Irrigation Water Quality.pdf

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PROJECT REPORT ON ASSESSMENT OF IRRIGATION WATER QUALITY OF GHAGGAR RIVER SUBMITTED TO SUBMITTED BY DR. SIBY JOHN ABHISHEK KOUL PROFESSOR 13201001 ENVIRONMENTAL ENGG M.E ENVIRONMENTAL ENGG

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Suitability of Ghaggar river water for irrigation purposes.

Transcript of Irrigation Water Quality.pdf

  • PROJECT REPORT

    ON

    ASSESSMENT OF IRRIGATION WATER

    QUALITY OF GHAGGAR RIVER

    SUBMITTED TO SUBMITTED BY

    DR. SIBY JOHN ABHISHEK KOUL

    PROFESSOR 13201001

    ENVIRONMENTAL ENGG M.E ENVIRONMENTAL ENGG

  • 1

    1. Introduction

    India is rich in water resources being endowed with a network of rivers that can

    meet a variety of water requirements of the country. However, with the rapid

    increase in the population of the country and the need to meet the increasing

    demands of irrigation, human and industrial consumption, the available water

    resources are getting depleted and the water quality has deteriorated. Indian rivers

    are polluted due to the discharge of untreated sewage and industrial effluents. It can

    be said that no water is pure or clean owing to the presence of some quantities of

    gases, minerals and life. However, for all practical purposes, pure water is considered

    to be that which has low dissolved or suspended solids and obnoxious gases as well

    as low in biological life. Such high quality of water may be required only for drinking

    purposes while for other uses like agriculture and industry, the quality of water can

    be quite flexible and water polluted up to certain extent in general sense can be

    regarded as pure.

    Agriculture is a major sector in the economic development of India, as it is the source

    of livelihood for majority of population. The Ghaggar, a major river of Haryana

    originates from the Siwalik Hills of Himachal Pradesh and Haryana. During its journey,

    a number of streams, streamlets, drains and tributaries debouch their load into the

    Ghaggar. The river has a total stretch of about 291 km with a catchment area of

    42,200 sq. km.

    For the purpose of assessment of suitability of water for the irrigation purposes,

    different properties were considered in accordance with IS: 11624-1986 (Guidelines

    for the Quality of Irrigation Water).

  • 2

    2. Methodology

    For analysis, water samples were collected from two locations near Sector 25 and 26,

    Panchkula. At the time of sampling, the containers were thoroughly rinsed two to

    three times with water to be sampled. Then the samples were collected by dipping

    the containers in the flowing water.

    The parameters which are to be assessed are Sodium Adsorption Ratio, Residual

    Sodium carbonate and Electrical Conductivity.

    Sodium Adsorption Ratio

    Excess sodium in waters produces the undesirable effects of changing soil properties

    and reducing soil permeability. Hence the assessment of sodium concentration is

    necessary while considering the suitability for irrigation. The degree to which

    irrigation water tends to enter into cation-exchange reactions in soil can be indicated

    by the sodium adsorption ratio. Sodium replacing adsorbed calcium and magnesium

    is a hazard as it causes damage to the soil structure. It becomes compact and

    impervious. SAR is an important parameter for the determination of suitability of

    irrigation water because it is responsible for the sodium hazard. The waters were

    classified in relation to irrigation based in the ranges of SAR values.

    It is calculated from following formula:

    = Na

    Ca +Mg2

    Where SAR = Sodium Adsorption Ratio

    Na+ = Sodium ion concentration, meq/l

    Ca2+

    = Calcium ion concentration, meq/l

    Mg2+

    = Magnesium ion concentration, meq/l

    In relation to hazardous effects of SAR, the irrigation water quality rating is given as

    S.No Class SAR Range

    1. Excellent Below 10

    2. Very Good 10-18

    3. Good 18-26

    4. Poor Above 26

  • 3

    Residual Sodium Carbonate

    Residual sodium carbonate (RSC) of irrigation water is used to indicate the alkalinity

    hazard of soil. The concentration of bicarbonate and carbonate also influences the

    suitability of water for irrigation purpose. One of the empirical approaches is based

    on the assumption that all Ca2+

    and Mg2+

    precipitate as carbonate. The water with

    high RSC has high pH and land irrigated with such water becomes infertile owing to

    deposition of sodium carbonate; as known from black colour of the soil.

    RSC is determined by the equation:

    RSC = (CO32-

    + HCO3-) (Ca

    2+ + Mg

    2+)

    Where RSC = Residual Sodium Carbonate, meq/l

    CO32-

    = Sodium ion concentration, meq/l

    HCO3- = Calcium ion concentration, meq/l

    Ca2+

    = Calcium ion concentration, meq/l

    Mg2+

    = Magnesium ion concentration, meq/l

    In relation to hazardous effects of RSC, the irrigation water quality rating is given as

    S.No Class RSC Range

    1. Excellent Below 1.5

    2. Very Good 1.5-3.0

    3. Good 3.0-6.0

    4. Poor Above 6.0

    Electrical Conductivity

    The most influential water quality guideline on crop productivity is the water salinity

    hazard as measured by electrical conductivity (EC). The primary effect of high EC

    water on crop productivity is the inability of the plant to compete with ions in the soil

    solution for water (physiological drought). The higher the EC, the less water is

    available to plants, even though the soil may appear wet. Because plants can only

    transpire "pure" water, usable plant water in the soil solution decreases dramatically

    as EC increases.

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    In relation to hazardous effects of EC, the irrigation water quality rating is given as

    S.No Class EC Range

    1. Excellent Below 1500

    2. Very Good 1500-3000

    3. Good 3000-6000

    4. Poor Above 6000

  • 5

    3. Experiment Performed

    While performing experiment, following parameters were calculated

    Ca2+

    concentration

    For detection of Ca2+

    , EDTA titrimetric method was used. 50 ml sample was taken

    and titrated with standard EDTA solution (0.01M). NaOH was added to produce a

    pH of 12 to 13 and Murexide was used as indicator. Titration is stopped when

    there is color change.

    Calculation:

    mgCa/L = AXBX400.8mlsample

    Calcium hardness as mg CaCO3/L = AXBX1000mlsample

    Where A= ml titrant for sample

    B = mg CaCO3 equivalent to 1 mL EDTA titrant

    Mg2+

    concentration

    It can be detected by calculation method as

    mg Mg/L = {Total hardness (as mg CaCO3/L)

    calcium hardness (as mg CaCO3/L)} X 0.243

    Total hardness of the sample is calculated by titrating it with standard EDTA

    solution, using Erichrome Black T as indicator and Ammonia buffer to bring pH to

    11.0.

    Total hardness as mg CaCO3/L = AXBX1000mlsample

    Where A= ml titrant for sample

    B = mg CaCO3 equivalent to 1 mL EDTA titrant

  • 6

    CO32-

    and HCO3- concentration

    Standard procedure for measurement of Alkalinity is used for measurement of

    CO32-

    and HCO32-

    concentration. N/50 sulphuric acid is used as titrant.

    Phenolphthalein and Methyl Orange are used as indicators. First add 3-4 drops of

    phenolphthalein to sample. If no color appears, phenolphthalein alkalinity is

    absent. If color changes to pink, titrate it till it disappears. Record the ml used (as

    P).

    Add one drop of Methyl Orange to titrated mixture and retitrate it until color

    changes from yellow to orangish-red. Record the ml used (as T).

    Phenolphthalein alkalinity

    = P X 1000

    ml sample

    Total alkalinity

    = T X 1000

    ml sample

    If P=0, total alkalinity due to bicarbonates

    If P

  • 7

    Calculations

    Alkalinity

    Phenolphthalein alkalinity was absent, therefore total alkalinity is due to

    bicarbonates only.

    Location Total Alkalinity (mean) HCO3- (mg/L) HCO3

    - (meq/L)

    1. 147.3 147.3 2.41

    2. 151.0 151 2.47

    Total hardness

    Location Total hardness (mean) as mg CaCO3/L

    1. 198

    2. 199.3

    Ca2+

    concentration

    Location mg Ca/L As mg CaCO3/L meq Ca/L

    1. 43.0 107.3 2.15

    2. 43.2 108.0 2.16

    Mg2+

    concentration

    Location mg Mg/L meq Mg/L

    1. 43.0 2.15

    2. 43.2 2.16

    Na+ concentration

    Na+ concentration value is taken from previous studies. It is 76.3 mg/L, which

    is equivalent to 3.3 meq/L.

  • 8

    EC value

    Since conductivity meter was not available, the EC value is taken from

    previous studies and is 807.52 mhos/cm.

    Sodium Adsorption Ratio

    Location SAR

    1. 2.3

    2. 2.3

    Residual Sodium Carbonate

    Location RSC

    1. -1.57

    2. -1.56

    4. Results

    From calculations it is observed that the SAR value is 2.3, which shows that

    the water is excellent for irrigation purposes.

    The value of RSC is -1.56, which also indicates that water is excellent for

    irrigation purposes.

    The value of EC as taken from previous studies is 807.52, which is excellent

    Hence, the overall quality of water is excellent and should be used for

    irrigation purposes.

  • 9

    References

    1. IS: 11624-1986, Guidelines for the Quality of Irrigation Water

    2. Standard Methods for Water and Wastewater treatment

    3. Kundu Sukhdev, Assessment of Surface Water Quality for Drinking and

    Irrigation Purposes: A Case Study of Ghaggar River System Surface Waters,

    Bulletin of Environment, Pharmacology & Life Sciences Volume 1, Issue 2,

    January 2012

    4. Joshi, D.M., Kumar Alok, Agrawal Namita, Assessment of the irrigation water

    quality of river Ganga in haridwar district, Rasayan J.Chem, Vol 2,No 2 (2009).

  • List of Contents

    Topic Page No.

    1. Introduction .........................................................................1

    2. Methodology...................................................................2

    3. Experiment Performed....................................5

    4. Results.............................................................................8

    References............................................................................9