 0.01 480 0.012 0.002
15 54 0 5.902 0.008 540 0.009 0.002
15 55 0 5.904 0.006 600 0.007 0.002
15 56 0 5.906 0.004 660 0.005 0.002
15 57 0 5.908 0.002 720 0.002 0.001
Formula :
Hs= V÷Pie*(r*r)
Hs=
V=volume of water(15lit) Or 0.015m3
Hs =
reciprocal
of time
(1/t) in
S. No. Name of village
Depth
to w.
l.(m.)
Residual
Head
"H"(m.)
Elapsed
Time
"t"(in sec.)
H/Hs
FIELD DATA OF SLUG TEST IN TABULAR FORM T. NO. 11
0.85
Time
Residual head
Pie=22/7 or (3.14)
r = inner radious of well (dia. 6") or 0.075m.
After HF
LAMERA
Page 49
H min. sec.
1 8 52 0.0 11.17 1.223
8 53 0.0 10.31 0.860 60 0.703 0.017
8 54 0.0 10.412 0.758 120 0.620 0.008
8 55 0.0 10.75 0.420 180 0.343 0.006
8 56 0.0 10.97 0.200 240 0.164 0.004
8 57 0.0 11.076 0.094 300 0.077 0.003
8 58 0.0 11.132 0.038 360 0.031 0.003
8 59 0.0 11.148 0.022 420 0.018 0.002
9 0 0.0 11.158 0.012 480 0.010 0.002
9 1 0.0 11.162 0.008 540 0.007 0.002
9 2 0.0 11.166 0.004 600 0.003 0.002
9 3 0.0 11.168 0.002 660 0.002 0.002
9 4 0.0 11.168 0.002 720 0.002 0.001
9 5 0.0 11.17 0.000 780 0.000 0.001
formula:
Hs= V÷Pie*(r*r)
Hs=Residual Head with injection of slug
V=volume of water(15lit) Or 0.015m3
Pie=22/7 or (3.14)
r= inner radious of well (dia. 5") or 0.0625m.
Hs=1.22
Elapsed
Time Name of village
Time Depth to
w. l.(m.)S. No.
slug of 15 litres injected
H/Hs
LAR BANJARIYA
before h.f.
Residual
Head
FIELD DATA OF SLUG TEST IN TABULAR FORM T. NO. 12
Reciprocal
of time
Page 51
H min. sec.
16 40 0 11.17 1.223
16 41 0 10.57 0.6 60 0.491 0.017
16 42 0 10.63 0.54 120 0.442 0.008
16 43 0 10.69 0.48 180 0.392 0.006
16 44 0 10.758 0.412 240 0.337 0.004
16 45 0 10.8 0.37 300 0.303 0.003
16 46 0 10.84 0.33 360 0.270 0.003
16 47 0 10.88 0.29 420 0.237 0.002
16 48 0 10.91 0.26 480 0.213 0.002
16 49 0 10.932 0.238 540 0.195 0.002
16 50 0 10.958 0.212 600 0.173 0.002
16 51 0 10.98 0.19 660 0.155 0.002
16 52 0 11.01 0.16 720 0.131 0.001
16 53 0 11.024 0.146 780 0.119 0.001
16 54 0 11.036 0.134 840 0.110 0.001
16 55 0 11.042 0.128 900 0.105 0.001
16 56 0 11.054 0.116 960 0.095 0.001
16 57 0 11.058 0.112 1020 0.092 0.001
16 58 0 11.064 0.106 1080 0.087 0.001
16 59 0 11.068 0.102 1140 0.083 0.001
17 0 0 11.072 0.098 1200 0.080 0.001
17 1 0 11.076 0.094 1260 0.077 0.001
17 2 0 11.078 0.092 1320 0.075 0.001
17 3 0 11.084 0.086 1380 0.070 0.001
17 4 0 11.088 0.082 1440 0.067 0.001
17 5 0 11.088 0.082 1500 0.067 0.001
17 6 0 11.09 0.08 1560 0.065 0.001
17 7 0 11.094 0.076 1620 0.062 0.001
17 8 0 11.096 0.074 1680 0.061 0.001
17 9 0 11.098 0.072 1740 0.059 0.001
17 10 0 11.098 0.072 1800 0.059 0.001
formula:
Hs= V÷Pie*(r*r)
Hs=Residual Head with injection of slug
V=volume of water(15lit) Or 0.015m3
Pie=22/7 or (3.14)
r= inner radious of well (dia. 5") or 0.0625m.
Hs=1.22
AFTER HF
FIELD DATA OF SLUG TEST IN TABULAR FORM T. NO. 13
slug of 15 litres injectedLAR BANJARIYA
Reciprocal
of time S. No. Name of village
Time Depth to
w. l.(m.)
Residual
Head
Elapsed
Time H/Hs
Page 53
BEFORE START OF TEST SWL : 6.96 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 14
NAME OF VILLAGE
YIELD TEST BEFORE HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
PADUWA 1 09.13.00 9.17.00 00.04.00 50.00
2 9.17.45 9.21.45 00.04.00 50.00
3 9.23.00 9.27.15 00.04.15 47.06
4 9.28.00 9.32.18 00.04.18 46.51
5 9.33.00 9.37.20 00.04.20 46.15
6 9.38.00 9.42.22 00.04.22 45.80
7 09.43.00 09.47.25 00.04.25 45.28
8 09.48.00 09.52.30 00.04.30 44.44
9 09.54.00 09.58.35 00.04.35 43.64
10 09.59.00 10.03.38 00.04.38 43.17
11 10.05.00 10.09.40 00.04.40 42.86
12 10.10.30 10.15.30 00.05.00 40.00
13 10.17.00 10.22.00 00.05.00 40.00
14 10.23.00 10.28.00 00.05.00 40.00
15 10.29.00 10.34.01 00.05.00 40.00
Page 54
AFTER START OF TEST SWL : 7.00 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 15
NAME OF VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION
RATE OF DISCHARGE
( IN LPM)
1 15.55.00 15.58.15 00.03.15 61.54
PADUWA 2 15.59.00 16.03.15 00.04.15 47.06
3 16.04.00 16.08.15 00.04.15 47.06
4 16.08.45 16.13.00 00.04.15 47.06
5 16.14.00 16.18.15 00.04.15 47.06
6 16.18.45 16.23.00 00.04.15 47.06
7 16.23.45 16.28.00 00.04.15 47.06
8 16.28.45 16.33.00 00.04.15 47.06
9 16.34.00 16.38.15 00.04.15 47.06
10 16.39.00 16.43.15 00.04.15 47.06
11 17.00.00 17.04.15 00.04.15 47.06
12 17.35.00 17.39.15 00.04.15 47.06
13 18.05.00 18.09.25 00.04.25 47.06
Page 55
BEFORE START OF TEST SWL : 2.76m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 16
NAME OF VILLAGE YIELD TEST BEFORE HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 10.45.00 10.49.00 0.04.00 50.00
MURRAHBABA 2 10.49.30 10.54.00 0.04.30 44.44
3 10.54.45 10.59.30 0.04.45 42.11
4 11.00.15 11.05.00 0.04.45 42.11
5 11.05.45 11.10.50 0.05.05 39.34
6 11.13.00 11.18.30 0.05.30 36.36
7 11.19.30 11.25.30 0.06.00 33.33
8 11.26.30 11.32.45 0.06.15 32.00
9 11.33.30 11.40.00 0.06.30 30.77
10 11.40.30 11.47.30 00.07.00 28.57
11 11.48.00 11.55.00 0.07.00 28.57
Page 56
AFTER START OF TEST SWL : 3.77 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 17
NAME OF VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 15.50.00 15.54.30 00.04.30 46.51
MURRAHBABA 2 15.55.30 16.00.00 00.04.30 46.51
3 16.01.00 16.05.50 00.04.50 44.44
4 16.06.30 16.11.30 00.05.00 40.00
5 16.12.00 16.17.00 00.05.00 40.00
6 16.18.30 16.23.35 00.05.05 39.60
7 16.39.00 16.44.30 00.05.30 37.74
8 17.00.00 17.05.50 00.05.50 36.36
9 17.35.00 17.41.00 00.06.00 33.33
10 18.10.00 18.16.00 00.06.00 33.33
Page 57
BEFORE START OF TEST SWL : 2.86 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 18
NAME OF VILLAGE YIELD TEST BEFORE HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 11.20.00 11.24.25 00.04.25 45.28
PURAINIYA 2 11.25.00 11.29.25 00.04.25 45.28
3 11.29.45 11.34.10 00.04.25 45.28
4 11.34.55 11.39.20 00.04.25 45.28
5 11.40.00 11.44.40 00.04.40 42.86
6 11.45.15 11.50.00 00.04.45 42.11
7 11.50.30 11.55.20 00.04.50 41.38
8 11.56.00 12.00.55 00.04.55 40.68
9 12.01.30 12.06.28 00.04.58 40.27
10 12.07.00 12.11.59 00.04.59 40.13
11 12.12.30 12.17.30 00.05.00 40.00
12 12.18.00 12.23.00 00.05.00 40.00
13 12.24.00 12.29.00 00.05.00 40.00
14 12.30.00 12.35.00 00.05.00 40.00
15 12.35.30 12.40.30 00.05.00 40.00
16 12.41.30 12.46.30 00.05.00 40.00
Page 58
AFTER START OF TEST SWL : 2.53 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO 19
NAME OF VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 14.35.00 14.38.00 00.03.00 66.67 PURAINIYA 2 14.39.00 14.43.30 00.04.30 44.44 3 14.45.00 14.49.30 00.04.30 44.44 4 14.50.00 14.54.30 00.04.30 44.44 5 14.55.00 14.59.30 00.04.30 44.44 6 15.15.00 15.19.30 00.04.30 44.44 7 15.30.00 15.34.30 00.04.30 44.44 8 15.45.00 15.49.30 00.04.30 44.44 9 16.00.00 16.04.30 00.04.30 44.44 10 16.15.00 16.19.30 00.04.30 44.44 11 16.30.00 16.34.30 00.04.30 44.44 12 16.45.00 16.49.30 00.04.30 44.44
13 17.00.00 17.04.30 00.04.30 44.44 14 17.15.00 17.19.30 00.04.30 44.44 15 17.30.00 17.34.30 00.04.30 44.44
Page 59
BEFORE START OF TEST SWL : 8.37 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 20
NAME OF VILLAGE YIELD TEST BEFORE HYDRO FRACTURING
S.NO. START TIME
END TIME DURATION RATE OF
DISCHARGE ( IN LPM)
1 11.25.00 11.36.30 00.11.30 17.39
RAMNAGAR 2 11.37.15 11.42.44 00.05.29 10.03
3 12.15.30 12.31.45 00.16.15 12.31
4 12.32.15 12.35.05 00.02.50 9.18
5 13.05.00 13.17.00 00.12.00 10.43
Page 60
AFTER START OF TEST SWL : 4.13 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 21
NAME OF
VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 16.05.00 16.17.15 00.12.15 16.33 RAMNAGAR 2 16.17.45 16.31.15 00.13.30 14.81 3 16.32.00 16.47.35 00.15.35 12.83 4 16.48.15 17.04.15 00.16.00 12.50 5 17.05.00 17.22.00 00.17.00 11.77 6 18.21.40 18.37.25 00.15.45 12.70 7 18.38.00 18.48.37 00.10.37 11.77
Page 61
BEFORE START OF TEST SWL : 7.00 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 22
YIELD TEST AFTER HYDRO FRACTURING
NAME OF VILLAGE
S.NO. START TIME
END TIME
DURATION RATE OF DISCHARGE ( IN LPM)
1 15.55.00 15.58.15 00.03.15 61.54
PADUWA 2 15.59.00 16.03.15 00.04.15 61.54
3 16.04.00 16.08.15 00.04.15 61.54
4 16.08.45 16.13.00 00.04.15 61.54
5 16.14.00 16.18.15 00.04.15 61.54
6 16.18.45 16.23.00 00.04.15 47.06
7 16.23.45 16.28.00 00.04.15 47.06
8 16.28.45 16.33.00 00.04.15 47.06
9 16.34.00 16.38.15 00.04.15 47.06
10 16.39.00 16.43.15 00.04.15 47.06
11 17.00.00 17.04.15 00.04.15 47.06
12 17.35.00 17.39.15 00.04.15 47.06
13 18.05.00 18.09.25 00.04.25 47.06
Page 62
AFTER START OF TEST SWL : 4.96m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO 23
NAME OF VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 16.30.00 16.36.25 00.06.25 31.17 DHANERA 2 16.37.00 16.45.10 00.08.10 24.49 3 16.46.00 16.58.45 00.12.45 15.69 4 16.59.30 17.16.30 00.16.00 12.50 5 17.17.15 17.36.42 00.19.27 9.77 6 18.10.00 18.19.10 00.09.10 21.82 7 18.20.00 18.40.00 00.20.00 10.00 8 18.41.00 19.01.00 00.20.00 10.00 9 20.00.00 20.19.05 00.19.05 10.48 10 20.20.00 20.40.00 00.20.00 10.00
Page 63
BEFORE START OF TEST SWL : 2.06m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 24
NAME OF
VILLAGE YIELD TEST BEFORE HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 11.20.00 11.24.00 00.04.00 50.00 DERI 2 11.24.30 11.28.50 00.04.20 46.15 3 11.29.30 11.36.00 00.06.30 30.77 4 11.34.30 11.43.15 00.08.45 22.86 5 11.44.00 11.59.30 00.15.30 12.90 6 12.00.00 12.17.30 00.17.30 11.43 7 12.18.00 12.36.00 00.18.00 11.11 8 13.10.00 13.26.45 00.16.45 11.94 9 13.27.30 13.33.49 00.06.19 11.11
Page 64
AFTER START OF TEST SWL : 2.06 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 25
NAME OF VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 15.40.00 15.43.30 00.03.30 57.14 DERI 2 15.44.00 15.49.00 00.05.00 40.00 3 15.50.00 15.56.30 00.06.30 30.77 4 15.57.00 16.03.30 00.06.30 30.77 5 16.04.00 16.10.30 00.06.30 30.77 6 16.11.15 16.17.45 00.6.30 30.77 7 16.16.30 16.23.00 00.06.30 30.77 8 16.23.45 16.30.15 00.06.30 30.77 9 16.31.00 16.37.30 00.06.30 30.77 10 16.38.15 16.42.19 00.4.04 30.74 11 18.00.00 18.06.25 00.06.25 31.17 12 18.07.00 18.13.25 00.06.25 31.17 13 18.14.00 18.20.30 00.6.30 30.77 14 18.21.15 18.27.45 00.6.30 30.77 15 18.28.30 18.35.00 00.6.30 30.77 16 18.36.00 18.42.30 00.6.30 30.77 17 18.43.15 18.49.45 00.6.30 30.77
Page 65
AFTER START OF TEST SWL : 2.06 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 25
NAME OF VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 15.40.00 15.43.30 00.03.30 57.14 DERI 2 15.44.00 15.49.00 00.05.00 40.00 3 15.50.00 15.56.30 00.06.30 30.77 4 15.57.00 16.03.30 00.06.30 30.77 5 16.04.00 16.10.30 00.06.30 30.77 6 16.11.15 16.17.45 00.6.30 30.77 7 16.16.30 16.23.00 00.06.30 30.77 8 16.23.45 16.30.15 00.06.30 30.77 9 16.31.00 16.37.30 00.06.30 30.77 10 16.38.15 16.42.19 00.4.04 30.74 11 18.00.00 18.06.25 00.06.25 31.17 12 18.07.00 18.13.25 00.06.25 31.17 13 18.14.00 18.20.30 00.6.30 30.77 14 18.21.15 18.27.45 00.6.30 30.77 15 18.28.30 18.35.00 00.6.30 30.77 16 18.36.00 18.42.30 00.6.30 30.77 17 18.43.15 18.49.45 00.6.30 30.77
Page 66
AFTER START OF TEST SWL : 1.00 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 27
NAME OF
VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 16.25.00 16.29.00 00.04.00 50.00 KUDILA 2 16.29.30 16.34.00 00.04.30 44.44 3 16.34.30 16.42.15 00.07.45 25.81 4 16.43.00 16.51.30 00.08.30 23.53 5 16.52.00 17.03.15 00.11.15 17.78 6 17.04.00 17.18.15 00.14.15 14.04 7 17.19.00 17.33.30 00.14.30 13.79 8 17.34.00 17.51.00 00.17.00 11.76 9 17.53.00 18.11.30 00.18.30 10.81 10 18.13.00 18.31.00 00.18.00 11.11 11 18.33.00 18.51.00 00.18.00 11.11
Page 67
BEFORE START OF TEST SWL : 4.79 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 28
NAME OF
VILLAGE YIELD TEST BEFORE HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 11.45.00 11.51.30 00.06.30 30.77 MALGUWAN 2 11.52.30 12.03.30 00.11.00 18.18 3 12.04.00 12.18.30 00.14.30 13.79 4 12.20.00 12.35.45 00.15.45 12.70 5 12.36.30 12.53.00 00.16.30 12.12 6 12.53.30 13.12.30 00.19.00 10.53 7 13.13.45 13.25.45 00.11.55 10.24 8 14.30.00 14.44.30 00.14.30 13.79 9 14.45.00 15.03.00 00.18.00 11.11 10 15.03.30 15.22.30 00.19.00 10.53 11 15.23.30 15.26.21 00.02.51 10.53
Page 68
AFTER START OF TEST SWL : 4.80 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 29
NAME OF
VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 18.00.00 18.05.00 00.05.00 40.00 MALGUAN 2 18.05.25 18.13.00 00.07.35 26.37 3 18.13.30 18.24.30 00.11.00 18.18 4 18.25.15 18.38.45 00.13.30 14.81 5 18.40.15 18.55.00 00.14.45 13.56 6 18.55.50 19.11.00 00.15.10 13.19 7 19.11.25 19.27.00 00.15.35 12.83 8 19.27.30 19.43.45 00.16.15 12.31 9 19.45.00 20.01.45 00.16.45 11.94 10 20.02.30 20.19.00 00.17.00 11.76 11 20.19.30 20.36.30 00.17.00 11.76 12 20.37.00 20.54.00 00.17.00 11.76
Page 69
BEFORE START OF TEST SWL : 11.17 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 30
NAME OF VILLAGE YIELD TEST BEFORE HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 10.00.00 10.05.00 00.05.00 40.00 LAR BANJARIYA 2 10.05.30 10.10.30 00.05.00 40.00 3 10.11.15 10.16.40 00.05.25 36.92 4 10.17.10 10.24.30 00.07.20 27.27 5 10.25.20 10.33.20 00.08.00 25.00 6 10.33.50 10.42.20 00.09.30 21.05 7 10.43.00 11.04.00 00.11.00 18.18 8 11.04.45 11.15.15 00.11.30 17.39 9 11.16.00 11.31.20 00.15.20 13.04 10 11.32.00 11.47.45 00.15.45 12.70 11 11.48.30 12.04.00 00.15.30 12.90 12 12.05.00 12.20.30 00.15.30 12.90
Page 70
AFTER START OF TEST SWL : 11.40 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 31
NAME OF
VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 18.05.00 18.09.45 00.04.45 42.105263 LAR BANJARIYA 2 18.10.30 18.16.05 00.05.35 35.820896 3 18.17.00 18.23.45 00.06.45 29.62963 4 18.24.30 18.32.00 00.07.30 26.666667 5 18.33.00 18.41.10 00.08.10 24.489796 6 18.42.00 18.50.50 00.08.50 23.076923 7 18.52.00 19.01.40 00.09.40 20.689655 8 19.02.30 19.12.45 00.10.15 19.512195 9 19.13.30 19.34.47 00.11.17. 17.725258 10 19.35.30 19.47.25 00.11.55 16.783217 11 19.48.15 20.00.20 00.12.05 16.551724 12 20.01.00 20.13.12 00.12.12 16.393443 13 20.14.00 20.26.12 00.12.12 16.393443
Page 71
BEFORE START OF TEST SWL : 8.09m. BMP
MP : 0.60m.AGL( TOP OF CASING ) MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 32
NAME OF
VILLAGE YIELD TEST BEFORE HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 10.20.00 10.25.30 00.05.30 36.36 PARAKHAS 2 10.26.15 10.36.00 00.09.45 20.51 (Darguwan) 3 10.36.45 10.48.45 00.12.00 10.00
Page 72
AFTER START OF TEST SWL : 8.09 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 33
NAME OF VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 16.37.00 16.42.00 00.05.00 40.00 PARAKHAS 2 16.43.00 16.48.00 00.05.00 40.00 (DARGUAN) 3 16.49.00 16.54.30 00.5.30 36.36 4 16.55.15 17.03.15 00.08.00 25.00 5 17.04.00 17.12.30 00.08.30 23.53 6 17.13.15 17.24.35 00.11.20 17.65 7 17.25.15 17.34.04 00.08.49 17.58 8 18.30.00 18.39.30 00.09.30 21.05 9 18.40.30 18.51.10 00.10.40 18.75 10 18.59.00 19.09.00 00.10.00 17.50
Page 73
BEFORE START OF TEST SWL : 7.97 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 34
NAME OF
VILLAGE YIELD TEST BEFORE HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 09.15.00 09.20.00 00.05.00 40.00 ANTOURA 2 09.20.45 09.26.15 00.05.30 36.36 3 09.27.00 09.32.30 00.05.30 36.36 4 09.33.15 09.43.40 00.10.25 19.20 5 09.44.30 09.56.30 00.12.00 16.67 6 09.57.15 10.00.15 00.03.00 16.00 7 10.30.00 10.40.20 00.10.20 19.35 8 10.41.00 10.53.00 00.12.00 16.67 9 10.53.45 10.59.45 00.06.00 16.67
Page 74
AFTER START OF TEST SWL : 7.97m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 35
NAME OF
VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 15.30.00 15.34.45 00.04.45 42.11 ANTOURA 2 15.35.15 15.40.30 00.05.15 38.10 3 15.41.00 15.46.20 00.05.20 37.50 4 15.47.00 15.52.30 00.05.30 36.36 5 15.53.15 15.58.55 00.05.40 35.29 6 15.59.30 16.05.15 00.05.45 34.78 7 16.06.00 16.12.20 00.05.45 0.04 8 16.13.00 16.19.15 00.06.15 32.00 9 16.20.00 16.22.58 00.09.00 10.56 10 17.00.00 17.05.40 00.05.40 35.29 11 17.06.15 17.12.15 00.06.00 40.00 12 17.12.00 17.18.15 00.06.15 32.00
Page 75
BEFORE START OF TEST SWL : 7.83 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO.36
NAME OF VILLAGE YIELD TEST BEFORE HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 10.15.30 10.20.30 00.05.00 40.00
MOKHRA 2 10.21.00 10.26.00 00.05.00 40.00
3 10.27.00 10.32.30 00.05.30 36.36
4 10.33.15 10.41.10 00.07.55 15.48
5 10.41.50 10.48.20 00.06.30 19.23
6 11.20.00 11.27.01 00.07.01 19.24
Page 76
AFTER START OF TEST SWL : 7.83 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 37
NAME OF
VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 16.24.30 16.29.30 00.05.00 40.00 MOKHRA 2 16.31.00 16.36.00 00.05.00 40.00 3 16.37.00 16.42.00 00.05.00 40.00 4 16.43.00 16.48.00 00.05.00 40.00 5 17.03.00 17.08.30 00.05.30 36.36 6 17.18.00 17.22.00 00.04.00 36.25 7 17.30.40 17.36.00 00.05.20 37.50 8 17.36.45 17.42.15 00.05.30 36.36
Page 77
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 38
NAME OF VILLAGE
YIELD TEST BEFORE HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 11.50.40 11.56.40 00.06.00 33.33 KHARILA 2 11.58.00 12.04.50 00.06.50 29.27 3 12.05.30 12.13.00 00.07.30 26.67 4 12.12.40 12.21.30 00.08.50 22.64 5 12.23.00 12.32.20 00.09.20 21.43 6 12.33.00 12.43.40 00.10.40 18.75 7 12.44.30 12.55.00 00.11.00 18.18 8 12.56.00 13.08.25 00.12.25 16.11 9 13.09.00 13.23.28 00.14.28 13.82 10 13.24.00 13.40.50 00.16.50 11.88 11 13.41.30 13.59.30 00.18.00 11.11 12 13.42.15 14.00.50 00.18.35 10.76 13 14.01.00 14.20.00 00.19.00 10.53 14 14.20.45 14.40.45 00.20.00 10.00 15 14.41.30 15.01.30 00.20.00 10.00 16 15.02.30 15.22.30 00.20.00 10.00
Page 78
AFTER START OF TEST SWL : 5.10 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 39
NAME OF
VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 20.15.35 20.21.35 00.06.00 33.33 KHARILA 2 20.22.30 20.30.10 00.07.40 26.09 3 20.31.00 20.39.00 00.08.00 25.00 4 20.40.00 20.49.00 00.09.00 22.22 5 20.49.45 20.59.35 00.09.50 20.34 6 21.00.30 21.11.05 00.10.35 18.90 7 21.12.00 21.22.50 00.10.50 18.46 8 21.23.30 21.35.00 00.11.30 17.39 9 21.35.45 21.47.25 00.11.40 17.14 10 21.48.00 21.59.50 00.11.50 16.90 11 22.00.45 22.12.40 00.11.55 16.78 12 22.13.30 22.25.30 00.12.00 16.67 13 22.26.30 22.38.30 00.12.00 16.67
Page 79
BEFORE START OF TEST SWL : 30.10 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION T. NO. 40
NAME OF VILLAGE YIELD TEST BEFORE HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 10.15.35 10.21.35 00.06.00 33.33 HATTA 2 10.22.30 10.30.10 00.07.40 3.83 3 10.51.00 11.01.40 00.10.40 18.75 4 11.02.25 11.18.45 00.16.20 12.24 5 11.19.30 11.45.00 00.25.30 7.83 6 11.45.45 12.02.45 00.17.00 2.94 7 12.30.00 12.57.40 00.27.40 2.94
Page 80
AFTER START OF TEST SWL : 30.14 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 41
NAME OF
VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 18.28.30 18.33.30 00.05.00 40.00 HATTA 2 18.34.15 18.44.25 00.10.00 20.00 3 18.45.00 19.05.35 00.20.35 9.72 4 19.06.10 19.29.10 00.23.00 8.70 5 19.30.00 19.46.40 00.16.40 8.70 6 20.15.20 20.26.50 00.11.30 8.70
Page 81
BEFORE START OF TEST SWL : 5.96 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 42
NAME OF VILLAGE YIELD TEST BEFORE HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 09.30.00 09.34.00 00.04.00 50.00 LAMERA 2 09.35.00 09.41.00 00.06.00 40.00 3 09.41.45 09.48.15 00.06.30 30.77 4 09.49.10 09.55.40 00.06.30 30.77 5 09.56.00 10.02.30 00.06.30 30.77 6 10.03.15 10.09.45 00.06.30 30.77 7 10.15.30 10.22.00 00.06.30 30.77 8 10.37.00 10.43.30 00.06.30 30.77 9 10.48.30 10.55.00 00.06.30 30.77 10 11.10.00 11.17.30 00.06.30 30.77 11 11.32.00 11.38.30 00.06.30 30.77 12 12.00.00 12.06.30 00.06.30 30.77 13 12.26.00 12.32.30 00.06.30 30.77 14 12.52.00 12.58.30 00.06.30 30.77
Page 82
AFTER START OF TEST SWL : 5.91 m. BMP MP : 0.60m.AGL( TOP OF CASING )
MEASURMENT OF DISCHARGE (200 LITRES CAPACITY DRUM)
DISCHARGE =VOLUME / DURATION
T. NO. 43
NAME OF
VILLAGE YIELD TEST AFTER HYDRO FRACTURING
S.NO. START TIME
END TIME
DURATION RATE OF
DISCHARGE ( IN LPM)
1 16.45.00 16.50.00 00.04.00 50.00
LAMERA 2 16.51.00 16.56.00 00.04.30 44.44
3 16.56.45 17.01.30 00.04.45 42.10
4 17.02.15 17.06.00 00.04.45 42.10
5 17.06.30 17.11.15 00.04.45 42.10
6 17.12.00 17.16.45 00.04.45 42.10
7 17.17.30 17.22.15 00.04.45 42.10
8 17.23.00 17.28.00 00.04.45 42.10
9 17.30.00 17.34.45 00.04.45 42.10
10 17.35.15 17.40.00 00.04.45 42.10
11 17.41.00 17.45.45 00.04.45 42.10
12 17.46.15 17.51.00 00.04.45 42.10
13 17.52.00 17.56.45 00.04.45 42.10
14 17.57.30 18.02.15 00.04.45 42.10
15 18.03.00 18.07.45 00.04.45 42.10
16 18.08.15 18.13.00 00.04.46 41.96
17 18.14.00 18.18.45 00.04.47 41.81
18 18.19.15 18.24.00 00.04.48 41.67
19 18.39.00 18.43.45 00.04.49 41.52
20 18.58.00 19.02.45 00.04.50 41.38
21 19.17.00 19.21.45 00.04.51 41.24
22 19.37.00 19.41.45 00.04.52 41.10
23 19.57.00 20.01.45 00.04.53 40.96
24 20.17.00 20.21.45 00.04.54 40.82
Page 83
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238
95.2
18.5
194
3156
5.3
282.
60
118
288
AFTE
R8.
350
439
430
823
192
.418
.717
228
575.
127
0.8
011
1827
6
TABL
E N
O. 4
6 CH
EMIC
AL
AN
ALY
SIS
OF
GRO
UN
DW
ATE
R SA
MPL
ES O
F RO
HN
I WA
TERS
HED
DU
RIN
G H
YDRO
FRA
CTU
RIN
G IN
DIS
TRIC
T TI
KAM
GA
RH(M
.P.)
S.N
O.
NA
ME
OF
VIL
LAG
E
BEFO
RE/A
FTER
GEN
ERA
LH
ARD
NES
SM
AJO
R IO
NS(
MG
/L)
ALK
ALI
NIT
Y
1PA
DU
A
2M
URR
A BA
BA
3PU
RAIN
IYA
4RA
MN
AGAR
(BU
JURG
)
5D
HAN
ERA
6D
ERI
7KU
DIL
A
8M
ALG
UAN
9LA
R BA
NJA
RIYA
10PA
RAKH
AS
(DAR
GU
AN)
11AN
TOU
RA
12M
OKH
RA
13KH
ARIL
A
14H
ATTA
15LA
MER
A