av1, shashikala r. s. prajapati2.pdfleaching of road and dissolution by flood waters as reported by...

4
A bi sa ac K 1 D lo w pl or la su ti P th to w 2 S m fr on L an P pH w m m D A K Stud La 1,2 ICLES` Abstract: Pres iochemical oxy amples were co ccording to sea Keywords: De . Introduct Dewale Lake ocation of Pan with an area o lant and dom rganic conten ake reduces uitable for dom mely monitor hysico-chemi he quality of w o understand water body. . Material ampling was morning at 8.0 rom Feb 2009 ne litre bottl Location of lak nd 2A & 2B). arameters suc H value were water was me meter while ele meter, other DO,CO 2 ,chlori APHA(2005), Kodarkar(2006 Figure dy of P ake in MJ College of sent investigat ygen demand, ollected and ev asons. ewale Lake, Phy tion is situated nvel is 18.58 0 N of 12.17 sq. k mestic waste nt, thereby po water quality mestic purpos ring of the l cal parameter water. Thus, p the biotic and and Metho done from fou 00 am to 10 a 9 - Jan 2010. W le and broug ke and sampli ch as tempera measured dir easured by th ectrical condu r parameter ides were Trivedy 6). 1: Location o Internatio V Licens Physic n Panv Dr. An Arts, Science & tion is carried chemical oxyg valuated from ysico-chemical in Panvel. N latitude and km. Lake is li from surroun olluting the l y and hence ses as well as lake is neces rs of the lake present investi d abiotic fact od ur different si am during the Water sample ght to labora ing stations a ature, electrica ectly in the fie hermometer an uctivity by ele s such a analyzed a and Geo of Dewale Lak onal Journa ISSN Impac Volume 3 I sed Under Cre co-Che vel, Di nita S. Jadh & Commerce, P d out to study gen demand, ch February 2009 parameter, seas The geograp d 73.12 0 E long ittered by leav nding adds t lake. Pollutin the water i aquaculture. sary to acces e in order to igation will h tors influencin te of the lake period of one es were collec atory for ana are shown in ( al conductivit eld. Temperat nd pH by pe ctrical conduc s BOD, as described ol (1986) ke in Panvel. al of Scienc N (Online): 23 ct Factor (201 Issue 9, Sep www.ijsr.n eative Commo emica ist –Ra hav 1 , Shashik Plot No. 53, Sec the Physico-c hloride, alkalin 9 to January 2 sonal variation. phical gitude ves of to the ng the is not Thus, ss the know elp us ng the in the e year cted in alysis. (Fig 1 ty and ture in en pH ctivity COD, d in and 3. The col 1. W ma ce and Rese 19-7064 12): 3.358 ptember 20 net ons Attribution al Para aigad kala R. S. Pr ctor 9A, Vashi, chemical param nity, hardness, 2010. Variation . Figure 2: Figure 2: Result and e physic – c lected during Water appear aterials and par earch (IJSR 014 n CC BY ameter (Mah rajapati 2 Mumbai Unive meters liketem conductivity, s n in the values (A) Photograp (B) Sampling d Discussion chemicalparam Feb 2009 to red to be gree rticulate matte R) r of De arasht ersity, Navi Mu mperature, pH, salinity, turbidi s of the param ph showing D g stations of D n meters of lak Jan 2010 is p enish in colou er. ewale tra) umbai 400 706 dissolved oxy ity and CO 2. W eters was obse Dewale Lake Dewale Lake ke water sam presented in T ur with suspen ygen, Water erved mples Table nded Paper ID: SEP14256 768

Upload: others

Post on 02-Aug-2020

2 views

Category:

Documents


0 download

TRANSCRIPT

Page 1: av1, Shashikala R. S. Prajapati2.pdfleaching of road and dissolution by flood waters as reported by Reshma Bhalla et al. (2007). Figure 7: Histograms showing Alkalinity and Hardness

Abisaac

K 1 DlowplorlasutiPthtow 2 SmfronLan PpHwmmDAK

StudLa

1,2ICLES`

Abstract: Presiochemical oxyamples were coccording to sea

Keywords: De

. Introduct

Dewale Lake ocation of Pan

with an area olant and domrganic contenake reduces uitable for dommely monitorhysico-chemi

he quality of wo understand

water body.

. Material

ampling was morning at 8.0rom Feb 2009ne litre bottl

Location of laknd 2A & 2B).

arameters sucH value were

water was memeter while elemeter, otherDO,CO2,chloriAPHA(2005), Kodarkar(2006

Figure

dy of Pake in

MJ College of

sent investigatygen demand, ollected and evasons.

ewale Lake, Phy

tion

is situated nvel is 18.580Nof 12.17 sq. kmestic waste nt, thereby powater qualitymestic purposring of the lcal parameterwater. Thus, pthe biotic and

and Metho

done from fou00 am to 10 a9 - Jan 2010. Wle and brougke and sampli

ch as temperameasured dir

easured by thectrical condur parameterides were

Trivedy 6).

1: Location o

Internatio

V

Licens

Physicn Panv

Dr. An

Arts, Science &

tion is carriedchemical oxygvaluated from

ysico-chemical

in Panvel. N latitude and

km. Lake is lifrom surroun

olluting the ly and hence ses as well aslake is necesrs of the lakepresent investid abiotic fact

od

ur different siam during the Water sampleght to laboraing stations a

ature, electricaectly in the fie

hermometer anuctivity by eles such aanalyzed aand Geo

of Dewale Lak

onal JournaISSN

Impac

Volume 3 I

sed Under Cre

co-Chevel, Di

nita S. Jadh

& Commerce, P

d out to studygen demand, ch

February 2009

parameter, seas

The geograpd 73.120E longittered by leavnding adds tlake. Pollutin

the water i aquaculture.sary to accese in order toigation will htors influencin

te of the lakeperiod of one

es were collecatory for anaare shown in (

al conductiviteld. Temperatnd pH by pectrical conducs BOD,as describedol (1986)

ke in Panvel.

al of SciencN (Online): 23ct Factor (201

Issue 9, Sepwww.ijsr.n

eative Commo

emicaist –Ra

hav1, Shashik

 

Plot No. 53, Sec

the Physico-chloride, alkalin9 to January 2

sonal variation.

phical gitude ves of to the ng the is not Thus,

ss the know elp us ng the

in the e year

cted in alysis. (Fig 1

ty and ture in en pH ctivity COD, d in

and

3. Thecol1. Wma

ce and Rese19-7064

12): 3.358

ptember 20net ons Attribution

al Paraaigadkala R. S. Pr

ctor 9A, Vashi,

chemical paramnity, hardness,2010. Variation

.

Figure 2:

Figure 2:

Result and

e physic – clected duringWater appear

aterials and par

earch (IJSR

014

n CC BY

ameter(Mahrajapati2

Mumbai Unive

meters liketemconductivity, s

n in the values

(A) Photograp

(B) Sampling

d Discussion

chemicalparamFeb 2009 to

red to be greerticulate matte

R)

r of Dearasht

ersity, Navi Mu

mperature, pH, salinity, turbidis of the param

ph showing D

g stations of D

n

meters of lakJan 2010 is p

enish in colouer.

ewaletra)

umbai 400 706

dissolved oxyity and CO2. Weters was obse

Dewale Lake

Dewale Lake

ke water sampresented in Tur with suspen

ygen, Water erved

mples Table nded

Paper ID: SEP14256 768

Page 2: av1, Shashikala R. S. Prajapati2.pdfleaching of road and dissolution by flood waters as reported by Reshma Bhalla et al. (2007). Figure 7: Histograms showing Alkalinity and Hardness

International Journal of Science and Research (IJSR) ISSN (Online): 2319-7064

Impact Factor (2012): 3.358

Volume 3 Issue 9, September 2014 www.ijsr.net

Licensed Under Creative Commons Attribution CC BY

Table 1: Seasonal variation of Physico – chemical parameters in Dewale Lake during Feb. 2009 to Jan. 2010.

Parameters Pre -

monsoon Monsoon

Post – monsoon

Temp 31.4 28.9  27.3 Chloride 23.04  15.95  21.72

pH 7.7  7.5  7.57BOD 7.29  9.02  11.07DO 5.21 7.35 8.82 CO2 7.5 4.5 8.2

Conductivity 0.835 0.427 0.472 Salinity 0.57 0.43 0.23

Turbidity 1.9 2.86 1.47 Alkalinity 186 161.4 229.4 Hardness 107.1 187.5 106.2

COD 36.2 46.37 68.78 Acidity 328.2 179.6 258.2 Silicates 176.59 348.43 604.13

Temperature -Maximum temperature was observed in

the pre - monsoon and minimum in post – monsoon (Table 1; Fig.3). These observations are in agreement with (Kumar et. al. 2006; Gayathriet. al. 2013; Balakrishna et. al. 2013;Shiddamallayya and Pratima 2011). Decrease or increase in water temperature is attributed to the climatic conditions, water environment such as turbidity and humidity. The change in water temperature is caused due to change in the atmospheric temperature with change in the seasons (Agarwal and Rajwar, 2010). The moderate temperature during monsoon season may be due to cooling effect of the water mass that entered the lake after heavy monsoon rains during this period (Chattopadhyay and Banerjee, 2007). Temperature influences the bacterial growth, responsible for the decomposition of organic matter for nutrient recycling,(Mohamed and Korium, 2009).

Chloride - In the present investigation the maximum level was observed during the pre-monsoon, (Table 1; Fig 3). High level during the pre - monsoon may be due to high content of chloride left behind by evaporation which also indicates pollution of animal origin, (Shashikala, 2007; Mohamed and Korium, 2009; Patil and Auti, 2005). Low level during monsoon may be due to mixing of the rain water. (Patra, and et al., 2010), the tolerance limit of chloride is 250mg/l(BIS) the lake water is fairly within the permissible limit.

Figure 3: Histograms showing temperature and chloride

content of the lake.

pH–It is the measure of the intensity of acidity or alkalinity and measures the hydrogen ion concentration in water. Most of the plant and animal species can survive a narrow range of pH from slightly acidic to alkaline. So, pH is important for biotic compound. In the present study pH range was recorded between 7.5 to 7.7. Maximum pH was observed during pre - monsoon and minimum during monsoon. Similar observation were made by (Helen et al., 2008; Koshy and Nair,2000; Pejavar, 2002; Shashikala, 2007; Mohamedand Korium, 2009; Patra et al.,2010) (Table 1; Fig 4 ). Suitable pH for most aquatic organisms ranges from 6.5-8.5which is the prescribed limit given by BIS 1983 and National River Water Quality standard. Rise in pH can be correlated with increase in temperature. High pH indicates higher productivity. Thus, we can say that water is not polluted with respect to hydrogen ion concentration.

BOD–It is the quantity of oxygen required for the metabolic activities of microorganisms for the degradation of organic matter present in water.Higher values are observed in post monsoon indicating higher rate of organic decomposition and favourable condition for microbial activity. (Patra et al., 2010; Nayak et al., 2004; Nayak and Behera, 2004).Minimum BOD value in pre monsoon (Table 1; Fig 4), may be the caused due to decrease in the level of water and increase in zoo planktons and phytoplanktons (Mishra and Patel, 2007)

Figure 4: Histograms showing pH and BOD content of the

lake. DO– It is one of the most important parameter in the

analysis of water and reflects the physical and biological process prevailing in water.D.O. is required by plants and animals for respiration. D.O. shows inverse relation with temperature. It is the indicator for organic pollutant. Minimum values observed during pre-monsoon (Table 1;Fig 5) are in agreement with those made by (George and Koshy, 2008; Koshy and Nair,2000; Radhika et al., 2004; Sharma and Walia, 2014),low level of O2 during pre - monsoon may be due to utility of O2 by bacteria and other animal as well as decomposition of organic matter (Mohamedand Korium, 2009; Patil and Auti, 2005; Meshram, 2005;Patra et al.,2010). High values in the post monsoon may be due to the increase in the photosynthetic activity.

CO2 – Free CO2 in water may be produced due to decomposition of organic matter and respiratory activities of aquatic organisms. High values in post monsoon (Table

Paper ID: SEP14256 769

Page 3: av1, Shashikala R. S. Prajapati2.pdfleaching of road and dissolution by flood waters as reported by Reshma Bhalla et al. (2007). Figure 7: Histograms showing Alkalinity and Hardness

International Journal of Science and Research (IJSR) ISSN (Online): 2319-7064

Impact Factor (2012): 3.358

Volume 3 Issue 9, September 2014 www.ijsr.net

Licensed Under Creative Commons Attribution CC BY

1, Figure 5)may be due to process of anaerobic digestion of dead aquatic plant and fluctuation in the DO.

Figure 5: Histograms showing DO and CO2 content of the

lake

Conductivity - Electrical conductivity of water indicates pollution. In the present study the EC values were maximum in pre monsoon and minimum in the monsoon (Table 1; Fig 6) (Mohamedand Korium, 2009). The high value may be due to bathing, domestic waste sewage, low level of conductance may be due to dilution of salts by rain water (George and Koshy, 2008; Koshy and Nair, 2000, Helen et al., 2008).

Salinity–The salinity act as a limiting factor in the distribution of living organisms and its variation is caused by dilution and evaporation and influence the distribution of fauna(Gibson 1982).High values were observed during the pre-monsoon, and lowest in the post monsoon (Table 1; Fig 6). Salinity higher in the pre monsoon may be due to evaporation leaving high content of chloride. It can be correlated with conductance, as chlorides increase electric conductance increases.

Turbidity - Values were maximum during monsoon and minimum in post monsoon (Table 1;Fig6) Higher values in monsoon may be due to the addition of the influx of run off during the monsoon (Shashikala, 2007; Patil and Auti, 2005: Sahib, 2004 ).

Figure 6: Histograms showing Conductivity, Salinity and

Turbidity content of the lake.

Alkalinity– Alkalinity is a measure of the buffering capacity of a solution or the capacity of bases to neutralize acids without an increase in pH. Alkalinity is due to carbonate (CO3

2-), bicarbonate (HCO3-) and hydroxides. Maximum values were observed in post monsoon and minimum in monsoon (Table 1, Fig 7). This is in accordance with the Roy et al. (2010).

Hardness–Hardness is used as an indicator of water quality which depends on the concentration of carbonates and bicarbonates, salts of calcium and magnesium or sulphate chloride or other anions. It is found to be highest in the monsoon, (Table 1; Fig 7).The result showed that water of the lake is hard (Thorat,2000; Patil and Auti,2005). Increase in hardness of water may be due to leaching of road and dissolution by flood waters as reported by Reshma Bhalla et al. (2007).

Figure 7: Histograms showing Alkalinity and Hardness

content of the lake

COD–It is a method to determine the organic load of water body i.e. susceptibility to oxidation. It is maximum in post – monsoon and minimum in pre – monsoon (Table 1, figure 8). Enhanced level of COD may be due chemical pollutants(Patra and et al., 2010).

Acidity–It is higher in pre – monsoon and lower in monsoon. Higher level may be due to low level of water and lower due to dilution of water by rain (Table 1; Fig 8).

Silicates–Maximum in post – monsoon may be attributed to the increased level of organic decomposition which adds silica to water body (Table 1; Fig 8).

Figure 8: Histograms showing COD, Acidity and Silicates

content of the lake

Paper ID: SEP14256 770

Page 4: av1, Shashikala R. S. Prajapati2.pdfleaching of road and dissolution by flood waters as reported by Reshma Bhalla et al. (2007). Figure 7: Histograms showing Alkalinity and Hardness

R

[1

[2

[3

[4

[5

[6

[7

[8

[9

[1

[1

[1

[1[1

[1

[1

[1

[1

References

1] APHA, Sand wast3710 (200

2] R. K. TrMethods (1986).

3] Kodarkar(2006).

4] S. GayathImpact PhytoplanBangalor

5] D. BalakrChemicalGhanpur Issue 1: 4

6] N. Shiddin PhytoBidar, KCharacterDevelopm

7] A. K. Agand MicrGarhwal Science, 6

8] C. Chattchanges iof net phy31, 287-2

9] L. B. ShNaldurg Marathw

10] MohamedPhysicochLake NasResearch

11] S. S. PzooplankBioinfole

12] A. P. PatSwain, ParameteMouth neFish and

13] BIS, Bure14] M. H. H

impact ocharacter390 (2008

15] M. KoshPamba at(2000).

16] M. PejaAmbegos(2002).

17] B. K. NaS.K. AchLake, Or(2004).

18] L. Nayakphysico

Standard methewater. 21st E05). rivedy, P. K. of Water Poll

r, Methodolog

hri, N. Lathaof Physico

nkton Divere. JAIR Vol. 2rishna, T. R. Rl Parameters

Lake, Wara44-48, (2013).damallaya andoplankton CoKarnataka Aristics of Wment research,garwal and Grobiological S

Himalaya, 6(6), 65-71 (2topadhyay anin environmenytoplankton in

296 (2007). hashikala, Hy

district Osmada Universitd, A.F. Themical Charsser Water.G

h,3 (3): 141-14Patil, R.G.

kton from Sat., 2(2) : 81-5 tra, J.K. PatraSeasonal V

ers of Chilikaear GabakundaMarine Scieneau of Indian

Helen, S. Premof a Sewageistics of Poov8).

hy, V. Nair, t Kozhencher

avar, Physicsale Thane. In

ayak, B.C. Acharya, Variatirissa. Indian

k, D.P. Behechemical par

Internatio

V

Licens

ods for the exEdition. Wash

Geol, Chemilution Studies

gy for water A

a and M. Ram-chemical Crsity of N2 Issue 6: 349Reddy and D.s and Plankangal, A.P. In

d M. Pratima, ommunity in

Along With Water. Journa

, 2(2), 186-19G. S. Rajwar,Study of Teh

India. Jour2010). nd T. C. Bntal charactern a freshwater

ydrobiology smanabad (M.ty (2007). Toufeek, Mracteristics oflobal Journal

48. (2009). Auti, Seaso

alim Ali lak(2005).

a, N.K. MahapVariation in a Lake after a, Orissa, Indi

nces., 2(2): 109Standard, (19mjith, D.S Jae discharge

var estuary. Po

Water qualitrry. Poll Res

co-chemical ndia. J. Ecogi

charya, U.C. Pion of water

J. Mar, Sc

era, Seasonal rameters of t

onal JournaISSN

Impac

Volume 3 I

sed Under Cre

xamination ofington, DC 2

ical and Biolo. Env. Publ K

Analysis 3rd e

machandra MCharacteristicsNalligudda9-352, (2013). Samatha, Phy

kton Diversitndia. IJZR V

Seasonal Chn Pappnash

Physico-Chel of Advanc

90 (2011). Physico-Che

hri Dam Resernal of Ame

anerjee, Temristics and divr lake. Turk J

study of BoriS) INDIA T

M. A. Kof Water Quall of Environm

onal variatioke at Aurang

patra, S. Das,Physicoche

Opening ofia World Jour9-117, (2010)

992). aya, Studies o

on the sedoll Res., 27(3)

ty aspects of., 19 (4): 66

studies ofiol., 14(4): 27

Panda, B.B. Nquality in C

i., 33(2): 16

variation ofthe Chilika la

al of SciencN (Online): 23ct Factor (201

Issue 9, Sepwww.ijsr.n

eative Commo

waste 20001-

ogical Karad.,

edition

Mohan, s on Lake, ysico-ty of

Vol. 3

hanges Pond,

emical ces in

emical ervoir, erican

mporal versity J. Bot.,

i tank Thesis

orium, lity in mental

on of gabad,

, G.C. emical f New rnal of ).

on the diment : 387-

f river 65-668

lake 77-281

Nayak, Chilika 64-169

some agoon

[19

[20

[21

[22

[23

[24

[25

[26

[27

 

Au

AssComa ch

ce and Rese19-7064

12): 3.358

ptember 20net ons Attribution

(east coastSipakuda. I

9] P.C. Mishraround anProtection,

0] A.V. GeorSasthamko(2008).

1] Radhika, Cparameterslake-Trivan(2004).

2] V. Sharmausing physLake H. P.(2014).

3] C.B. MeshpollutionEnviron M

4] R. N. Gibintertidal f363-414 (1

5] S. Sahib, HRiver. Kera

6] U. Roy, BFazlul, andand SeasonPond, Ban(2010).

7] S. R. ThoAurangbad

uthor Profi

Dr. (Mdegreand from

sociate Professommerce at Vashhairperson for T

earch (IJSR

014

n CC BY

of India) afteIndian J. Marra, R.K. Patel,

industrial ci, 2(27): 114-1rge, M. Kos

otta lake of Ke

C. I. Mini, T. Gs of a tropicandrum, Keral

a and Y. K. Wsico-chemical (India). Asia

hram, Zooplanof lake Wa

Monit.,15(1): 55bson, Recent

fishes. Oceano982).

Hydrology andala J.Envir,Bi

B. K. Shaha, Kd M. D. S. Gnal Variation

ngladesh. Mar

orat, Pollutiod (M.S) Poll R

ile

Mrs.) Anita S.ees in Zoology 1987 respectivMumbai Univ

or in ICLES` hi, Navi MumbT. Y. B. Sc. Pra

R)

er opening ther. Sc., 33(2): 2, Status of waity a case stu24 (2007). hy, Water qerala. Poll Res

Ganga Devi, Sal fresh watela. Poll. Res

Walia, Analysi parameters

an J. of Basic

nkton biodiveradali Amarva5-59 (2005). t studies on ogr. Mar. Bio

d phytoplankto., 10(6) :185K. H. Mazhab

Golam, Study n of Zooplanrine. Res. Aq

on status of Res., 19 (2):30

. Jadhav receivfrom Mumbai

vely. She receversity in 1994.MJ College of

bai since 1989 aactical examinat

e new mouth,206-208 (2004ater quality inudy. Ind. J. E

quality studiess., 27(3): 419-

Studies on abier lake Vellas., 23 (1): 49

s of water quof Govind SSci. 2(3) : 83

rsity in relatioati. J. Ectox

the biologyol. Ann. Rev.,

ton in the Kal-188 (2004).buddin, M. Don the Diver

kton in a Brqua., 1(1), 30

Salim Ali7-309, (2000)

ved B.Sc. and MUniversity in

eived Ph.D. de. She is workinf Arts, Scienceand also workintion.

near 4).

and Env.

s of -424

iotic ayani 9-69

ality agar

3-91,

on to xicol

y of , 20,

llada

D. H. rsity rood 0-37

lake ).

M.Sc. 1985 egree ng as e and ng as

Paper ID: SEP14256 771