Saturday, March 14, 2015

WATERSHED DEVELOPMENT AND OTHER METHODS IN TACKLING OVER DRAFT GROUNDWATER CONDITONS.

 NATIONAL SEMINAR ON PUMP SET ENENGISATION AND GROUND WATER RESOURCE MANAGEMENT, CIRE, HYDERABAD, P.117-123, FEB 1999.


C.SATYANARAYANA
ABSTRACT    
The enthusiasm shown towards exploitation of Groundwater through agricultural pump set energisation program lacking in simultaneous formulation of artificial groundwater recharge schemes and generation of additional power. This has led to steep decline of water table and power crisis in certain parts of the country. From groundwater point of view, water shed wise development projects in critical areas to reduce soil erosion, run-off and to increase groundwater recharge from annual rainfall are the suitable measures to tackle over-exploitation of groundwater.


INTRODUCTION
 The recurrence of droughts highlighted the importance of groundwater exploitation.
After 1970, large scale construction of irrigation wells started and with the introduction of SPA participative programs since 1978, the pace of ground water exploitation has increased manifold.  Desired results of increased food production and establishment of ancillary units in rural areas were achieved in a satisfactory manner.

The pump set energisation programme is so fast particularly in few states covered by hard rock terrain like Maharashtra, Andhra Pradesh, TamilNadu, parts of Karnataka, Gujarat and Madhya Pradesh that the ground water draft exceeded the safe yield resulting in decline of water levels.

The initiation and enthusiasm shown for exploitation of ground water through energisation of agricultural pump sets were missing towards the artificial recharge of groundwater projects and additional generation projects to meet the growing demand.  As a result, a number of white area blocks were transforming into grey blocks and grey into dark area from groundwater point of view and severe power crisis developed in many states.  However, still there is a lot of demand for agricultural connections in these areas.
 *Sr.Hydrogeologist, Rural Electrification Corporation Limited, Project Office, Chennai.


ONGOING STUDIES: 
As the Groundwater related Departments were also established after 1970, taluk wise and district wise groundwater assessment studies were carried out taking some of the norms on Adhoc basis.  After acquiring some field data and experience now modified norms are being adopted for assessment of groundwater particularly in areas where exploitation of groundwater exceeds safe Yields. The methods include 1) Watershed wise assessment of groundwater 2) Water level fluctuation and specific yield method.

WHAT IS WATERSHED.                           
Watershed is a drainage basin or catchment with natural stream outlet and is separated from another watershed by topographic ridge and slope.  The catchment of bigger river like Ganga, Godavari, Krishna are called basin, the catchment of tributaries of bigger rivers are called sub Basin and the catchment of smaller stream is watershed. The groundwater assessment is done taking watershed as a unit which covers catchment of a small stream, covering about 12 to 15 villages.  Even micro-watersheds comprising the area under the jurisdiction of one village is also suggested as this help in grouping the people in one co-operative society.  These schemes depend mainly on the co-operation of people as multiple activities are involved.(Basin and Water Shed map enclosed)

The advantages of watershed approach are:
  1). The entire rain fall experienced by a watershed could be accounted easily as the total Rainfall, evaporation, surface run-off and soil moisture are confined to the catchment of water shed only.
  2). There is a specific entry point and outlet and a spread area in the form of catchment is available in watershed.  Hence the budgeting of groundwater is possible with certain degree of accuracy than the assessment made on administrative boundaries like taluk/block.

IMPORTANCE OF WATERSHEDWISE DEVELOPMENT IN TACKLING OVER   EXPLOITATION OF GROUNDWATER.
There are three important components in the assessment of groundwater.
1). Recharge of groundwater basin.
2). Surface run-off.
3). Evaporation and Transpiration.           
 It is estimated that in our country, 47% of rainfall goes as surface run-off, 30 to 35% as evaporation and 15 to 25% to groundwater recharge. The groundwater recharge depends on the nature of soil, rock formation and topography etc., if any watershed becomes dark or grey category due to overexploitation, the alternate methods to increase groundwater recharge are - to reduce surface run-off and evaporation.

  The following watershed wise methods enable to increase the groundwater recharge from rainfall.
1.    Gully plugging in minor streams.
2.    Sub-surface dykes or percolation tanks along stream.
3.    Contour bunding.
4.    Trenching along hill slopes.
5.    Farm ponds in the foot hill zone.
6.    Check dam cum minor irrigation on the main stream.
7.    Land leveling (terracing)
8.    A forestation.

 The above methods check the erosion of soil, reduce surface run-off and increase groundwater recharge.

PRESENT STATUS OF WATERSHED PROJECTS:

The methods like bunding, land leveling, afforestation and other soil conservation measures were already taken up in most of the states.  Construction of percolation tanks and assessment of groundwater by watershed method was taken up by Maharashtra government from 1973 onwards.  About 7000 percolation tanks were constructed in Maharashtra state. Evaluation studies on selected percolation tanks in DPAP areas indicated that groundwater recharge has increased up to 50% of its gross storage.  Under normal conditions the groundwater recharge from rainfall is 10 to 15% in hard rocks. With other artificial recharge projects like trenching at nala bed, contour trenching, flooding nala has increased the recharge to Groundwater from 30 to 40% of gross storage of projects.          
1) Though large numbers of watershed development projects are now being taken up in several parts of the country, the results of these projects are not available to other agencies who are engaged in the same field.
2). The details of water level data, discharge of wells, run-off data, evapotranspiration data, soil/fertility cropping pattern before taking up watershed programme and collection of similar data after completion of project is necessary so that benefit due to watershed development programme could be quantified.
The publications of such results are very useful as it could act as a guide to other areas where similar programs are likely to be taken up.



OTHER METHODS TO TACKLE OVER-EXPLOITED AREAS
 As the watershed projects involves long gestation period and involve lot of financial commitment, it is very difficult to cover even small number of watersheds in the coming 5 to 10 year period. Hence the alternative methods are to be searched to tackle the over draft conditions. Some of the alternatives are given below;-

a)    Even in the dark category watersheds also, the groundwater conditions near the tanks, ponds, valley-fill areas, flood plains, natural levees, meandering courses of rivers, streams etc. palaeo channels, and foot -hill zones are some of the groundwater potential zones to be taken up for groundwater extraction.  These areas can be delineated utilizing aerial photos and satellite imageries.  Already several groundwater departments brought out district wise groundwater reports where the maps depicting the above aspects are demarcated.
b)    In hard rock terrain where deep water level conditions are existing and deep bore wells are the only groundwater abstraction structures, the ‘deep fractured aquifers should be utilized for meeting the drinking water needs only. Drilling of bore wells for irrigation purpose in such areas should be discouraged as the groundwater potential in deep fractured terrain is limited.
c)    Desilting of tanks and ponds should be carried out to increase the recharge of groundwater. During the dry seasons, farmers may be allowed to collect the silt/clay material accumulated at the bottom of the tanks. This will enable the farmers to put the silt in their agricultural fields to enhance the fertility of the soil. This program can enhance the recharge to groundwater from tanks and ponds. Desilting not only increase the discharge of wells but also reduce the total head of agricultural pump sets to Pump out water.  This in turn will cause lot of savings in consumption of power in agricultural pumping systems.  As the ultimate beneficiary for watershed development is power sector, SEB’s can associate with schemes formulated for watershed development in association with financial institutions, NABARD and minor irrigation departments.
d)    At present both state and Central Groundwater Departments are carrying out monitoring of National Network observation wells periodically. Under the programme, monitoring of water level fluctuation and changes in quality of groundwater were carried out. But it is also advisable to establish some piezometers in representative areas in grey and white blocks particularly in hard rock terrain and carry out step drawdown test to monitor:
·         Changes in efficiency of wells.
·         Changes in Discharge, water levels and Drawdown of wells etc.
The collection of above data enables us to watch the groundwater system and can take                                       preventive measures in case the aquifers are leading for overdraft conditions.
   e). Artificial recharge of groundwater by channel spreading, induced recharge and injection               some of the important methods to tackle over draft conditions.  Few artificial recharge projects were taken already by CGWB and state GWD’s. But the studies are in preliminary stage only and projects are to be taken up to cover major portion of over exploited area.


CONCLUSIONS  
  Large scale groundwater exploitation through pump set energisation has taken up mostly in the   States covered by hard rock terrain, like Maharashtra, Andhra Pradesh, Tamil Nadu, part of Gujarat, Madhya Pradesh and Karnataka etc., In some districts of these states, large scale exploitation of groundwater caused decline of water levels which involves lot of money in deepening of existing wells, construction of bore wells and requirement of additional power to meet the enhanced connected load which was caused due to increase in total head. The decline of water levels increased the total head and high density of irrigation wells reduces the discharge rate.  These factors added to the high consumption of power.  This has lot of impact on the existing power systems in the way of erecting additional distribution transformers, substations and generation of additional power.
For the above problems, watershed development projects to enhance the groundwater recharge are one of the important solutions besides artificial recharge of groundwater by several methods which are in vogue.   









           
















                                 

Thursday, January 8, 2015

UTILISATION OF AQUIFER CHARACTERISTICS FOR SELECTION OF AGRICULTURAL PUMP SETS IN ANDHRA PRADESH AND TELANGANA.

                                                         * C.SATYANARAYANA


INTRODUCTION
Selecting an agricultural pump set of appropriate size and installing energy efficient pumping system for these pump sets avoids wasteful consumption of power. Shortage of power can be mitigated to a great extent by adopting an efficient pumping system to the existing pump sets since increasing the generation capacity is both capital intensive and it requires a long gestation period. Electrical pump sets used by farmers in Andhra Pradesh and Telangana states are, in majority of the cases, inefficient and therefore result in considerable wastage of energy. Installation of new energy efficient pumping system will definitely save the valuable power to some extent but to save more energy, the pump specifications should match the well characteristics like discharge, total  head etc.  Aquifer characteristics like discharge, drawdown,  transmissivity,  specific capacity, specific yield or storage coefficient varies depending on the type of rock  formations, topographical conditions, recharge conditions, soil cover etc.  The study on Hydrogeological conditions of different rock formations existing in Andhra Pradesh and Telangana state enable us to understand the above mentioned characteristics which are useful for the selection of correct size of agricultural pump sets.                                           
EFFICIENT PUMPING SYSTEM
To overcome the problems of low efficiency and low power factor of pumping system, following measures are to be followed.
·         Efficient pumping system adopting BIS mark pumps, motors, piping system and foot valve etc
·         Correct estimation of Discharge (Q), Total Head (H) of groundwater abstraction structures (Bore well, Tube well, Dug well, etc.) so as to select correct size of pumping system.
Ø  Efficient Pumping system: - Regarding the installation of efficient pumping system, several field studies were carried out since last 20 years. The studies include

1.       Replacement of foot valve with frictionless foot valve
2.       Replacement of GI piping with PVC and HDPE pipes
3.       Replacement of Motors and Pumps with energy efficient Motor and Pump sets.
Of late, some state governments like Andhra Pradesh and Maharashtra are going for complete replacement of existing pumping system with new energy efficient pumping system. Energy efficient pumping system adopting the following BIS standards are to be installed.

*Groundwater specialist, retired from RURAL ELECTRIFICATION CORPORATION.

Equipment
Relevant Indian Standard
Centrifugal pump        
IS 6595
Mono set pumps         
IS 9079
Submersible pump set
IS 8034
Electric Motor            
IS 7538
Suction and Delivery or Piping system
IS 4984 and 4985
Pipe fittings PVC fittings                        
IS 10124

Ø  Correct estimation of Discharge (Q) and Total Head (H):-,
Though installation of new energy efficient pumping system will definitely save the valuable power to some extent but to save more energy, the Pump specifications should match the well characteristics like discharge and total head etc. Generally, the farmers select the agricultural pump sets as per the advice of pump dealer without considering the discharge, static water level, pumped water level etc. In order to maintain higher efficiency of pump set, well characteristics should be taken into account, mainly discharge and total head. If the discharge and total head are appreciably lower or higher than the pump specifications for which pump is selected, low efficiency and reduction in power factor results. Therefore, there is a need for optimum selection. Due to large seasonal variation in ground water level and discharge, pump sets operate under varying load conditions. Under loading of motor results in lower efficiency, Power factor reduction and ultimately higher power consumption. Due to power cuts, farmers try to get maximum water in less time by opting for higher ratings of motors.  In such cases, motors are operating between 50 and 75 per cent of rated load.  Higher rating of motors lead to  over  loading  of  distribution  transformers  and together with existing  higher HT and LT ratio, results in high line losses and  fluctuations in  voltage conditions.
Aquifer characteristics like discharge, drawdown, transmissivity, specific capacity, specific yield or storage coefficient vary with the type of rock formations, topographical conditions, recharge conditions, soil cover etc.  Weathered and fractured zones in hard rock’s under favorable soil, recharge and topographical conditions yield adequate ground water potential. Sandstones belongs to Gondwana and Tertiary formations yield large quantity of water and it is observed that though number of Tube wells increased many fold in these rock formations since last 30 years but there is no significant decrease in transmissivity of Sandstone aquifers unlike in Granitic Gneissic rock formations where discharge and transmissivity decreased considerably results in steep decline of water levels. Though large area in Godavari, Krishna and Penna River Delta area is underlain by alluvial formations, the wells are restricted to shallow depth only, due to quality problem in higher depth. But along stream courses and in canal command areas, the filter points yield adequate ground water without quality problem.
  

HYDROGEOLOGICAL CONDITIONS OF DIFFERENT ROCK FORMATIONS IN ANDHRA PRADESH AND TELANGANA

                               Image source: http://apsgwd.gov.in/ApgwdGroundwaterScenario.aspx
Geological formations for the purpose of ground water availability can be divided into 3 main categories.
1.       Hard rocks or consolidated rock formations
2.       Sedimentary or Semi-consolidated rock formations
3.       Unconsolidated formations.
In Andhra Pradesh the Hard rock, comprising of Granitic Gneisses, Schist, Khondalite, Charnockite, consolidated   Shale, Quartzite, Limestone, Dolomites etc., occupies about 82% of the total area. The Sedimentary or Semi-consolidated formations occupy 6% and unconsolidated (Alluvial) formations cover 12%.In the Geological history of the state, the Hard rock formations are the oldest rocks(3500
million years)and hardness of rock formations gradually decreases with age, leading to Schist, Quartzite, Lime stone, Dolomite, Sandstones, Shale etc and finally recent  alluvial formations. Similarly the water bearing zones also improve from old age to recent formations. But the quality of ground water is affected by other factors like chemical composition of rocks, sea water intrusion, water logging conditions etc.

        THE GEOLOGICAL SUCCESSION IS GIVEN BELOW
SL.NO
PERIOD
ROCK FORMATIONS
AGE Mil Years
1
Recent
Alluvium/Laterite
0-2
2
Tertiary
Rajahmundry Sand stone
25-2
3
Post Cretaceous
Deccan Traps
70
4
Permian-Early Cretaceous
Gondwana formations
270-85
5
Late Proterozoic
Kurnool formations
1100-600
6
Middle Proterozoic
Kadapa formations
1700-1100
7
Early Proterozoic
High grade
 Schist,Charnockite,Khondalite and low grade Schist
2350-3000
8
Late  Archaean
Granitic Gneisses
3000-
9
Early Archaean
Peninsula Gneiss
3750








 HARD ROCKS OR CONSOLIDATED ROCK FORMATIONS
 EASTERN DHARWAR CRATON (EDC)-(In the above map shown as Archaean formations).
The EDC is one of the six cratons which are part of Indian shield made up of Archaean rock formations comprising of Granitic Gneisses, Green schist, Fold belts, intrusive dykes, sills etc. The EDC is bound in the north by the Deccan Traps and Bastar craton, east by Eastern Ghat Mobile Belt , south by Southern Granulites, and west by Closepet Granite and Western Dharwar craton.  Between EDC and Eastern Ghat Mobile Belt, Kadapa type rock formations are occupied in the shear zone. The Eastern Dharwar craton occupied western portion of the state covering Telangana area except parts of Adilabad, Karimnagar, Khammam and Warangal districts.
There are two main rock types in EDC, which occupy major portion of the area
1.       Granitic Gneisses
2.       Green Schist
Granitic Gneisses occur as elongated plutonic belts running parallel to Schist belts. Origin and distribution of these rock formations have considerable impact on ground water potential of this region.

           Origin of Granitic Gneisses (Dharwar Craton)
The Dharwar Batholith is a term first used by Chadwick et al.(2000) to describe a series of parallel plutonic belts. Previous works consistently used the term ‘Peninsular Gneisses’ to describe the majority of the EDC;  however, it is compositionally different than the Western Dharwar  Craton gneisses, more granitic than gneissic and hence the new terminology is more appropriate(Ramakrishnan and Vaidyanathan,2008). There are numerous elongated Granitic Gneisses running parallel to the Schist belts of the EDC. The plutonic belts are approximately 15-25 km wide, hundreds of km long and separated by greenstone belts. They trend NW-SE except for in the south where the trends become North-South.
 These intruded Granites could have been originated from partial melting of the continental crust during subduction or during rise of mantle plume. The Dharwar batholiths then obliquely converged with the Western Dharwar Craton causing shear systems along the margins. 
           Origin of Green schist belts-In the above map shown as Dharwars.
The linear schist belts represent back-arc basin environment which were metamorphosed during accretion. Back arc basins are the submarine basins associated with island arcs and subduction zones. As per Plate tectonic theory, convergent plate margin is located at ocean trench where two plates converge and when denser of the two plates sink along an inclined plane below the other to be eventually absorbed into mantle. This process is called subduction.
Subduction of oceanic crust between two crystal blocks gives rise to back-arc basin, volcanic arc, fore arc basin and formation of ocean type crust. It is by subduction only that calc-alkaline volcanic and tonalite magma were generated. During Dharwar Orogeny the volcanics have been metamorphosed into Green schist, Amphibolites and higher grade basic Granulites while the associated sediments have recrystallised into Quartzites, Marbles etc.  Another theory suggests that Green schist belts developed as a result of intra-arc basins associated with batholiths. Important Greenstone belts and Super groups are given below:-
1.       Sandur schist belt,
2.       Ramagiri-Penakacherla-Sirigeri-Hungund super belt (RPSH),
3.       Kolar-Kadiri-Jonnagiri-Hutti super belt (KKJH), and
4.       Veligallu-Raichur-Gadwal super belt (VRG).
 Sandur schist belt is located north of closepet granite on the western side of EDC.  RPSH consists of two discontinuous schist belts. These belts are intruded by granites and gneisses.  It is located north of Ananthpur Town and in Kurnool district.  KKJH schist belt is located in the southern portion of EDC and below kadapa basin in southern side.  The Kolar region contains mostly amphibolite grade metamorphic rocks.  The VRG super group is located north of Kadapa basin. The super group consists of granites, metabasalts which are typically formed during the early stages of subduction. 
         Intrusives of EDC-
Majority of intrusives include mafic dykes, kimberllites, lamproites and have the trends of NW-SE,   E-W and NE-SW.
Five major intrusives are
1.       Hyderabad cluster
2.       Mahabubnagar
3.       Bangalore
4.       Anantpur
5.       Tirupati.

Ø  Hyderabad cluster is widely spaced NNE-SSW to N-S trending dykes transverse E-W oriented dykes. The majority of the dykes present are dolerites in composition.
Ø  Mahabunagar dyke intrude local granitic gneisses. The mafic dykes are predominantly gabbroic and partly dolerite and metapyroxenite.They are oriented NW-SE with 50 km long and average 5-30 km wide.
Ø  Anantpur dyke swarm and south of the Kadapa basin is the Tirupathi swarm. 
Ø  Anantpur dykes trends at NE-SW and ENE-WSW
Ø  Tirupathi Dykes show E-W and NW-SE trends.
          Groundwater conditions in Eastern Dharwar Craton
The major rock formation where high density of agricultural pump sets are concentrated is Granitic Gneisses occupying major portion of Telangana area, Chittoor, Anantpur, part of Kurnool district and  few pockets in other districts of Andhra Pradesh. Weathered zone and fractured zones are favorable ground water areas. Another major rock formation is schistose rock where the ground water yield is limited as clay material is more compared to weathered zone of Granitic Gneisses rock. The other category of rocks is intrusive rocks which occur mainly as dykes and comprise dolerites and amphibolites.  These rocks lack primary porosity and as a result, normally yield poor quantity of water. Wherever the dykes exist they act as barriers for ground water movement. Hence one side of dyke yields high ground water and other side poor yield or dry.
Highly to moderately weathered rock material:-This zone is restricted to shallow depths which generally vary up to 30m. Under favorable topographical and recharge conditions, this zone acts as shallow groundwater zone. Generally, Dug wells are feasible in this zone. Due to large number of wells constructed in this zone, groundwater in this zone is almost exhausted and water levels have gone down beyond this zone in major portion of the state except in few areas which are under the command areas of surface water bodies. Generally, under favorable conditions, the thickness of weathered zone is up to 15m in hard rocks.
Fractured rocks:-Fractures in hard rocks below weathered zone are prevalent in major portion of the Hard rock area. In such zones, dug cum bore wells were constructed wherever   Dug wells failed to yield Water. This practice of construction of dug cum bore wells also continued for few years and due to intensive energisation of agricultural pump sets, these groundwater abstraction structures also failed to yield water. Finally, Bore wells started with the depth range of 150 to 200 feet in the initial days and continued to Increase the depth of bore wells up to 300 feet in general and depth of bore wells in some areas gone up to 1000 feet. In Hyderabad city the depth of bore wells have gone more than 1000 feet. The successful Bore wells are those which struck fractured, jointed and fissured rocks. It is generally believed that the weathered zone is restricted to maximum depth up to 15m and fractured zone usually up to 30m and in higher depth fractures/joints are absent. In continental crustal rocks like Peninsula Gneiss it may be correct but in Granitic Gneisses (Dharwar Batholithof EDC which are formed due to partial melting of the continental crust during subduction or during rise of mantle plume, fracture/joints might have formed in higher depths also during the cooling history of Granitic Gneisses (Dharwar Batholith) and subsequent shrinkage of rocks.  In the light of above theory, the fracture/joints encountered up to the depth of 1000 feet and above may be justified.
 However, delineation of such fractured zones in higher depth is very difficult. If the thickness of water bearing strata is quite significant and yield large quantity of water, Geophysical methods like Resistivity survey can delineate the fractured zones at higher depth. But if the aquifers are very limited in thickness, it is difficult to identify such zones. It is common observation that deep bore wells up to 1000 feet are drilled without any technical guidance and whenever bore well is successful; others in the same locality also follow the same depth for construction of bore wells. But in such attempts, failure rate of bore wells is more  and in several cases farmers tried more  number of bore wells say 5 to 10 numbers to get success but they failed to get  water and also miserably failed financially.
After 1980’s number of agricultural pump sets increased mostly in hard rock areas of Telangana area, chittoor district, Anantpur, Kadapa and Kurnool districts thereby increased the exploitation of Ground water resources.   About 65% of Agricultural pump sets against the total  33 lakhs  of existing pump sets are  located in Granitic Gneisses  and Schistose rocks  (Hard  rocks ).The highest number of  3.20 lakhs pump sets  in Karimnagar district, 2.90 lakhs in chittoor district, 2.80 lakhs in Nalgonda district, 2.75 lakhs in Warangal district, 2.25 lakhs each  in Nizamabad and Mahabubnagar  districts,2.15 lakh in Medak and more than 2.0 lakhs in Anantpur district.  This has resulted in decline of water levels, decrease in discharge rate and transmissivity values and increase in power consumption. The aquifer characteristics of Granitic Gneisses during 1980’s and in recent years are given below:-
Sl.No
year
Discharge(Q) m3/day
Transmissivity
(T) m2/d
Depth range
(m)
Depth to water level(M)
Power consumption (kwh/units)per pump set per year
Acres/pump set
v1
1980
516-691
68-254
DW  4-20
5-15
2500
1-8
2
2003 onwards
18-54
6-40
BW 50-120
20-38-14% wells
8-20-30% wells
5-10-32% wells
72 m DTW in Agali village in Anantpur
7000
1-2
                                                                                                                                                                               
As the hard rocks having low storage space (water bearing and transmitting capacity) increased exploitation of the groundwater over the last few decades has resulted steep decline of water levels. Hence access to Groundwater become difficult due to high cost and high risks of getting adequate water. Generally, it is observed that wells which can sustain 50 m3/day can be said to be moderate and sustainable.  When Transmissivity ‘T’ of an aquifer is 100 m2/d or more, well yield can be adequate. The above data (in Table) indicate ‘T’ values are on very much on lower side and minimum discharge (18 m3/d) values are on lower side. Partial penetration and vertical heterogeneity might also be the reasons for low yields and transmissivity values.  
As per the field observations, two decades back, density of wells used to be 5 wells per Sq.Km and at present increased up to 20 wells per Sq.Km. Hence, increased the possibilities of interference of wells and decline of water levels.  As already mentioned that 85% of land area in Andhra Pradesh and Telangana states is underlain by Archaean basement rocks. Out of these 85% rocks, 20% area in major irrigation canal command area, 30% in poorly developed schistose rocks outside irrigation command area, and balance 35% area in deeply weathered and fractured hard rock aquifers outside canal command area.
          Area under major irrigation canal command area
  Groundwater conditions of hard rock areas falling under canal command area of Godavari, Krishna and Penna Rivers multipurpose irrigation projects is somewhat satisfactory.  The existing and proposed major irrigation projects and the area covered under each project are given below. 
1.Sriramsagar Project,Stage-1: Works started in 1963 to create a potential of 3.92 lakh hectares been partially completed to supply water to 2.87 lakh hectare and irrigate 1.28 lakh hectare in less developed districts of 1.Adilabad,2.Nizamabad,3.Karimnagar,4.Warangal districts.  Except Adilabad district other districts are predominantly covered by hard rocks.  In Karimnagar district highest number of agricultural pump sets is operating i.e. nearly 3.2 lakh pump sets. In Warangal district 2.75 lakhs and in Nizamabad district 2.25 lakhs pump sets are operating.
2. Sriramsagar, stage-2: This project was already sanctioned and works are yet to start. Under this project Warangal, Khammam and Nalgonda districts will be benefitted for irrigation purpose.
3. Sriramsagar flood flow canal:- This project envisaged to irrigate 2.20 lakh acres  in Karimnagar, Warangal and Nalgonda districts.
4. Devadula Lift irrigation Project:- The location of the lift point on Godavari is 12 Km downstream of Ichampally Dam site, near Devadula village of Warangal district. It is proposed to irrigate large ayacut available in Karimnagar, Warangal, Nalgonda and Medak districts which are backward upland areas chronically affected under drought conditions. To bring this area under cultivation Lift is inevitable as the river flow at +90M level and the ayacut is at +360M and up to +500M contours.50 TMC of water is proposed to be lifted and supply for irrigation.
5.  Nizamsagar Project: Already existing irrigation project benefit 0.97 lakh hectares in Nizamabad district.
6. Proposed Pranhita and Chevella Project is proposed to irrigate 16.4 lakh hectares in Nizamabad, Adilabad, Karimnagar, Medak, Rangareddy, Warangal and Nalgonda districts. 
In all the above projects, the canal net work is located in hard rock terrain and these projects improves the groundwater conditions of the area wherever the canal net work spreads. Besides the canal net work, Artificial recharge of groundwater projects also can be proposed in suitable areas diverting the canal water  to bring back the deep water levels to safe levels so that consumption of power will be reduced and beneficial to power utilities and individual farmers.      
        The Eastern Ghat Mobile Belt (EGMB)- (In the above map shown as Khon-
         dalites and Charnockites)                            
EGMB is NE-SW trending arcuate Pre-Cambrian fold belt extending from Cuttack in Orissa to Nellore in Andhra Pradesh. Maximum width of 100 Km in North and less than 20 Km in South. EGMB is in contact with Singhbhum Craton in North, Bastar Craton in West, Dharwar Craton in South and East by Bay of Bengal. In western side with Bastar Craton the contact is marked by a shear zone and regarded as continuation of Sileru shear zone. The contact between EGMB and Singhbhum craton is marked by shear zone i.e. sukinda thrust.
East of EGMB also has one shear zone at which Chilka Lake is located.
EGMB is dissected by two prominent Rifts with infillings of Gondwana sediments.
1.       Mahanadi Graben
2.       Godavari Graben
Rifts trend NW-SE
Origin of EGMB-
EGMB has been divided into two segments namely North EGMB (NEGMB) and South EGMB (NEGMB) by NW-SE Godavari graben filled with Gondwana formations. Both northern EGMB and south EGMB have undergone high-pressure isobaric cooling (IBC) The isobarically cooled rocks of NEGMB have been uplifted by isothermal decompression (ITD) during an Orogeny. Basic magma is the source for high temperature heating of the deeper crustal rocks.
The SEGMB escaped the Orogeny as the rocks retain older ages and do not show isothermal decompression. 
The prevailing NE-SW trend of the fold belt suggests a dominant E-W compression during the Eastern Ghats Orogeny. The compression is attributed to the collision between the continent of India (eastern part) and the Antarctica, giving rise to this Eastern Ghats fold belt.
Collissional processes have been responsible for the formation of mobile belts as well as thrust zones.
The folding events are thrust –related deformation.
The EGMB is supposed to have been juxtaposed against the East Antarctica in all Proterozoic reconstructions. 
The deformation/fold phases have caused sufficient shortening of the crust which finally yielded to shearing and helped excavate the high-pressure granulites to shallower depth to be emplaced on the cratonic rock. 
The last episode of deformation is marked by open folds, the axial plane of which is nearly parallel to the shear plane. The Granulite-Khondalite rock suite of EGMB was excavated along a shear zone.
The entire Charnockite rocks of EGMB have been exhumed by up thrusting along a ductile shear zone, the shear zone is found around the Proterozoic fold belt.
Godavari Graben is devoid of any igneous material but contain sediments of Pakhal Group and Gondwanas.
Ground water conditions in Charnockites and Knondalites   
The area underlain by Khondalites and Charnockites are located in hilly and forest areas in Visakhapatnam, Vizianagaram and Srikakulam district inhabited mostly by Tribal population hence the exploitation of ground water resources is low to moderate. Up to 2000 year, mostly Dug wells were the main ground water abstraction structures and after the year  2000 onwards bore wells  become common ground water abstraction structures but the density of wells are low to moderate.  The yield of Bore wells ranges from 20-180 m3/d in Khondalite and Charnockite rocks and yield of dug wells was 18-90 m3/d. Valley fill area and foot hill zones are potential areas for ground water exploitation. Dominant E-W compression during the Eastern Ghats Orogeny results in development of fractures in the rock formations which are good source for groundwater.   The depth to water level as on 2012 in Khondalite and Charnockite formations varies from 2-13m but in Guntur district the DTW is 27m and in West Godavari district is 19m.

 KADAPA ROCK FORMATIONS OF ANDHRA PRADESH- (In the above map shown as Cuddapahs.)
The crescent shaped Kadapa basin with its convexity to the west occurs in the eastern dharwar craton underlain by basement rocks. The Kadapa super group of rocks consists of three sub-groups namely Papagni group, Chitravathi and Nallamalai groups.
Papagni and Chitravathi group of rocks occupied western portion of the basin while the Nallamalai group of rocks occupied eastern portion of the basin.  The Papagni sub-basin in the western portion of basin marked by volcanic rocks in the form of sills and flows while the eastern side of the basin is marked by intensely folded and highly sheared Nallamalai group of rocks.
The equivalent of Kadapa basin rocks occur in either side of Godavari Graben. The Northeastern part of Kadapa basin where the different structural trends culminate is the site of maximum tectonic disturbanc.Thenumber of shear zones show the close relationship with the thrust boundaries of the Nallamalai basin.


SUBDIVISIONS OF KADAPA FORMATIONS:-
KURNOOL GROUP          Banganapalli Quartzite etc.,
NALLAMALAI GROUP      Bairenkonda Quartzite, Nagari Quartzite
                          ----------- Tectonic Contact------
CHITRAVATHI GROUP     Gandikota Quratzite, Tadipatri shale
                                            Pulivendla Quartzite.
PAPAGNI GROUP             Vempalli formations, Gulcheru Quartzite
 It is assumed that extensional tectonics and compression played an important role in the evolution of Kadapa basin. Extensional tectonics followed by volcanic activity and normal faulting resulted in the formation of Papagni and Nallamalai basins. In general, the extensional tectonics is widespread, while the compressive deformation is restricted to narrow zones.
LOWER KADAPAS
Indications of marine, intertidal and sub-tidal origin observed in Vempalli, Chitravathi and Tadipathriformations.  The following indications support the above theory.
1.       Shelfal mud deposition in the upper part of Vempalli formation.
2.       Laminated shales at the top suggest shore face inner-shelf deposition.
3.       Algal laminites, Stromatolites and ripple sandstone suggest an intertidal, sub-tidal regime in Tadipathri formations.
4.       Gandikota Quartzite represent a bar inter bar facies with tidal influence.
UPPER KADAPAS
1.       Nallamalai group of rocks are folded and faulted
2.       Consists of sandstone dominated Bairankonda Quartzite
3.       Cumbum formation consists mainly of Shales with Limestone intercalations.
4.       4. Nallamalai fold belt has been regarded as major strike slip fault associated with   Subduction and Transpression.
5.       Nallamalai group show a tidal and storm influence indicating connection with open Sea.     
Two numbers of cross fault that cut across the entire basin observed in the eastern                                                       part of basin.
1.       Gudur-Kadapa fault
2.       Veldurthi-kalva-Gani fault.             
 Ground water conditions in Kadapa and Kurnool formations
The kadapa and Kurnool system of rocks comprises of Quartzites, Shales, Slates and limestones also belongs to consolidated rock types as they have undergone large scale compaction, folding, faulting and metamorphism. The primary porosity and permeability of these formations have been very much reduced.However, the extensional tectonics and compression forces which played important role in the evolution of Kadapa basin might have produced large number of fractures which are good source for availability for groundwater.  Under favorable conditions, the fractured shales and cavernous limestones yield moderate amount of water. Shelfal mud deposition in the upper part of Vempalli formation and other formations prevent rainfall recharge to groundwater and there is likely failure of Bore wells drilled in such areas. The Quartzite rocks in most of the areas exist as ridges and hilly terrain which acts as run-off zone. In Shales and Phyllites the DTW varies from 21 to 53m and in Kurnool formations the DTW varies from 14-38m.
                                                                                                                                                                        
GONDWANA ROCK FORMATIONS OF ANDHRA PRADESH – (In the above map shown as upper and lower Gondwanas.)
Gondwana land is part of Pangaea super continent that existed 510 to 180 M.Years ago Included Antarctica, South America, Africa, Madagascar and Australia. Some 170-180 M.Years ago many fissures were formed through which lava was outpoured to the surface giving rise to the Rajamahal Hills. This was probably the time of disintegration of Gondwana land.  East Gondwana began to separate about 120 M.Years ago when India began to move north wards.  The Madagascar block  was broken off India. The separation (India-Madagascar) coincides with the eruption of Deccan Basalt.
Gondwana formation in Andhra Pradesh.
The Gondwana formations represent about 5000 m thick sequence ranges in age from Permo-Carboniferous to Early Cretaceous Gondwanas in A.P deposited in rift valleys or Grabens in NW-SE direction along River Godavari extending from Adilabad district to Eluru in West Godavari district.
These rocks lie unconformably on Proterozoic (Kadapa) formations in Pranhita-Godavari basin. The coastward extension of Godavari-Pranhita Graben (Gondwana) is terminated by NE-SW trending Bapatla ridge along the Eastern Ghats characterized by ridges and grabens which are the sites of sedimentation. The tilting of basins eastwards resulted in drowning of the coastal land. After Godavari-Pranhita
Graben, Gondwana formations lying on Archaean formations toward Delta region.  Gondwana rocks are exposed in few locations but larger part lie concealed under younger deltaic and marine sediments of coastal and Off-shore shelf.
ORIGIN OF GONDWANA FORMATIONS
The  Gondwana  succession in south India represent glacial beds at base(Talchir) ,Coal measures In the middle(Barakars) and red beds at the top. Basement lineament, control the origin and evolution of sedimentary basins. The basement of Gondwana formations in Pranhita-Godavari is Proterozoic age was formed due to collision of various proto continent (Naqvi & Rogers, 1987). The Proterozoic sedimentation and merger of gondwana land in Carboniferous period initiate Gondwana sedimentation.  Gondwana sedimentation begins with glaciations in northwesterly sloping valley.  Subsequent deglaciation might have provided initial depression and controlled basin formation.  Repeated rifting of Pre-gondwana basement took place in Proterozoic age in Pranhita-Godavari valley area. The gondwana basins of Peninsular India are therefore, bounded between two rift episodes of Early Permian and late Triassic/Jurassic respectively.  The former initiated gondwana basin development following deglaciation whereas the later terminated sedimentation.(R.C. Tiwari and Watare Maejima,2010)
Groundwater conditions of Gondwana rock formations
 Among the Gondwana formations the Sandstones are of importance from groundwater point of view. The impervious shale or clay layers form confined beds to give rise to semi-confined to confined conditions. 
The sandstone of Kamthis stage located in Telangana area and its equivalent of Chintalapudi sandstone in West Godavari district are highly productive groundwater zones yielding high discharges throughout year.
                               Fluvatile deposits                                                                Coastal deposits
Upper            )       Chikila stage            --      ---         ---                                  Tirupathi Sandstone
Gondwana    )       Kota stage                                                                           Raghavapuram Shales
                               Maleri stage                                                                        Gollapalli Sandstone
                              Kamthi stage         --           ---           ---                              Chintalapude Sandstone
Lower             )     Barakar stage
Gondwana     )     Talchir stage
In West Godavari district, Gondwana rock formations are prominently exposed in the upland areas in northern portion of the district.  Chintalapudi sandstone equivalent of Kamthi sandstone of Lower Gondwana formations occupied the north western portion near Chintalapudi, Kamavarapukota villages Etc, followed by Raghavaram Shale occur in narrow elongated strip south of chintalapudi. Tirupathi .Sandstone occupied the area between Rajahmundry sandstone in south and Raghavaram Shale in north covering Dubacherla, Nallajerla, Polavaram, NW of Devarapalli and Gopalapuram villages. 
LOCATION AND HYDROGEOLOGICAL CHARACTERISTICS OF GONDWANA FORMATIONS
SL.NO
Stage
Rock Type/Aquifer
Depth
m
Discharge
LPS
Drawdown
m
Transmissivity
m2/d
Locations/Areas
1
Gollapalli
sandstone
Sandstone U.C and Conf
600
8-60
--
80-900

2
Tirupathi
sandstone
Sandstone
300
10-40
6
86-1900


Raghavapu
ram shale
Has
Limited scope
 for
Gr .water
development.
3
Barakar
Sandstone
--
3.30-
16.20
12-38
18-84

4
Kamthi
Sandstone
250
4-50
9-30
28-950

5
Chintalapu-di
Sandstone
50-150
7-16
7-13
150-303 flowing conditions

Comparison of aquifer characteristics like discharge and Transmissivity values during the period from 1980 to 2010 indicated that there is decrease in discharge and Transmissivity values in Chintalapudi sandstone in West Godavari  district and  in Kamthi Sandstones covered in Telangana area, almost no change in the values of Transmissivity but there is change in the discharge of wells. River Godavari is recharging the Gondwana formations in both Telangana and West Godavari districts besides precipitation annually. Large number of high capacity pump sets is operating in West Godavari district compared to Tube wells operating in Kamthis Sandstone area. The details are given below:-
SL.NO
YEAR
DISCHARGE  ‘Q’ M3/D
TRANSMISSIVITY
‘T’  M2/D
DEPTH
RANGE   (M)
DEPTH TO
WATER LEVEL(M)


KAMTHI SANDSTONE
TELANGANA


1
1980
1630-4197
50-957
Up to 250
2-10
2
After 2000
1000-1260
28-950
100-300
24-32


CHINTALAPUDI SANDSTONE
W.G.DIST


1
1980
176-2254
30-3540
30-150
2-7
2
After 2000
187-408
150-303
100-300
16-69m
In Koyyalagudem village the DTW is 69m

If the  proposed Polavaram project canals are constructed from Polavaram to Buttayagudem,Koyyalagudem,Jangareddygudem and Chintalapudi instead of present layout of Polavaram to Devarapalli,Bhimadolu,Eluru and to Vijayawada( parallel to existing  Doweleswaram project canals) there is good recharge to ground water aquifers in upland areas and could yield adequate water . As the canal works are under progress towards Bhimadolu area, separate canal net work could be designed from the proposed Polavaram Dam -if feasible- toward upland areas of west Godavari district. If this project is realized, the Gondwana formations in Telangana area, West Godavari district and Tertiary Sandstones in East and West Godavari district would be formed as Ground water Sanctuary’s. In case of severe drought conditions, these aquifers can meet the drinking water needs of neighboring areas. Or these formations could be one of the source for” Water Grid” –a concept which is actively under consideration by present governments taking the example of Gujarat model.
TERTIARY RAJAHMUNDRY SANDSTONE OF COASTAL ANDHRA PRADESH.
The highly potential rock formation for groundwater development is Tertiary Rajahmundry sandstone located on either side of Godavari River in East and West Godavari districts. Rajahmundry Sandstone is fluvial, unfossiliferous, ferruginous and feldspathic sandstone of Oligo-Miocene age equivalent to that of Ravva formation of Off-Shore area.
Resting unconformably on the older rocks including Khondalite and Charnockite rocks forms as small hills in the Coastal area.  The 600 m thick succession of Rajahmundry Sandstone made up of coarse grained sandstone with subordinate clay stone and pebble beds, hence formed as the highly favorable Groundwater zone, next to alluvial formation in the state. 
Location and occurrence of Rajahmundry Sandstone
SL.No
District
Main villages covered
Discharge LPS
Drawdown (m)
Transmissivity m2/day
1
East Godavari
Vemagiri,  Rajahmundry,  Dowleswaram
Balabhadrapuram, between Kadiam and Kasavaram, Peddapuram, Samalkot, Rangampet,Gandepalli.

10-128
6-15
86-576
2
West
Godavari
Eluru(S),Bhimadolu,Kovvur(W),Dwaraka Tirumala,Gopalapuram,Pedavegi,west of Nallajerla,Chagallu(W),Devarapalli(S)
-do-
-do-
-do-
3.
Krishna
Nuzuvidu,Gannavaram
-do-
-do-
-do-

The depth range of Tube wells ranges from 100-200m in East Godavari and from 100-300m in West Godavari districts. Transmissivity of aquifers ranges from 86-2500 m2/day .In West Godavari and Krishna district the Tertiary formations are noticed in the contact zone between Gondwana and Alluvial formations. The deep Tube wells in this area yield groundwater under confined (artesian) to semi-confined conditions.  Even free flowing wells were also noticed few years back but at present free flowing conditions  ceases to exist due to high density of Groundwater abstraction structures. 
Comparison of the aquifer characteristic of Discharge and Transmissivity  during the period from 1980 and after 2000 indicate that there is decrease in yield of Tube wells   but there is no change in Transmissivity values as given below:-
TERTIARY SANDSTONE OF EAST AND WEST GODAVARI DISTRICTS
A. West Godavari District
SL.NO
YEAR
DISCHARGE ‘Q’ M3/D
TRANSMISSIVITY ‘T’ M2/D
DEPTH RANGE (M)
DEPTH TO WATER LEVEL(M)
1
1980
1368-4320
299-2550
Up to 300
7 and free flowing conditions.
2
After 2000
126-252
300-2500
100-300


  
B.East Godavari District
SL.NO
YEAR
DISCHARGE ‘Q’ M3/D
TRANSMISSIVITY ‘T’ M2/D
DEPTH RANGE (M)
DEPTH TO WATER LEVEL(M)
1
1980
NOT
AVILABLE
30-50 shallow TW’s
100-200 deep TW’s


2
After 2000
630-1260
36-2261
100-300
20-61m.In Gandepalli village the DTW is 61m.

The Seaward extension of Rajahmundry sandstone unconformably covering the Narsapur Claystone belongs to the Miocene to Pliocene temporal span. In the Off-shore regime, the Mio-Pliocene equivalent of the Rajahmundry sandstone is the Godavari clay stone, containing layers of sandstone. 
The water quality of Rajahmundry sandstone deteriorates towards the coast while their equivalents of Cuddalore sandstone even near coast also, the quality of water is good.
DELTA FORMATION AND ALLUVIAL FORMATIONS.
Krishna Godavari basin/delta came into existence following rifting along eastern continental margin of Indian craton (Eastern Dharwar Craton in Andhra Pradesh) in early Mesozoic. The down to the basement faults which define the series of horsts and grabens are aligned NE-SW along Pre-Cambrian Eastern Ghats Mobile Belt trend. In the marine shelf, Carbonates and Clastic sediments formed a fan-shaped delta along the ridges and turbidites covered the slopes and graben floors.  It could also be large prograding delta lobe over the coastal region where fluvial and marine sediments interfingered.  In Godavari Delta fresh water samples are generally coarse to very fine sands confined to along the ridges and Estaurine samples are fine sand to clays rich in organic matter are confined to slopes and grabens  yield saline water.
The chronological sequence of Delta formation are-
1 Rifting during permo-triassic
2. Followed by drifting results southerly, south-easterly tilt
3. Resulting marine transgression and deposition of shale sequence
4. Increased gradients for river systems and increased sediment load and significant sea level falls
5. Source for thick pile of sediment is long linear Gondwana belt located in Godavari graben.

Ground water conditions in Delta Area:-
 Alluvial deposits concentrated in East and West Godavari, Krishna and Guntur districts and in few pockets in Prakasam, Nellore, Srikakulam, Khammam and Karimnagar districts.
East Godavari district- Southern portion of district where along the River Godavari and Delta area, vast thickness of Alluvium formed. Along the River Yeleru also alluvial deposits formed. Deeper aquifers in the above areas are yielding saline water.   
West Godavari district: - Southern portion of district covered with highly thick alluvium. The basement rock struck at 3000m in this area compared to 500m in East Godavari and Guntur districts. Fresh water limited to shallow depth along canals, along River course. Shallow filter points are common in this area. Along Canals and Drains, small shallow pits are constructed to utilize the water for irrigation and during the non-flow of canal water shallow pits are used for fish ponds.
Krishna District: Shallow aquifers are yielding potable water and with depth, quality of water deteriorates. Krishna River between Ibrahimpatnam and Jaggayyapeta alluvial deposits comprising of sticky clay and silt occurred over a distance of 40 Km. It is observed that irregular nature of occurrence of alluvium. Hence a trial bore is necessary to ascertain the thickness of aquifer.
Guntur District; Along River Krishna, along Canals and in island areas of River, filter points are common. In Repalle, Tenali and in Bapatla fresh water is limited to pockets and lenses at shallow depths varying from 1m to 14m. Extensive fresh water aquifers at shallow depth are not possible in these areas.
ALLUVIAL FORMATIONS                                            
SL.NO
District
Common Groundwater Abstraction Structures
Depth
Range
(M)
Areas covered with Alluvium
Quality of Ground-
water
1
East Godavari
Filter Points


Tube wells
12-20


100-150
Alamuru, Ramachandrapuram Kakinada and Kothapeta areas

Pitapuram and Chebrolu areas

Up to the average depth of 45m, quality of water is potable.
HP of p.sets up to 25 also common.
2
West Godavari
Shallow Filter points
Upto 60m
Tanuku, Kovvur, South of Tadepalligudem.
Saline areas-Bheemavaram,Narsapur etc.
3
Krishna district.
Filter points


Shallow Tube wells
Up to 20m

Up to 100m
Divi,Bandar,Gudivada,Kaikalur,
Gannavaram,Nandigama(part)
Vijayavada(south)
With the increasing depth quality of water deteriorates.
4
Guntur district
Filter points
Shallow Tube wells
20-50

40-100

Along Krishna River and along Canals.

 Repalle, Tenali, Bapatla and partly in Chilakaluripeta, Duggirala, kothur and Amritalur areas.
With depth quality of water deteriorates.
SELECTION OF CORRECT SIZE OF AGRICULTURAL PUMP SET
Every pump set is manufactured for certain discharge (Q) and total head (H). Diameter of impeller and the speed (RPM) at which it is rotated decides the total Head (H). Area through which (impeller dia) the flow occurs and velocity of flow decides the discharge. Each pump set is manufactured with certain dia of impeller and fixed RPM. Hence Q and H are fixed for each category of pump set. For different requirement of discharge and total Head, the design of impeller and RPM changes.
To select the correct size of pump set, well should be tested for discharge, static water level, draw down etc.  Maximum discharge (generally during winter season) and maximum total head (during summer season) are to be selected for calculating the HP of pump set.
Discharge measurement:- For new bore well while the drilling is in the final stage and when Air compressor is  under operation, discharge of Bore well can be estimated roughly by using fixed volume Drum or by V-notch method. If possible after 24 hours, using the tape, the static water level of the bore well can be measured. Generally these details are not available at the time of installation of pump set. In such cases the discharge and Static water level of the neighboring  Bore wells having the same depth and  geological  formations  could be taken up for calculation. The discharge and Transmissivity details are also available in the reports prepared by Central Ground water Board and state Groundwater departments.http://www.cgwb.gov.in/District_Profile/AP/Kurnool.pdf
Static water level:- Central Ground water Board is maintaining National net work observation well data throughout Indiahttp://gis2.nic.in/cgwb/Gemsdata.aspx   and state ground water department maintain the observation well and Peizometer’s data in their state jurisdiction http://apsgwd.gov.in/swfFiles/reports/state/monitoring.pdf,   . The static water level data during summer season of nearby observation well  maintained  by ground water departments can be utilized if there is difficulty in collecting same from the well under investigation for  installation of pump set.
DRAW DOWN DATA:-The discharge and static water level data could be collected with some efforts but the data on draw down is very difficult to collect. Generally, Ground water departments conduct pumping tests like Step draw down and Aquifer performance test as a part of exploratory drilling activities and systematic ground water surveys.  But such data is very limited compared to large number of wells fitted with pump sets which are likely to be replaced with energy efficient pump sets. Hence as mentioned above, an attempt has been made to calculate the draw down data using the empirical formulas.
For calculating the correct size of pump set and measure efficiency of pump set installed , the two parameters like discharge and total head of ground water abstraction structure(well/Bore well/Tube well ) are necessary.  The total head includes depth to water well, maximum drawdown during summer season and fictional losses of piping system.  Static water levels during summer month can be taken from  National Net work observation well (CGWB) and observation well and piezometric water level data from state ground water department.  Discharge details of wells during maximum utilization of ground water can be obtained from existing district wise/state wise reports/CGWB aquifer atlas/Ground water user maps of CGWB ground water reports. 
But the data regarding drawdown of wells is not available in the above mentioned reports except for few wells where Aquifer performance tests were conducted. But the published data of such wells are limited to few locations.  Considering the large number of Agricultural pump sets likely to be replaced with energy efficient pump sets, draw down data for different areas with different geological conditions are very limited. Hence it is decided to calculate the drawdown data using indirect methods.
Approximate formulas for estimating Transmissivity from Specific Capacity:-
FormuIa-1. 
 Discroll (1986) estimates Transmissivity(T) from specific capacity.
 1. Metric system-
                T= 1.385 X Q/s                         confined aquifer
                T= 1.042 X Q/s                         unconfined aquifer
                 Where T Transmissivity in m2/d,   Q discharge in m3/d/m, s draw down in metres

Formula-2
 FPS system
                 T =     2000 X Q/s                    confined aquifer
                 T =     1500 X Q/s                   un-confined aquifer
                 Where T in us gal/d/ft, Q in gpm and s in metre
As the values of Transmissivity and discharge of the wells are available in the reports of CGWB, substituting these values in above formula, the value of‘s’ i.e. draw down can be calculated
Similarly the following formulas also used to calculate the drawdown.
Formula-3.
Vertical fracture model of Gringarten & Witherspon (1972) fractured hard rock areas. Assess Transmissivity from Specific Capacity.

                 T = 0.29(Q/s) 1.18
                  Where T in ft3/d/ft
                              Q in ft3/d
                              s in ft
Formula-4.
 Modified Theim’s equation is used for determining permissible drawdown.
       S         =    (528 X Q x log R/r )/  T 
                         where T in gpd/ft
                                      Q in gpm
                                     S drawdown in ft
                                     R radius of influence in ft  
                                     r radius of well in ft
Formula- 5. 
     Thomson etc calculated Transmissivity ‘T’ under steady state transient conditions.
                     T    =   Q/s x 1/2 x3.17x log R/r
i.e.                 T     = (Q   X   1  X  log  R/r)/( s X   2 X 3.72     )
                        Where T in ft3/min/ft
                                     Q in ft3/min
                                     s in ft
                                     R radius of influence in ft
                                    r radius of well  
 All the above formulas were used for calculating draw down substituting the values of Transmissivity and discharge and compared with the actual values of Draw down measured during the aquifer performance test. It is observed that sl.no 1 and sl.no 4 of above mentioned formula’s, the calculated draw down tallied with aquifer performance test value of draw down with  30% deviation in Kamthi formation , 20% in Granitic Gneisses formations , 80 to 100% in Chintalapudi  sand- stone in West Godavari and  60%  in Tertiary formations of West and East Godavari districts.
CALCULATION OF DRAW DOWN FROM EMPIRICAL FORMULAS

SL.NO
LOCATION
DRAWDOWN VALUE AS PER PUMPING TEST IN FT.
FORMULA-1 CONFINED AQUIFER D/D IN FT
FORMULA-2 UNCONFINED AQUIFER D/D IN FT.
FORMULA-3 D/D IN FT.
A
ALLUVIAL FORMATIONS
1
Eturnagaram,Karimnagar dist
117
92
72
87
2
Pedapudi,Krishna dist
7
4
3
3.5
3
Narayanpura,East Godavari dist
11
7
5
4
Chodavaram,Visaka dist
27
23
17
21
Per cent deviation in Draw Down
15-42
37-57
22-50
B
TERTIARY,RAJAHMUNDRY SANDSTONE
1
Viravalli,West Godavari dist
28
21
16
19
2
Takkapadu,West Godavari dist
59
26
20
24
3
Chagallu,West Godavari dist
33
7
6
7
4
Muppavaram,West Godavari dist
98
3
2
3
Per cent deviation in Draw Down
25-97
43-98
32-97
C
GONDWANA FORMATIONS
UPPER GONDWANA FORMATIONS
1
Bhimadolu-II,West Godavari dist
102
55
42
2
Kavaluru,West Godavari dist
27
8
6
8
3
Tirumalapalem,West Godavari dist
26
17
12
16
4
Nimmalagudem,West Godavari dist
44
24
18
35
Per cent deviation in Draw Down
35-70
54-78
8-35
LOWER GONDWANA
CHINTALAPUDI SST,EQUI OF KAMTHIS
1
Kallacheruvu,West Godavari dist
42
9
7
2
Jangareddygudem,West Godavari dis
58
128
96
119
3
Dharbagudem,West Godavari dist
91
170
128
158
Per cent deviation in Draw Down
78-120
40-83
74-105
KAMTHIS, TELANGANA
1
Narwa,Adilabad dist
92
111
83
103
2
Kaleswar,Karimnagar dist
100
164
124
152
3
Gangavaram,Khammam
57
50
37
46
4
Narvavarigudem,Khammam dist
29
16
12
24
5
Patwarigudem,Khammam
74
79
59
72
6
Koyyuru,
61
27
20
25
7
Yadlapalli,Karimnagar dist
74
40
30
37
Per cent deviation in Draw Down
12-64
9-67
3-59
GRANITIC GNEISSES
1
Damalacheruvu,Chittoor dist
44
60
45
50
2
Gundlapalle,Chittoor dist
31
94
71
79
3
Mattampalli,Chittoor dist
37
34
26
23
4
Mogili,Chittoor dist
18
25
19
22
5
Kalvagunta,Chittoor dist
30
33
25
28
Per cent deviation in Draw Down
8-39
2-30
6-38

DEVIATION OF CALCULATED VALUES OF DRAW DOWN COMPARED TO MEASURED VALUES  OF DRAW DOWN  DURING AQUIFER PERFORMANCE TESTS.
SL.NO
ROCK FORMATION
DEVIATIN RANGE IN PER CENT
AVERAGE VALUE IN PERCENT
1
Alluvium or Recent formations
15-57
36
2
Tertiary Sandstone(Rajahmundry sst)
25-98
62
3
UP Gondwanas (W.G. Dist)
35-78
56
4
Lower Gondwanas(Chintalapudi  sst)
78-120
100
5
Kamthis (Telangana districts)sst.
9-67
38
6
Granitic Gneisses
2-39
20
The above data can be further modified by calculating the values of draw down using the latest pumping test data in different rock formations by Ground water departments who has access to voluminous aquifer performance test data. This exercise will enable to predict the draw down values up to mandal and village level. Wherever the discharge, Transmissivity and Draw down values are available, the data should be made available to farmers or to the agencies who are engaged in the installation of energy efficient pump sets as a part of energy conservation programme. Maximum benefits of energy conservation can be achieved if the energy efficient pump sets are selected based on aquifer characteristics like discharge and total head of the wells.
REPLACEMENT OF EXISTING OLD PUMP SET WITH NEW ENERGY EFFICIENT PUMP SET.
Many state governments are planning to replace the existing inefficient agricultural pump sets with new efficient pump sets. For such new pump sets using the old pump set, measure the discharge (preferably during winter) static water level  and pumping water level  to  select the correct size of pump set. It is also advisable to calculate the efficiency of well using the old pump set. The details like discharge, total Head, voltage, current in amperes and power factor are to be measured using the old pump set. Due to inefficient pump set the values of Discharge, total head may be on lower side, hence  10 to 15% extra value may be added to these values  so that it cover friction losses and compensation to inefficient pump set.
                                             Out put
                     Efficiency = -------------
                                             Input                                          
                                            Q X H X 0.746 X100
                   Efficiency =    -------------------------
                                                Kwh x 76
                                        Q x H x 0.98
                  Efficiency = --------------
                                         Kwh x 76
             Where Q is discharge in Litres per second,
              H is total head in metres.
             Kwh is input energy. Kwh is calculated by measuring voltage, current in amperes and power factor.
            Input energy = v3 x V x I x P.F
 After installing the new pump set, Efficiency of pump set may be calculated  measuring Q,H,V,I and power factor. With the new pump set, there will be improvement in the Efficiency value.             
MATCHING OF PUMP CURVES AND WELL CHARACTERISTICS
Having known the discharge and total head, the correct size of pump set is selected on the basis of pump characteristic curves. These pump curves are plotted from the result of tests on a pump when running at its design speed.  They show the relationship between discharge, head, efficiency and Brake horse power.  Pump manufacturers provide characteristic curves or some time the details in tabular statement for the various models of the pumps. Each pump curve typically reflects a single model of pump made by manufacturer. It is usual to draw the discharge vs. drawdown curve of testing irrigation well on the same scale as the pump characteristic curve. The characteristics of the pump manufactured by leading manufacturer are matched with well characteristic curve (system head curve).This will lead to the selection of the pump which gives maximum efficiency and the desired discharge at the estimated total head. The point of intersection of head capacity curve of pump and well characteristic curve provide a point of selection. At the intersection of desired discharge (bottom scale) and head-capacity curve read the Head value on left side. In the Characteristic curve given below the value of Head at discharge intersection of head capacity curve is 11.5m.  Divide this value into the total head to determine number of stages.
                       


We have to select the make and model of pump which tallies with the well characteristics (discharge and Total head) and the efficiency curve reasonably flat at the top. The characteristic curve also shows the brake horse power of the driver of the pump. The Brake horse power can also be obtained from the following formula.

                BHP    =                          Q X H
                               --------------------------------------------------
                               76 X pump efficiency x motor efficiency    
                              Where Q is discharge in lps,
                              H is total head in meters.
                                          76 is work done by one HP (in Kg meters)in one second. One metric HP is the power to raise a mass of 76 kilograms against the earth’s gravitational force over a distance of one meter in one second. This is equivalent to 735.5 watts or 0.736 Kw. Brake horse power or pump input break horse power is the actual horse power delivered to the pump shaft.
Ideally pump should extract water at such a rate so that water level in the well stabilizes after some time and do not fall further. Within the stabilized water level (particularly during summer season) only submersible pump set should be installed. To monitor the water level in the well it is advisable to install 1 inch or 1.5 inch flexible PVC pipes in the bore well up to bottom of submersible pump set.
CONCLUSIONS
1. The Granitic Gneisses rock formation occupies major part of Telangana state, Chittoor, Anantpur and part of Kurnool district in Andhra Pradesh. Limited water bearing zone in the form of weathered and fractured zones in Granitic Gneisses. Sixty five per cent of 33 lakhs pump sets located in this area. The density of pump sets is more than 20 no’s pump sets  per Sq.Km. Due to this,  discharge of wells reduced and there is steep decline of water levels compared to the conditions existing 3 decades back.
Construction of Bore wells in the following Green schist belts and swarm dyke are not very productive from ground water point of view.  
·         Sandur schist belt
·         Ramgiri-Penekacherla-Serigeri-Hungund super belt
·         Kolar-kadiri-Jonnagiri-Hutti super belt
·         Veligallu-Raichur-Gadwal super belt
Swarm dykes:
·         Hyderabad dykes
·         Mahabubnagar dykes
·         Anantpur dykes
·         Tirupathi dykes.
In these dyke areas one side exists good ground water potential and other side, poor to dry Bore wells. North east of Kadapa basin experienced tectonic disturbance and Western side of Kadapa basin on convex side, there has been sequence of tectonic events of extension and compression evolution of Kadapa basin.
Before taking up ground water extraction programme and installation of efficient pump sets all the above aspects are to be taken into account. Detailed survey of Hydro geological conditions is necessary in this area.
2. Ground water development in Khondalite and Charnockites belongs to Eastern Ghats Mobile Belt (EGMB) and Shales, Phyllites and Quartzites of Kadapa and Kurnool formations under safe conditions and the yield of Bore wells also low to moderate due to limited water bearing zones in the form of weathered and fractured zones. The EGMB area is covered with hilly and tribal areas and Kadapa formations also dotted with hilly and valley portions. Quartzite rocks form as hills and ridges and Shales, Phyllites and Lime stone in plain and valley areas.
The Tertiary and Gondwana formation are highly productive from ground water point of view and high capacity pump sets (up to 25 HP) are operating in these formations. The data on discharge and Transmissivity of last 3 decades indicates that though there is reduction in discharge of wells but there is no change in Transmissivity values in Kamthi formations of Gondwanas and Tertiary Sandstones.
3. Due to high density of pump sets in hard rock terrain, HT/LT ratio is quite high results in high line losses. In such cases to reduce the line losses HVDS system can be encouraged.
4. In high density pump set areas wherever steep decline of water levels and reduction in discharge values observed, artificial recharge of ground water projects are to be taken up. As several  irrigation projects are under progress/proposal (in Godavari River) in Granitic terrain of  Telangana state, irrigation wells located in Karimnagar,Warangal,Nizamabad, Nalgonda,Khammam and Medak district get benefitted  wherever the area comes under   canal command  net work. Canal water also can divert to other neighboring areas to utilize the water for artificial recharge of ground water projects. In Mahabubnagar and Anantpur districts major portion of the area acts as catchment areas to major rivers. In Mahabubnagar district, Krishna River and in Anantpur district, Pennar River and its tributaries act as catchment areas.  Run-off in this area is more than groundwater recharge, hence several check dams may construct across the tributaries of these rivers so as to increase the groundwater recharge. Major portion of Medak,Nizamabad,Rangareddy districts, the terrain  looks like plateau with almost lying on  600m altitude (above sea level). In these districts revival of Tanks and Ponds and construction of new Tanks are helpful for the groundwater recharge. Up to Nagarjunsagar Dam the catchment area of Krishna river is surprisingly on northern side only i.e. in Telangana state and negligible portion in southern side. In this catchment area on northern side, check dams can be constructed on stream courses falling in the catchment of Krishna River so as to improve the groundwater recharge.
5. Ground water departments established net work of observation wells and water level measurement s taken quarterly to observe the fluctuation of water levels. It is advisable that in addition to water level monitoring, measurement of Specific Capacity values annually indicate the health of wells.
                                                        Specific Capacity (actual)
                   Efficiency of well   ---------------------------------------
                                                         Specific Capacity (Maximum)
                             Where, Specific Capacity actual is the value measured during investigation
                            Specific Capacity Maximum is the value measured at the time of construction of well                                                          
                            Or first time investigation.  
                        Specific Capacity is the ratio of Discharge to Drawdown. If Specific Capacity is high it means well is performing well and vice versa it is poor performance. In higher values of specific capacity Discharge is more and drawdown is less but if sp. capacity value is low, means Discharge is low and Draw down is more.
When Specific Capacity values are continuously recorded low, means there is decline of water levels. The reasons for the decline of water levels to be find out. One of the possible reason is interference of wells i.e. the distance between two wells is less than prescribed limit(less than 300m in hard rocks and 150m unconsolidated formations). In such areas artificial recharge of ground water projects are to be taken up.
For the selection of correct size of pump set to new irrigation wells and replacement of old pump sets with energy efficient new pump sets, service of Hydrogeologist and Electrical Engineers is very helpful in getting correct details of Discharge, Total head, sustainablity of groundwater yield, voltage regulatios, input energy and power factor which are useful in the calculation of efficiency of pump sets etc.
ACKNOWLEDGEMENTS
 The hard work,  devotion and the  difficult field conditions  under  which the Geologists mapped the Geological formations, Geophysicists  carried out the investigations and Drilling crew carried out the exploratory  work and the valuable articles contributed by  Geoscientists enable me write the article.                                                                                                                                                         
REFERENCES
Ø  Aditi Mukherji, Tushar  Shah and  Shilp Verma;  Electricity Reforms and their impact on Groundwater                                                                                                                                                      use in states like Gujrat,West Bengal and Uttarakhand, India.
Ø  Aditi Mukherji, Tushar Shah and Mark Glordano; 2012. Managing Energy-Irrigation Nexus in India-2012, IWMI-TATA water.
Ø  A.K.Jain, B.M.Muralikrishna Rao, M.S.Rama Mohana Rao, M.Venkataswamy; Groundwater Scenario in Andhra Pradesh-Dec. 2009
Ø  A.M. Michael, S.D. Khepar; Water Well and Pump Engineering, Tata McGraw-Hill Publishing Company Limited, New Delhi.
Ø  APGWD Report, Groundwater Estimation in 1993
Ø  APGWD Report, Groundwater level Scenario in Andhra Pradesh-March, 2012.
Ø  CGWB-1980, Groundwater Resources of Andhra Pradesh.
Ø  CGWB-2003, Groundwater User Maps-Andhra Pradesh.
Ø  CGWB, District Reports of Andhra Pradesh.
Ø  CGWB-2012, Aquifer Atlas of India.
Ø  Central Institute of Rural Electrification-Pumping Systems-Reading Material
Ø  C.Satyanarayana-1994. Improper Matching of wells and pump sets-Need for carrying out Step draw-down test in representative wells, National  Seminar on Conservation of Energy in Agricultural Pumping System.CIRE,Hyderabad.
Ø  David Hundtley, Roger Nommensen and Duane Steffey. The use of Specific Capacity to assess Transmissivity in Fractured rock Aquifers.
Ø  Dilip Saha,Vikash Tripathy; Palaeoproterozoic Sedimentation in the Kadapa basin in South India and Regional tectonics: a review.
Ø  Hector Garudu fio, Stephen Foster, Pradeep Raj et. April 2009. Addressing Groundwater Depletion Through Community Based Management Actions in the Weathered Granitic Basement Aquifer of Drought-Prone Andhra Pradesh-India.
Ø  Joseph G.Meert, Manoj K.Pandit, Vimal R.Pradhan et la; 2010. Precambrian Crustal Evolution of Peninsular India: 3.0 billion year Odyssey.
Ø  Nisha Naid and Tushaar Shah, IWMI-TATA-2012. The other side of India’s Electricity-Groundwater Nexus.
Ø  O.P. Pande and P.K.Agrawal-Lateral Zonation around Archaean Nucleus of the Dharwar Craton, India.Its deformation, segmentation and subsequent breakup.
Ø  Ramachandra Tiwari and Wataru Maejima; Origin of Gondwana Basins of Peninsular India.
Ø  REC-Best practices for Agricultural Pump sets and Rural Demand side Management (DSM), USAID, Ministry of Power, Drum training programme.
Ø  Robert E.Mace;  Determination of Transmissivity from Specific Capacity Tests in Karst Aquifer.
Ø  R.S.Sharma; 2009.Cratons and Fold Belts of India, Lecture notes in Earth Sciences.
Ø  T.R.K.Chetty, NGRI; Tectonics of Proterozoic   Kadapa Basin, Southern India: A conceptual Model.



                                                                                                                                                       ANNEXURE 1                                                                                                                                                                                                                                                                                              AREAS LOCATED IN GRANITIC GNEISS OF EASTERN DHARWAR                           CRATON IN ANDHRA PRADESH     
SL.NO
District
Major portion/Small part.
If small part name of Tk/Mdl
If major part, name of other Tk/Mdl and rock type.
Remarks
1
Nizamabad
Complete district
         -------
         -----

2
Ranagareddy
Complete district
        ---------
        -------

3
Nalgonda
Major part
         --------
Devarakonda-SE portion,Miryalaguda-South,Zaheerabad-South.covered by Kadapa formations

4
Medak
Major part
         ------
Zaheerabad-partly by Deccan Traps

5
Mahabubnagar
Major part
      --------
Achampet-SW portion covered by Kadapa formations.

6
Karimnagar
Major part
       -------
Manthani and part of Peddapalli covered by Gondwana formations.

7
Warangal
Major part
       --------  
Narsampet,Mulug and Parkal partly covered by Kadapas etc.

8
Chittoor
Major part
    ---------
Srikalahasti and Vayalpadu covered by Kadapas.

9
Anantapur
Major part
  -------------
Singanamala,Gooty and Kadiri covered by Kadapa formations.

10
Kurnool
Western portion of the district, Aler,Adoni,yemignur,Pattikonda Taluks etc


-----
Eastern part of district covered by Kadapas and Kurnool formations.

11
Khammam
Small part of district
Khammam,Yellandu,Burgampadu-SE,Nugur-SE,Kothagudem-E and W,Madhira.

Other formations-eastern part of district covered with Gondwanas(NW-SE),Western side with Dharwars and Archaean formations.


Adilabad
Small part of district
Luxettipet except eastern part,Adilabad-south,Mudhole-except North west.and Nirmal.


13
Nellore
Small part of district
Udayagiri,Atmakur and Rapur.


14
Prakasam
Small part of district
Podili-east,Ongole-west,Darsi-east,Addanki.



15
Guntur
Small part of district
Narsaraopet, Sattenapalli,Guntur partly


16
Krishna
Small part of district
Jaggayyapet,Vijayawada-North,Tiruvur,Nu-zuvidu-west, Gudivada-NW








                                                                                         
                                                                                                                                      
ANNEXURE-2
AREA COVERED BY SCHISTS AND RELATED ROCKS OF EASTERN DHARWAR CRATON
SL.NO
District
Major portion/Small part.
If small part name of Tk/Mdl
If major part, name of other Tk/Mdl and rock type.
Remarks
1
Prakasam
Small part
Darsi-central,Podili-Central portion,Kanigiri Taluks
-------

2
Nellore
Small part
Udayagir,Atmakkur,Nellore-west,Gudur-West,apur-West,


3
Guntur
Small part
Vinukonda-south,Sattenapalli-part,Narsaraopet-part


4
Krishna
Small part
Nandigama-west,Vijayawada-part,Nuzuvidu-west,Gudivada-north west.


5
West Godavari
Small portion
Chintalapudi-west


6
Khammam
Small portion
Khammam-partly,Madhir-partly.









                                                                                                                                     
 ANNEXURE-3
AREA COVERED BY EASTERN GHAT MOBILE BELT- CHARNOCKITES AND KHONDALITE ROCKS

Sl.No
District
Major part/Small part
If small part,name of Tk/Mdl
If major part,name of small part Tk/Mdl and rock type.
Remarks
1
Srikakulam
Major portion
---
Alluvium in Palakonda,Narasannapet,Patapatnam,Sompeta partly

2
Vizianagaram
Major portion
---
Alluvium in Parvathipuram partly

3
Visakapatnam
Major portion
----
Alluvium in Elamanchali and Bheemunipatnam Partly

4
East Godavari district
Small portion
Rampachodavaram,yellavaram,Prathipadu,Rajahmundry north,Peddapuram north,Tuni north
--------

5
West Godavari district
Small portion
Polavaram


6
Krishna
Small portion
Nandigama partly


7
Guntur
Small portion
Sattenapalli central


8
Prakasam
Small portion
Ongole patly


9
Nellore
Small portion
Kavali-west


10
Khammam
Small portion
Burgampadu SE portion,Bhadrachalam-SE portion,Kothagudem-East



    
                                                                                                                                            ANNEXURE-4
AREAS COVERED BY KADAPA FORMATIONS IN ANDHRA PRADESH
SL.NO
District
Major portion/Small part
If small portion name of Tk/Mdl
If Major portion name of Small portion of Tk/Mdl and rock type
Remarks
1
Kadapa
Complete district
---
--

2
Prakasam
Small portion
Giddalur,Markapur
Podili-west,Darsi-west


3
Guntur
Small portion
Piduguralla,Macherla,
Gurjala,Vinukonda- north


4
Khammam
Small portion
Yellandu central,Burgampadu central,Nugur-NW portion,


5
Warangal
Small portion
Narsampet-east,Mulug-east,Parkal-north-east.


6
Adilabad
Small portion
Adilabad-north,Asifabad-west and north-east,Luxettipet-east


                                                                                                                             

                                                                                                                                     ANNEXURE-5
                                         
AREAS COVERED BY KURNOOL FORMATIONS IN ANDHRA PRADESH
Sl.No
District
Major portion/Small part
If small part name of Tk/Mdl
If Major portion, name of small portion of Tk/Mdl and rock type.
Remarks
1.
Kurnool
Half of the district in eastern part of district, covering Banganapalli,Allagadda,Nandyal
Atmakur, Nandikotkur, Kiolakuntla.
-----
Western part of district. east of Dhone, and Nandikotkur covered by Granitic Gneiss.


2
Chittoor
Small portion
Srikalahasthi,Vayal
Padu.




ANNEXURE-6                               
AREAS COVERED BY GONDWANA FORMATIONS IN ANDHRA PRADESH
Sl.No
District
Major part/Small part
If small part name of Tk/Mdl.
If major part name of small part Tk/Mdl and rock type
Remarks
1
Adilabad
Small portion
Sirpur,Chinnur
Asifabad except west and north west portion
-------

2
Karimnagar
Small portion
Manthani,peddapalli North east  portion


3
Warangal
Small portion
Mulug except west portion,Parkal-eastern portion


4.
Khammam
Small portion
Yellandu-Eastern side, Burgampadu-north west portion, Kothagudem-central.


5
West Godavari
Considerable area
Lower Gondwana:-
 Chintalapudi-except west,Kamavarapukota,Lakkavaram,
Jangareddygudem,Koyyalagudem,
Upper Gondwana:- Dubacherla,Nallajerla,Potavaram,North west of Devarapalli  and Gopalapuram.