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    Presentedby

    R. SUBALAKSHMI (2009262018)M.E - IWRM

    Supervisor

    Mr. V. LENIN KALYANA SUNDARAMAssistant Professor

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    Groundwater has become an essential resourceover the past few decades due to the increase in its

    usage for drinking, irrigation and industrial uses etc. The quality of groundwater is equally important as

    that of quantity. Rising population density will continue to have an

    impact on the quality and quantity of local water

    resources. Urbanisation reduces infiltration rate of groundwater

    and increased runoff.

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    The scope of the study is how ground waterquality, quantity and livelihood of the people are

    change due to urbanisation. Urbanisation affects land, groundwater and

    peoples livelihood. The over extraction of water and improper

    drainage leads to depletion of water resources,

    deterioration of water quality and loss of livelihood

    of the people

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    To delineate the land use changes for different

    periods using satellite imagery.

    To study the impact of urbanisation on groundwater quality and quantity.

    To assess the environmental changes which

    affects the livelihood of people throughquestionnaire survey.

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    Land use changes

    Jaiswal et. al, (1999) detected the change in

    land use mid-western part of Gohparu Block,Shahdol district, Madhya Pradesh. From visual analysis of satellite imagery and

    reconnaissance survey, major vegetation types and

    land cover classes were mapped. Analysed post-classification comparison techniques

    5

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    Hameed et. al, (2010) has assessed Evaluating

    Raw and Treated Water Quality of Tigris River within

    Baghdad by Index Analysis. The study monitored the groundwater quality.

    In this paper, the data considered from 2002 to 2008.

    Raw and treated water samples were collected and

    analysed for pH, Turbidity, TH, Ca, Mg, Cl, SO4, Iron

    Alkalinity, Dissolved solids, Ammonia, Fluoride and

    Aluminium.

    Water Quality Index (WQI) was calculated to find the

    suitability of water for drinking purpose. The WQI was

    calculated based on the Weightage factor and quality

    rating.

    6

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    Lenters (2001) studied the Long term Trends in

    the Seasonal Cycle of each of the Great Lakes,

    water levels from 1860 -1998. The study focused on the observations of L (monthly

    changes in water level) and addressed how the

    monthly changes in the Great Lakes water level varied

    over the period since 1860.

    The monthly changes were calculated as the difference

    of the monthly mean lake level of the current month

    and that of the following month. The monthly changes in water level L were calculated

    for all the months from the year 1860 -1998 and

    plotted against time

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    Mandere et. al, (2010) assess the livelihood

    change and household income in Nyahururu,

    Kenya. Assess the impact of the peri-urban development

    dynamics to household income.

    Identify and measures of household land use changes

    leading to declining significance of agriculture, adoption

    of new non-farm activities, and improvement livelihood

    and income

    They conducted the household survey and focus groupdiscussion with all communities.

    From the result, they see that there more than 10% of

    households connected in high income productivity.

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    Karapakkam

    District = Kancheepuram Taluk = Sholinganallur

    Coordinates = 1254'51.01"N latitude and

    8013'45.77"E longitude

    Area = 244.48ha Population = 7565 (Census of India, 2009)

    Government well = 1

    Panchayat well = 9

    Soil type = brown clayey soilNo Agricultural activities

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    Primary data Water level and water quality data for 2010-2011 Walk-through survey Focus Group Discussion Questionnaire Survey

    Secondary data Survey of India topomap No:66 D/1 and D/5

    Village map obtained from Karapakkam Panchayat

    office

    2002, 2004, 2006, 2008 and 2010 images aredownloaded from Google earth

    Previous year well data collected from Central

    Groundwater Board.

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    Study area visit

    Survey of India toposheet No: 66D/1 and D/5

    Study areadelineation

    Village map

    Water level

    fluctuation method

    GroundwaterQuality

    Groundwater

    Quantity

    Collection of well

    water Samples

    Questionnaire survey

    Analyses of Water

    Quality

    Parameters

    Focus Group

    Discussion

    Land use changes

    Groundwater

    Quality Index Map

    Image

    Measures forlivelihood changes13

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    14

    Geo referencing and

    create Base map

    Land use map change

    for different periods

    Geo referencing

    Delineate the land use

    changes

    Superimposing Map

    Village Map Image Field visit

    and mark

    control

    points for

    the current

    year

    Survey of India

    toposheet No: 66

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    Eleven observation wells was selected inKarapakkam village. Groundwater samples were collected during the

    month of September 2010, January, February

    and March 2011. Samples were analysed physical and chemicalparameters, such as pH, EC, TDS, Turbidity,CO3, HCO3, TH, Ca, Mg, Cl, Na, K, SO4 and NO3.

    Water quality index was calculated based onwater quality parameters.

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    16

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    The WQI is computed by adopting the followingformula, (Landwehr 1974)

    WQI =

    where,

    ai= the weight of the ith parameter,

    Ti= a function that transforms the measured value of ith

    parameter into a quality rating,Pi = measured value of i

    th parameter

    17

    =

    )(1

    ii

    n

    i

    i pTa

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    Water Quality Index Description

    0-25 Excellent

    26-50 Good

    51-75 Poor

    76-100 Very Poor

    >100 Unfit for drinking

    18

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    Water level was monitored from the observation well

    during the month of January, February and March

    2011. GPS was used to find the elevation of the well to

    calculate groundwater quantity. To study the changes in the water level the

    procedure followed by Lenters (2001)

    L = Lt+1 Lt

    Where,

    Lt - Monthly water level of the current month (m)

    Lt+1 - Monthly water level of the following month (m)

    19

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    Theissen polygon was created to find out theInfluence area of well (m2) Groundwater quantity is calculated by water level

    fluctuation method adopting the following formula,

    Q = A*L*SyWhere, Q = Volume of water (m3)

    A = Influence area of well (m2)

    L = Water level fluctuation (m)

    Sy = Specific yield of the well (6% for

    clayey soil according to Report of The Groundwater

    Resource Estimation Committee, 2009).

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    Focus Group Discussion and questionnaire survey

    was conducted to analyse the livelihood changes. In questionnaire survey around 53 people were

    surveyed. The questionnaire addresses the following aspects:

    Sources of domestic water including drinking water. Economic status of the people.

    About the groundwater quality and quantity conditions in the

    wells.

    Health problem in the area due to urbanisation, land use

    changes, deterioration of water quality, drainage facilities,

    etc.,

    Agricultural status.

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    Land use categories 2002 2004 2006 2008 2010

    Area (ha) Area (%) Area (ha) Area (%) Area (ha) Area (%) Area (ha) Area (%) Area (ha) Area (%)

    Agricultural land 93.24 38.14 80.47 32.92 74.39 30.43 19.10 7.81 0.00 0.00

    Aquifer recharge zone 24.59 10.06 24.59 10.06 24.59 10.06 24.59 10.06 24.59 10.06

    Fallow Land 12.15 4.97 13.64 5.58 16.56 6.78 70.24 28.73 87.99 35.99

    Buckingham canal 10.24 4.19 6.86 2.81 6.86 2.81 5.40 2.21 5.10 2.09

    Cemetery 1.85 0.76 1.85 0.76 1.85 0.76 1.85 0.76 1.85 0.76

    Collage 1.26 0.52 1.41 0.58 1.41 0.58 1.41 0.58 2.01 0.82

    Grass land 7.01 2.87 4.32 1.77 3.29 1.35 2.65 1.08 2.10 0.86

    Industries 11.72 4.80 14.22 5.82 14.46 5.91 20.50 8.38 25.22 10.31

    Pond 1.17 0.48 1.18 0.48 1.62 0.66 2.43 0.99 1.84 0.75

    Residential Area 11.03 4.51 12.82 5.24 15.42 6.31 18.58 7.60 25.52 10.44

    School 0.71 0.29 0.71 0.29 0.71 0.29 4.03 1.65 4.03 1.65

    Small industries 0.26 0.11 0.35 0.14 0.44 0.18 0.50 0.20 0.55 0.23

    Temple 0.74 0.30 0.77 0.31 0.82 0.33 0.86 0.35 0.92 0.38

    Total Area 244.48 244.48 244.48 244.48 244.4823

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    Land use Map -2002

    Land use Maps

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    Land use Map -2008Land use Map -2006

    Land use Maps

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    In 2002, Karapakkam villagehave 37% of agriculturalland.

    Due to urbanisation theseagricultural lands was turned

    into built-up area and fallowland.

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    Due to urbanisation the land value has increased. So

    the land owners was sold the land. Percentage of residential area increased due to

    urbanisation.

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    Groundwater quality parameters were analysedin the laboratory for four month.

    Bicarbonates, Nitrates Sulphates and Turbidity

    were found to be within the permissible limits. High concentration of Total Hardness was found

    in Rangasamy street, Indragandhi street and

    Near Okkium Maduvu.

    High concentration of Chloride was found NearOkkium Maduvu, Mahatma Gandhi Street and

    Sadagopan Street.

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    WQI was computed by Landwehr (1974) wasused for assessing the suitability of groundwater

    for drinking purposes.

    The estimated quantitative values of water quality

    parameters and their standards are used to

    calculate water quality index.

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    Parameters BIS Standards Weighting factor (ai)

    pH 8.5 0.24

    TDS (mg/l) 500 0.0041

    Turbidity (NTU) 50 0.41

    HCO3 (mg/l) 500 0.0041

    Ca (mg/l) 75 0.027

    Mg (mg/l) 30 0.0681

    Cl (mg/l) 250 0.0082

    Na (mg/l) 200 0.0102

    K (mg/l) 20 0.102

    SO4 (mg/l) 250 0.0082

    NO3 (mg/l) 45 0.045

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    ID Name Latitude andLongitude

    WQI (Sep) WQ RatingWQI (Jan) WQRating

    WQI (Feb) WQRating

    WQI (Mar) WQ Rating

    Well 1 Renganathanstreet 12 55' 14.74"N,80 13' 51.09"E 95.8 Very poor 61.84 Poor 113 Unfit for drinkingpurposes

    125 Unfit for drinkingpurposes

    Well 2 Near OkkiumMaduvu

    12 55' 7.07"N,80 14' 2.33"E

    141 Unfit for drinking

    purposes

    77.31 Very poor 112 Unfit for drinking

    purposes

    121 Unfit for drinking

    purposes

    Well 3 Indragandhistreet

    12 55' 1.01"N,80 13' 55.37"E

    63.6 Poor 42.73 Poor 93.3 Very Poor 99.8 Very Poor

    Well 4 Kupusamy street 12 54' 54.04"N,

    80 14' 2.15"E

    62.9 Poor 56.3 Poor 66.8 Poor 69.6 Poor

    Well 5 Kalaimagalnagar

    12 54' 48.69"N,80 14' 4.60"E

    54.7 Poor 42.4 Good 49.4 Good 56.8 Poor

    Well 6 Government well 12 54' 50.47"N,80 13' 55.19"E

    52.3 Poor 49.3 Good 58.8 Poor 62.3 Poor

    Well 7 Muthamil nagar 12 54' 54.05"N,80 13' 42.17"E

    100 Very poor 82.7 Very poor 93.78 Very Poor 101 Unfit for drinking

    purposes

    Well 8 Mahatma Gandhistreet

    12 54' 43.34"N,80 13' 48.06"E

    45.3 Good 32.4 Good 42.9 Good 56.2 Poor

    Well 9 Vendraai ammankovil steet

    12 54' 42.43"N,80 13' 56.11"E

    87.6 Very Poor 64.3 Poor 91.46 Very Poor 99.3 Very Poor

    Well 10 Rangasamystreet

    12 54' 41.55"N,80 14' 2.15"E

    73.5 Very Poor 62.6 Poor 71.8 Poor 76.8 Very Poor

    Well 11 Sadagopanstreet

    12 54' 37.63"N,80 13' 58.22"E

    49.8 Good 39.34 Good 43.1 Good 49.6 Good32

    Q S

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    Water Quality Index Map- September 2010

    Well 2 (Near Okkium Maduvu) water quality was unfit for drinking purpose.

    Well 3 (Indragandhi street), Well 4 (Kupusamy street), Well 5 (Kalaimagal nagar), Well 6(Government

    well), Well 8 (Mahatma Gandhi street) and Well 11 (Sadagopan street) water quality was good.

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    W t Q lit I d M J 2011

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    Water Quality Index Map- January 2011

    Well 2 (Near Okkium Maduvu) and Well 7 (Muthamil nagar) water quality was very poor.

    Well 3 (Indragandhi street), Well 5 (Kalaimagal nagar), Well 6(Government well), Well 8

    (Mahatma Gandhi street) and Well 11 (Sadagopan street) water quality was good.

    34

    W t Q lit I d M F b 2011

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    Water Quality Index Map- February 2011

    Well 1 (Renganathan street) and Well2 (Near Okkium Maduvu) water was not used

    for drinking purpose. Because the WQI value was >100.

    Well 5 (Kalaimagal nagar), Well 8 (Mahatma Gandhi street) and Well 11 (Sadagopan

    street) water quality was good. 35

    W t Q lit I d M M h 2011

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    Water Quality Index Map- March 2011

    Well 1 (Renganathan street), Well 2 (Near Okkium Maduvu) and Well 7 (Muthamil

    nagar) water was not used for drinking purpose. Because the WQI value was >100.

    Well 11 (Sadagopan street) water quality was good.

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    Description Well No Name

    Good Well 8 and Well 11 Mahatma Gandhi street andSadagopan street

    Poor Well 4, Well 5, Well

    6 and Well10

    Kupusamy street, Kalaimagal

    nagar, Government well andRangasamy street

    Very Poor Well 3, Well 7 andWell 9

    Indragandhi street, Muthamil nagarand Vendraai amman kovil steet

    Unfit for DrinkingPurpose

    Well 1 and Well 2 Renganathan street and NearOkkium Maduvu

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    Water level contour map was generated usingwell elevation data and GIS contouring methods. Groundwater flows was identified with the help

    of water level contour map.

    The groundwater movement was northwestdirection to southeast direction.

    Renganathan street, Okkium Maduvu,

    Indragandhi Street have high elevation and

    Rengasamy street has low elevation. Area of influence well was calculated by using

    Theissen polygon method.

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    Water level contour- January 2011

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    40

    Water level contour- February 2011

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    Water level contour- March 2011

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    42

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    Theissen Polygon Map

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    Well No Name Latitude and

    Longitude

    Area (m2) Change in Water Level (L)

    (m)

    Groundwater Potential (m3)

    Jan Feb Jan-Feb Feb-Mar

    Well 1 Renganathanstreet

    12 55' 14.74"N,80 13' 51.09"E

    290200 -0.75 -1.25 -13059 -21765

    Well 2 Near OkkiumMaduvu

    12 55' 7.07"N,80 14' 2.33"E

    512100 -0.7 -1.05 -21508 -32262

    Well 3 Indragandhi street 12 55' 1.01"N,80 13' 55.37"E

    128700 -0.6 -0.75 -4633.2 -5792

    Well 4 Kupusamy street 12 54' 54.04"N,80 14' 2.15"E

    126600 -0.7 -1.15 -5317.2 -8735

    Well 5 Kalaimagal nagar 12 54' 48.69"N,80 14' 4.60"E

    589300 -1.1 -1.35 -38894 -47733

    Well 6 Government well 12 54' 50.47"N,80 13' 55.19"E

    81570 -1.2 -1.6 -5873 -7831

    Well 7 Muthamil nagar 12 54' 54.05"N,80 13' 42.17"E 213100 -1.1 -1.45 -14065 -18540

    Well 8 Mahatma Gandhistreet

    12 54' 43.34"N,80 13' 48.06"E

    125700 -0.9 -1.05 -6787.8 -7919

    Well 9 Vendraai ammankovil steet

    12 54' 42.43"N,80 13' 56.11"E

    48840 -0.8 -1.2 -2344.3 -3516

    Well 10 Rangasamy street 12 54' 41.55"N,80 14' 2.15"E

    275900 -1.3 -1.9 -21520 -31453

    Well 11 Sadagopan street 12 54' 37.63"N,80 13' 58.22"E

    43930 -0.9 -1.3 -2372.2 -3427

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    Sources of drinking water

    In 2002, 76% of the respondents were used well waterfor drinking purpose and it is reduced to 4% in 2010.

    Because of the groundwater quality deterioration.

    18% of the peoples are spend more than Rs

    200/month for using portable water. Sources of Drinking Water Amounts spend for Drinking Water

    46

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    From the questionnaire survey, the groundwaterquality data were collected on five differentcategories namely Excellent, Good, Moderate,

    Poor and Very Poor. The data were analysed in GIS software atspecially for all the observation well during 2002,2005 and 2010.

    Before 2005, mostly the well water was excellentand good. After 2005, the quality of the water gets too

    deteriorated.

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    Water Quality Map 2002

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    Water Quality Map - 2002

    Well 3 (Indragandhi street, Well 4 (Rangasamy street), Well 6(Government

    well), Well 8 (Mahatma Gandhi street), Well 10 (Kupusamy street), and Well 11

    (Sadagopan street) water quality was Excellent.

    Remaining well water quality was good. 48

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    Water Quality Map - 2005

    Well 3 (Indragandhi street, Well 4 (Rangasamy street), Well 5 (Kalaimagal

    nagar), Well 6(Government well), Well 8 (Mahatma Gandhi street) and Well 10

    (Kupusamy street) water quality was Good.

    Well 7 (Muthamil nagar) water quality was Poor. 49

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    Water Quality Map - 2010

    Well 6 (Government well), Well 10 (Kupusamy street), and Well 11

    (Sadagopan street) water quality was good.

    Well 1 (Renganathan street), Well 2 (Near Okkium Maduvu) and Well 7(Muthamil nagar) water quality was very poor. 50

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    The reason for the quality deterioration was

    extraction of more water, lack of improperdrainage system and natural geology.

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    In 2002, 42% of the people had own agricultural land,

    and 34% of the people were agricultural labourers. Now no agricultural practices.

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    69% of people have sanitation facility. Major problems faced by the people due to water

    stagnation such as health disease. 64% of people have health impact (cold, fever, allergy,

    psoriasis etc.,) due to groundwater quality degradation.

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    Out this 64%, 54% of residents are affected bycold, 33% of residents were affected by fever

    and 13% of residents were affected by skin

    disease such as allergy, psoriaris etc.,

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    Positive impacts of livelihood Negative impact of livelihood

    The landless agricultural labourer

    dependent on agriculture. Now they shifted

    to other jobs in the industries, construction

    works etc.

    Due to urbanisation agricultural lands was

    turned into industries and fallow land. The

    landless agricultural labourers dependent

    only agriculture.

    66% of people got the income 5000-

    10000(House keeping, constructionlabourer, Bottle company, Lathe works and

    catering).

    Some people manage and settle other

    jobs. 13% of the people were unemployedwith comparatively lower living standard.

    Petty shops and Hotels was developed. Groundwater quality and level also varied

    due to over extraction and improper

    drainage.

    People has a sense of awareness towards

    education, due to IT companies.

    High pollution.

    Awareness for saving groundwater, and

    improve the livelihood.

    Health problem.

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    As of now (2010) agricultural land was no movein Karapakkam village. Due to urbanisation the land value has

    increased.

    The demand for land has increased and all theagricultural lands are converted into urbandevelopment.

    Some lands were converted to fallow land due to

    shortage of irrigation water source. Younger generation is not interested in doing

    agriculture.

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    Earlier the village had appreciable groundwater

    potential and the quality of groundwater was goodfor domestic purposes.

    Water resources are declining day by day in termsof water level and also deteriorating in quality.

    In earlier, Okkium Maduvu and Renganathan streetwell was used drinking purpose. Now it was unfit fordrinking purposes, where the water quality indexwas found to be more than 100.

    The reasons attributed for the quality deteriorationwere over extraction and lack of improper drainagesystem.

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    Due to the groundwater quality deterioration,

    51% of people are using portable water fordrinking purpose and 18% of people spendmore than 200 rupees per month for buyingportable water.

    Due to urbanisation economic status of thevillage people has to be changed.

    21% of the people earned high income due to ITcompanies, petty shops and hotels.

    13% of the people livelihood was affected byurbanisation and no agricultural activities. Themonthly income they earn is below Rs.5000.

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    Urbanisation is a major challenge for water resources.

    Planned urbanisation gives positive impacts, butunplanned urbanisation creates more problems andcomplicates the situation, which in fact give morenegative impacts.

    Awareness must be created among the people about the

    urbanisation, over extraction of water and sanitation toconserve the water resources.

    It is learned that most of people doesnt have enoughknowledge about septic tank, disposal of sewage in waterbodies and their advantages.

    The people depends on agricultural labour are asking forsome other water source to encourage agriculture, but itseems to be impractical for the present scenario.

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    strategies of farming communities in hard rock areas of southern

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    System and groundwater quality mapping in Panvel Basin, Maharashtra,

    India, Environmental Geology, Vol.45, pp. 753761.

    Brahmabhatt V.S., Dalwadi G.B., Chhabra S.B., Ray S.S. and Dadhwal

    V.K. (2000), Land Use/Land Cover Change Mapping In Mahi Canal

    Command Area, Gujarat, Using Multi-temporal Satellite Data, Journal of

    the Indian Society of Remote Sensing, Vol. 28, No. 4, pp. 221-232.

    Delin G., Healy R., Lorenz D. and Nimmo J. (2007), Comparison of

    local- to regional-scale estimates of ground-water recharge in

    Minnesota, USA. Journal of Hydrology, Vol 334, No. 1-2, pp. 231- 249.

    60

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    GEC (2009), Report of the groundwater resource estimationcommittee, Ministry of water resources government of India, NewDelhi.

    Graniel C. E., Morris L. B. and Rivera J. J. (1999), Effects ofurbanization on groundwater resources of Merida, Yucatan, Mexico,Environmental Geology, Vol. 37, pp. 303-312.

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