Comparison of various properties of water
sample collected from different lakes of
Bhopal
A
Dissertation Work
Submitted as Major Project-I in Partial fulfillment for the award of Graduate
Degree in Bachelor of Technology in Civil Engineering
Submitted to
RAJIV GANDHI PROUDYOGIKI VISHWAVIDYALAYA
BHOPAL (M.P)
Submitted By
ABHISHEK RAJ (0191CE223D01)
ADITYA SINGH (0191CE223D01)
Under the Guidance of
Prof- HARISH NEMA
(Department of Civil Engineering)
Session: 2022-25
Department of Civil Engineering
Technocrats Institute of Technology-(EXCELLENCE), Bhopal
TECHNOCRATS INSTITUTE OF TECHNOLOGY
EXCELLENCE BHOPAL
Approved by AICTE New Delhi & Govt. of Madhya Pradesh and Affiliated to Rajiv Gandhi
Proudyogiki Vishwavidyalaya, Bhopal, Anand Nagar, Post Piplani BHEL, Bhopal-462021 (M.P.)
Department of Civil Engineering
CERTIFICATE
This is to certify that the project entitled Comparison of various properties
of water sample collected from different lakes of Bhopal being submitted
by ABHISHEK RAJ & ADITYA SINGH student of seventh Semester,
Degree in Civil Engineering has done their work as Major Project-I for
Partial fulfillment of the degree from RGPV, Bhopal (M.P.) is a record of
bonafide work out by him under our supervision.
Prof. Harish Nema Prof. -Dr Ravindra Gautam
Guide Head
Department of Department of
Civil Engineering Civil Engineering
TECHNOCRATS INSTITUTE OF TECHNOLOGY-
EXCELLENCE, BHOPAL
Approved by AICTE New Delhi & Govt. of Madhya Pradesh and Affiliated to Rajiv Gandhi
Proudyogiki Vishwavidyalaya, Bhopal, Anand Nagar, Post Piplani BHEL, Bhopal-462021 (M.P.)
Department of Civil Engineering
ACKNOWLEDGEMENT
I take the opportunity to express my cordial gratitude and deep sense of
indebtedness to my guide Prof. Harish Nema for the valuable guidance and
inspiration throughout the project duration. I feel thankful to him for his innovative
ideas, which led to successful completion of this project work. I feel proud and
fortune to work under such an outstanding mentor in the field of Comparison of
various properties of water sample collected from different lakes of
Bhopal . He has always welcomed my problem and helped me to clear my doubt. I
will always be grateful to him for providing me moral support and sufficient time.
I owe sincere thanks to Dr. Ravindra Gautam, Director, TIT-, who helped
me duly in time during my project work in the Department.
I would also thank to my Institution, faculty members and staff without whom
this project would have been a distant reality. I also extend my heartfelt thanks to my
family and well wishers.
STUDENT NAME-ABHISHEK RAJ; ADITYA SINGH
Roll number - 0191CE223D01 ,0191CE223D02
TECHNOCRATS INSTITUTE OF TECHNOLOGY (EX),
BHOPAL
Approved by AICTE New Delhi & Govt. of Madhya Pradesh and Affiliated to Rajiv Gandhi
Proudyogiki Vishwavidyalaya, Bhopal, Anand Nagar, Post Piplani BHEL, Bhopal-462021 (M.P.)
Department of Civil Engineering
APPROVAL CERTIFICATE
This is to certify that the project entitled “Comparison of various properties of
water sample collected from different lakes of Bhopal” being
submitted by “ABHISHEK RAJ”, ADITYA SINGH student of Seventh Semester,
Degree in Civil Engineering have done their work as Major Project I for Partial
fulfillment of the degree from RGPV, Bhopal (M.P.).
Guide Name –
Harish Nema
ABSTRACT
Water is an important component of life of every living being. Aquatic
environment is considered as important factor affecting health of flora and
fauna. In the present study, the physico-chemical analysis of water of five
different water bodies of Bhopal region viz. Upper Lake, Lower Lake,
Sarangpani Lake, Shahpura Lake and Kolar Lake was done to determine the
suitability of water. The parameters analyzed were Temperature,
Conductivity, pH, Total Dissolved Solids (TDS), Turbidity, Dissolved
Oxygen, Hardness, Chloride content, free CO2 and Total Alkalinity. All
the parameters were ranged within the desirable limit accounting for
healthy status of water bodies of Bhopal region.
Water is an important component of life of every living being. Aquatic
environment is considered as important factor affecting health of flora and
fauna. In the present study, the physico-chemical analysis of water of five
different water bodies of Bhopal region viz. Upper Lake, Lower Lake,
Sarangpani Lake, Shahpura Lake and Kolar Lake was done to determine the
suitability of water. The parameters analyzed were Temperature,
Conductivity, pH, Total Dissolved Solids (TDS), Turbidity, Dissolved
Oxygen, Hardness, Chloride content, free CO2 and Total Alkalinity. All
the parameters were ranged within the desirable limit accounting for
healthy status of water bodies of Bhopal region.
This study assigned weights to different parameters based on their
importance to water quality and their potential to have detrimental
effects. The study found that Cd, Cr, Mn, and Pb had the highest weight,
while Co, Ni, and Zn had the lowest weight.
1. INTRODUCTION
The seasonal variations and Anthropogenic stresses such as introduction of
chemicals into Water domestic sewage, agriculture, urbanization etc in or near
the catchment area of water bodies often results in the decline of Physico-
chemical properties of the water and water quality on the whole (Khan et al.,
1988; Mohapatra and Singh 1999). The physico-chemical parameters of water
provide the present information about the solute concentration at a given time
(Singh and Shrivastava (2016). Imbalance in Physico-chemical properties of
the water may adversely affect many species of aquatic flora and fauna that
are dependent on both abiotic and biotic conditions (Santhosh and Singh,
2007). In India five water quality classes have been designated (A-E) on the
basis of the water quality requirements fo a particular use (UNECE 1993).
Class A waters recommended as drinking water source straight without
treatment but after disinfection. Class B waters categorize for outdoor
bathing. Class C waters considered as drinking water source with
conventional treatment followed by disinfection. Class D waters to
maintain aquatic life (i.e. propagation of wildlife and fisheries) and class
E waters for use for irrigation, industrial cooling and controlled waste
disposal.
Parameters of water quality of concern are traditionally Temperature,
turbidity, nutrients, hardness, alkalinity and dissolved oxygen are some of the
important parameter that play a significant role for the growth of biota or
living organisms in the water body (Chiaudani and Premazzi, 1988). The
deviation in the physicochemical properties of water unswervingly
influences the biotic communities and primary productivity of the water
bodies. Aquaculture contributes to economy in many developing countries
like India therefore, there is crucial need of monitoring the water quality to
maintain healthy aquatic ecosystem to ensure proper yield of cultures. For the
optimal performance, aquacultures including fishes need tolerable limits of
water parameters (Kiran, 2010). Planktons and other organism may be affected
by poor quality water causing impaired growth and death. Variables of
concern include nitrates, sulphates, total dissolved solids (salinity), a number
of metals and organic micropollutants such as pesticides. In addition,
bluegreen algae and pathogens in water can present problems. The lakeside
constructions in Bhopal affect water quality of Upper Lake (Khan and Ganaie,
2014). The quality of water in Lower Lake in Bhopal has also been
exaggerated than Upper Lake (Pani and Mishra 2000). The water quality of
Kolar Lake of Bhopal is reported to be relatively good (Shukla 1996).
The objective of the current study is to provide information on physico-
chemical analysis of water of five lakes of Bhopal i.e. Upper Lake, Lower
Lake, Sarangpani Lake, Shahpura Lake and Kolar Lake to assess the water
quality in order to confer its ecological suitability for aquatic flora, fauna and
human consumption. A study finds that freshwater fishes in these lakes have
remarkable proportion of Enterobacteriaceae and these bacteria constitute
a potential risk for fish population and public health (Borkar et al.,
2017). It is worth mentioning that upper lake and Kolar Lake are major
source of drinking water supply and considered as life line of Bhopal.
2. MATERIAL AND METHODS
2.1 Study Sites :-
Five fresh water lakes were selected for analysis of quality of water. All
these lakes are man-made and are located in different localities of
Bhopal. Upper Lake is situated at 23.25°N 77.34°E; this sampling site
receives domestic wastes. Lower Lake is located at 23°16′0″N and
77°25′0″E. This lake receives the waste from the temple including
polythene bags and the flowers and other solid waste at some point.
Sarangpani Lake is situated in BHEL area of Bhopal. The inflow of
sewage water over the years has resulted in deterioration of the water
quality of the lake. Shahpura Lake is one of the important lake of Bhopal
and its coordinates are 23°12'17"N and 77°25'35"E. The lake shows the
marshy vegetation growing at the bank of the lake along with drains
and pools that quantify pollution cost by municipal and industrial
waste. Kolar Lake is situated 29°14’N 79°10’E. This Lake is
comparatively less polluted and favorable destination for fishing.
2.2. Sample Collection :-
The samples were collected in uncontaminated sampling bottles of I
liter capacity. Monitoring was performed during June 2015 to May 2016.
For unsteady parameters such as temperature, electrical conductivity
(EC), pH, were measured at the sampling site. Samples were brought to
the laboratory for analysis of other physico-chemical parameters like
Conductivity, pH, Total Dissolved Solids (TDS), Turbidity, Dissolved
Oxygen, Hardness, Chloride content, free CO2 and Total Alkalinity.
2.3. Laboratory Methods :-
o Physical analysis was done for coloure and odour of water. Colour was
measured by visual comparison method. Odour was determined by
sniffing water manually. Temperature was measured with the
thermometer (Philips) by immersing it directly into the water body
sufficient time period to get constant reading.
Conductivity :- Conductance was measured by conductometer (215K,
Elite Scientific Co. India). The electrode of the conductivity meter is dipped
into the sample, and the readings are noted for stable value shown as ms/cm.
pH :- pH value of water sample was determined by pH meter (LT-PH57, Elite
Scientific Co. India) using standard buffer solutions.
Total Dissolved Solid (TDS) :- It was determined by evaporation method. A
known volume of the well-mixed sample (50ml) was measured into a
preweighed dish and evaporated to dryness at 103 0C on a steam bath. The
evaporated sample is dried in an oven for about an hour at 103-105 0C and
cooled in a desiccators and recorded for constant weight.
Turbidity: Turbidity was determined by Turbidity meter (CL 880, Accumax
India). The electrode was dipped into the sample, and the reading noted.
Dissolved Oxygen (DO): It was measured by dissolved oxygen meter (CL
930, Accumax India). The electrode was dipped into the sample, and the
reading noted. Total Hardness: The hardness of water body was determined by
titration. Exactly 50ml of the well-mixed sample is pipetted into a conical flask,
to which 1ml of ammonium buffer and 2-3 drops of Eriochrome black -T
indicator is added. The mixture is titrated against standard 0.01M EDTA until
the wine red colour of the solution turns pale blue at the end point. Chloride:
Chloride measured by Argentometric titration method with standard silver
nitrate using potassium chromate as an indicator. A known volume of filtered
sample (50ml) is taken in a conical flask, to which about 0.5ml of potassium
chromate indicator is added and titrated against standard silver nitrate till silver
dichromate (AgCrO4) starts precipitating. Free CO2: free CO2 was determined
by Coulometric Titration. 100 ml of water was acidified with HClO4 and
boiled vigorously for at least 15 min to remove dissolved CO2. Total
Alkalinity: Total alkalinity was determined with titration with standard H2 SO4
or HCI solution. Titration to pH 8.3 or decolourisation of phenolphthalein
indicator will indicate complete neutralization of OH- and 1/2 of CO2-3 ,
while to pH 4.5 or sharp change from yellow to orange of methyl orange
indicator will indicate total alkalinity.
Parameters for Comparison
1. Physical Parameters
pH : Indicates acidity or alkalinity.
Turbidity: Measures water clarity.
Temperature: Affects chemical reactions and aquatic life.
Color and Odor: Indicates contamination or organic matter.
2. Chemical Parameters
Dissolved Oxygen (DO): Essential for aquatic life; low levels indicate
pollution.
Biochemical Oxygen Demand (BOD): Indicates organic pollution.
Chemical Oxygen Demand (COD): Measures total pollution levels.
Nutrient Levels (Nitrates, Phosphates): High levels cause
eutrophication.
Heavy Metals (Lead, Mercury, Arsenic): Indicates industrial pollution.
Salinity and Conductivity: Reflect dissolved salt content.
3. Biological Parameters
Coliform Bacteria : Indicates contamination from sewage or waste.
Algal Bloom Presence: High nutrients can cause harmful algal growth.
4. Microbial Analysis
Pathogenic Microorganisms : Assess health risks.
Potential Lakes in Bhopal for Sampling
1. Upper Lake (Bhojtal)
- Largest lake in Madhya Pradesh, primarily used for drinking water.
2. Lower Lake
- Adjacent to Upper Lake, known for recreational activities.
3. Shahpura Lake
- Urban lake surrounded by residential areas.
4. Kaliasot Dam Reservoir
- Supports irrigation and has industrial influences.
3. RESULTS AND DISCUSSION
The results of physico-chemical parameters of the water samples from Upper
Lake, Lower, Lake, Sarangpani Lake, Shahpura Lake and Kolar Lake are
represented in Table-1. The physico-chemical quality of water is one of the
most important parameter. The health, growth and productivity of the fish are
directly influenced by quality of water. The various physic-chemical
parameters of water such as temperature, conductivity, pH, total Dissolved
Solids (TDS), turbidity, Dissolved Oxygen (DO), hardness, chloride
content, free CO2 and total alkalinity may influence the density of
bacterial populations. The disturbance in these parameters can affect
adversely the fish production by decreasing the rate of food conversion,
reducing the weight gain and availability of soluble nutrients into the water
body (Sapkota et al., 2008; Gorlach-Lira et al., 2013). Human and animals
excreta are considered to be one of the common sources of pathogenic
microorganisms in any ecosystem (Servais et al., 2005). The excreta reach to
water bodies through run off during rainy season and make them
polluted.
Water temperature play an important role in the physico-chemical and
physiological behavior of the aquatic system (Welch, 1952). Fish being a cold
blooded animal its body temperature is likely to vary according to
fluctuations in temperature of water which affects its metabolism and
physiology. This ultimately affects the fish production. The high temperature
and bright sunshine accelerates the process of organic matter decay
resulting into the liberation of large quantities of CO2 and nutrients (Vasile,
2017). The acceptable temperature tolerance limit to fish can be 28 to 35 0C
for tropical major carps (Delince, 1992; Bhatnagar et al., 2004). We noticed
a range of temperature from 26 0C to 31 0C in 5 different stations studied
which is within the suitable range (Table-1). These observations are in line
with those of the study reported by Salla and Ghosh (2014) who reported 31.5
0
C temperature at Lower Lake of Bhopal during pre monsoon, 29.5 0C
0
monsoon temperature and 28 C post monsoon temperature. Other
investigators suggested 30 to 35 0C (Delince, 1992) and 28-32 0C
Bhatnagar et al., 2004).
Conductivity is a measurement of the ability of an aqueous solution to
carry an electric current. The acceptable limit of conductivity of freshwater
varies between 50 to 1500µs/cm (Boyd, 1979). In the current study the
conductivity was ranged between 644µs/cm ± 0.30 to 248µs/cm ± 0.41 (Table-
1). We observed maximum conductivity 644µs/cm ± 0.30 in water of
Shahpura Lake. Increased value of conductivity might be due to increased
concentration of salts at the bottom by sedimentation. This finding is in
agreement with Shivhare et al. (2013) who recorded the average conductivity
614µs/cm.
Any change in the pH of water is accompanied by the change in other
physic-chemical parameters. Maintenance of pH is one of the most important
factors of any aquatic system since all biochemical activities depends on the
pH. According to Santhosh and Singh (2007) the ideal pH level is 7.5 to 8.5
and below this is stressful to the fishes. We recorded highest pH 8.1 ± 0.15 of
water at both Lower Lake and Kolar Lake and the lowest pH 6.78 ± 0.13 of
water in Sarangpani Lake (Table-1). These values are in agreement with
results of Singh and Shrivastava (2016) who recorded pH value of Upper Lake
ranging 6.72 to 8.32. This could be due to accumulated organic matters
possibly because of decay and decomposition of religious waste which on
biological oxidation gives off CO2 which ultimately reduces the pH (Vyas et
al., 2006).
Total dissolved solids (TDS) may indicate increased organic matter within
the water body from wastewater discharge and effluents (Phiri et al., 2005;
Tay, 2008). A recommended level of TDS for most freshwater fish is less
than 400ppm (Terry Fairfield, 2000). We observed maximum TDS
398ppm ± 1.37 from Sarangpani Lake, 386ppm ± 4.32 from Shahpura
Lake, 209ppm ± 1.28 from Kolar Lake, 178ppm±2.16 from Lower Lake
and 145ppm ± 2.42 from Upper Lake which is in the acceptable range (Table-
1). Our results are in agreement with Singh and Shrivastava (2016) mentioned
the TDS range between 94t o 158 ppm. According to them the high content
of total dissolved solids elevates the density of water and influences
osmoregulation in fresh water organisms.
Turbidity accounts for the pollution by a wide variety of material, such as
silt, decaying, animal and plant matter, industrial wastes and sewage. In
majority it decreases the water clarity. Suspended sediments can clog fish
gills, reduce the growth rates. Ramama et al. (2008) reported higher
turbidity is unacceptable for bathing, industrial and other purposes. Boyd and
Lichtkoppler (1979) suggested that the clay turbidity in water should be 30 to
60 cm. We observed the highest turbidity 49cm± 2.12 from Sarangpani Lake,
45cm ± 1.21 for Lower Lake, 43cm±1.42 for Upper Lake, 37cm ± 2.01 for
Shahpura Lake and 32cm ± 3.16 for Kolar Lake (Table-1). The range of
turbidity was acceptable and also in line with Singh and Shrivastava (2016)
who noticed the turbidity in the range 37.6-53.2cm. We noted that maximum
turbidity from Sarangpani Lake may be due to lot of religious waste disposed
in the lake.
Dissolved oxygen (DO) illustrates the physico-chemical and biological
processes which take place in water. The tolerable limit of DO for Cyprinids is
6 to 8 mg per litre (Svobodova, 1993). The level of DO in all 5 water
stations was in acceptable range (Table-1). In the present study we observed
highest DO 6.8mg/l ± 1.42 from Kolar Lake. However other lakes showed DO
6.5mg/l±1.21 from Shahpura Lake and 6.1mg/l±2.01 from Upper Lake,
4.9mg/l ± 2.14 from Sarangpani Lake and DO 6.8mg/l ± 1.42 from Lower
Lake. Our range of DO 4.5mg/l to 6.8mg/l was acceptable. Similar results
were reported by Salla and Ghosh (2014) demonstrating DO in the range of
2.2 to 2.4mg/l in Lower Lake of Bhopal.
Hardness is the characteristics of water which prevents the foaming of soap.
This is due to the presence in water of certain salts of calcium and magnesium
dissolve in it. Also the addition of sewage, detergents and large scale human
use might be the cause of elevation of hardness (Mohanta and Patra, 2000).
The recommended ideal value of hardness for fish culture is in a range of 30-
180 mg/l (Santhosh and Singh, 2007). We observed maximum hardness
286 mg/l±18.26 from Sarangpani Lake, 114mg/l ± 8.29 from Lower Lake,
161.6mg/ l± 10.23 from Shahpura Lake, 126mg/l±13.58 from Kolar Lake and
112.6±11.41 from Upper Lake . The values for hardness were in range which
is acceptable (Table-1). We observed maximum hardness from Sarangpani
Lake where the addition of religious waste is the major cause of hardness of
water. These observations are lower than those reported by Salla and
Ghosh (2014) who registered variation in the total Hardness of Lower Lake of
Bhopal and reported values as 685mg/l at the pre monsoon, 620mg/l
monsoon temperature and 635mg/l post monsoon temperature.
The presence of chlorides in natural waters can mainly be attributed to
dissolution of salt deposits in the form of ions (Cl-). Higher concentrations
may indicate pollution by sewage, industrial wastes, intrusion of seawater
or other saline water. According to Stone and Thomforde (2004) the
desirable range of chlorides for commercial catfish production is above
60 mg/l. We observed chloride content 177mg/l ± 3.52 from Lower Lake,
86mg/l±8.05 from Upper Lake, 77 ± 2.19 from Kolar Lake, 67mg/l ± 5.29
from Shahpura Lake and 66mg/l ± 3.28 from Sarangpani Lake. The
hardness was recorded in the range 186 mg/l±18-112.6mg/l ± 11.41
(Table-1). The highest values at Lower Lake was due to inflow of
different types of religious waste as well as sewage pollution nearby this lake
which is similar to results noted by Vass and Zutshi (1983) in Kashmir
Himalayan Lake. These findings are higher than those of Shukla and Thakur
(2017) who retrieved the Chloride values from Shahpura Lake in the range
of 39.18 to 51.3mg/l in rainy season and 48.98 to 50.18 mg/l in winter season.
The major cause of high free CO2 content in stagnant water is due to its
diffusion from atmosphere, respiration by animals along with plants and
bacterial decomposition of organic matter (Misra et al., 1993). The ideal level
of CO2 in fishponds is less than 10 mg/l (Ekubo and Abowei, 2011). We
observed that maximum free CO2 was 9mg/l ± 1.56 from Upper Lake, 8.8mg/l
± 1.37 from Lower Lake, 7.9mg/l±1.29 from Sarangpani Lake, 6.3mg/l ± 1.62
from Shahpura Lake and 3.6mg/l ± 1.41 from Kolar Lake (Table-1). The
free CO2 values were in acceptable range which was closer to range
observed by Singh and Shrivastava (2016) as 4-18.2mg/l from Upper Lake.
Alkalinity in natural water is due to the presence of salts of weak acids.
According to Santhosh and Singh (2007) the ideal value of alkalinity for fish
culture is 50 to 300 mg/l. In our study, we observed maximum alkalinity
352mg/l ± 12.25 from Lower Lake, 129mg/l ± 6.48 from Kolar Lake,
114mg/l ± 8.12 from Shahpura Lake and 102mg/l ± 12.09 from
Sarangpani Lake (Table-1). Minimum alkalinity was 91.2mg/l ± 6.24
from Upper Lake. These results are in line with the findings of Parashar
(2006) who mentioned 88 to 90 mg/l pre monsoon alkalinity and 76 to 80 mg/l
post monsoon alkalinity.
Overall, the physico-chemical parameters of water studied from different
water bodies showed minor variations (Fig. 1 to 10) and were within the
desirable limit for the survival of fishes indicating healthy status of lakes of
Bhopal region.
Table-1: Physico-chemical analysis of water from samples collected from five Stations studied.
4. CONCLUSION
In the present study, all the water parameters studied were within the level.
The Sarangpani Lake and Shahpura Lake were observed to be more polluted
as the parameters like alkalinity and pH were slightly higher than the other
lakes. Overall, the water bodies of Bhopal found to be in favorable condition.
To maintain the healthy status of water bodies there should be continuous
assessment of the pollution level of the lakes.
5. ACKNOWLEDGMENT
First author thankfully acknowledge help extended by M.P. Council of
Science and Technology (MPCST), Bhopal for the laboratory facilities during
the research work.
6. KEy OBSERvATIONS
i. Upper Lake: Generally good water quality with low pollution levels, suitable
for drinking with minimal treatment.
ii. Lower Lake: Higher organic and bacterial pollution due to urban runoff and
sewage inflow.
iii. Shahpura Lake: Moderate pollution, likely from residential areas and
recreational activities.
iv. Kaliasot Reservoir: Higher levels of industrial and agricultural runoff
pollutants.
7. REFERENCES
I. APHA, 1998. Standard methods for the examination of water and
waste water 20th Ed., New York.
II. Bhatnagar, A. and Devi, P., 2013. Water quality guidelines for the
management of pond fish culture. Int J of Env Sci, 3(6): 1980-2009.
III. Bhatnagar, A., S.N. Jana, S.K. Garg, B.C. Patra, G. Singh and U.K.
Barman, 2004. Water quality management in aquaculture. Course
Manual of Summer school on Development of Sustainable
Aquaculture Technology in Fresh Andsaline Waters, CCS Haryana
Agricultural, Hisar, India, pp. 203-210.
Iv. Boyd, C. E., 1979. Water quality in warmwater fish ponds,
Agriculture Experiment Station, Auburn, Alabama, pp. 359.
v. Boyd, C.E and Lichtkoppler, F., 1979. Water Quality
Management in Fish Ponds. Research and Development Series No.
22, International Centre for Aquaculture (J.C.A.A) Experimental
Station Auburn University, Alabama, pp. 45-47.
vI. Boyd, C.E., 1979. Water quality in warmwater fish ponds. Univ of
Alabama, pp. 359.
vII. Chiaudani, G. and Premazzi, G. 1988. Water quality criteria in
Environmental Management. Report EUR 11638 EN, Commission
of the European Communities, Luxembourg.
vIII. Delince, G., 1992. The ecology of the fish pond ecosystem, Kluwer
Acadmic Publisers London, pp. 230.
Ix. Ekubo, A.A. and Abowei, J.F.N., 2011. Review of some water
quality management principles in culture fisheries. Res J App Sci,
Eng & Tech, 3(12): 1342-1357.
x. Fairfield, T., 2000. A commonsense guide to fish health.
Woodbury, N.Y: Barron's Educational Series 2000.
xI. FAO, I., 2016. WFP 2015. The State of Food Insecurity in the World
2015. Meeting the 2015 international hunger targets: taking stock of
uneven progress. Food and Agriculture Organization Publications,
Rome, Italy, pp.200.
xII. Gorlach-Lira, K., Pacheco, C., Carvalho, L.C.T., Melo Júnior, H.N.
and Crispim, M.C., 2013. The influence of fish culture in floating net
cages on microbial indicators of water quality. Braz J Biol, 73(3):
457-463.
xIII. Khan, A. A., Bhatnagar, A., & Saxena, R. 1988. An introduction of
Bhopal Lakes. In S. K. Kulshreshtha (Ed.), Proc. nat. symp. present,
past & future of Bhopal lakes
xIv. Khan, M.U.Z. and Ganaie, I.M., 2014. Assessment of Physico-
Chemical Parameters of Upper Lake Bhopal (MP) India. Int. Jou.
Engg. Res & Gen. Sci, 2(4): 354-363.
xv. Kiran, B. R., 2010. Physico-chemical characteristics of fish ponds of
Bhadra project at Karnataka, RASĀYAN Journal of Chemistry, 3(4):
671-676.
xvI. Mishra, S. and Panigrahy, R.C., 1995. Occurrence of diatom blooms
in Bahuda estuary, East Coast of India. Ind J Mar Sci, 24: 99-101.
xvII. Mohanta, B.K. and Patra, A.K., 2000. Studies on the water
quality index of river Sanamachhakandana at Keonjhar Garh,
Orissa, India. Poll Res, 19(3): 377-385.
xvIII. Mohapatra, U. K., & Singh, B. C. 1999. Trace metals in drinking
water from different sources in old capital city of Cuttak. Indian
Journal of Environmental Health, 41(2): 115–120.
xIx. Pani, S., & Mishra, S. M. 2000. Impact of hydraulic detention
on water quality characteristics of a tropical wetland (Lower Lake).
In P. Shrivastava (Ed.), Environmental pollution and its management.
New Delhi, India: ABS Publication.
xx. Parashar, C., Dixit, S. and Shrivastava, R., 2006. Seasonal variations
in physico-chemical characteristics in upper lake of Bhopal. Asian J.
Exp. Sci, 20(2): 297-302.
xxI. Phiri, O., Mumba, P., Moyo, B.H.Z. and Kadewa, W., 2005.
Assessment of the impact of industrial effluents on water quality of
receiving rivers in urban areas of Malawi. IntJournal of Env Sci &
Tech, 2(3): 237-244.
xxII. Ramana, P., Patil, S.K. and Sankri, G., 2007. Evaluation of water
quality of Magad wetland in Gadag district, Karnataka. Proceeding
of Tall, the world 12th Lak Conference, pp. 355-359. Salla S and
Ghosh S. Assessment of water quality parameters of lower lake,
Bhopal. 2014. Arch App Sci Res, 6(2): 8-11.
xxIII. Santhosh, B. and Singh, N.P., 2007. Guidelines for water quality
management for fish culture in Tripura. ICAR Research Complex for
NEH Region, Tripura Center, Publication no. 29.
xxIv. Sapkota A, Sapkota AR, Kucharski M, Burke J, McKenzie S, Walker
P, Lawrence R., 2008. Aquaculture practices and potential human
health risks: current knowledge and future priorities. Env int. 34(8):
1215-26.
xxv. Servais, P., Garcia-Armisen, T., Lepeuple, A.S. and Lebaron, P.,
2005. An early warning method to detect faecal contamination of
river waters. Annals of Microbio, 55(2): 151-156.
xxvi. Shivhare, N., Khan, S., Patel, N., Joshi, A. and Dutt, B., 2017.
Effect of nallahs on groundwater in indore city. Int J Eng Sci & Res
Tech. 6(5): 434-443.
xxvii. Shukla, S., Thakur, R., 2017. Distribution pattern of Algal species
in Shahpura Lake, Bhopal, with respect to physicochemical
parameters. Int J Pharm & Biol Arch, 8(05): 29-32.
xxviii. Singh, P.K. and Shrivastava, P., 2016. Assessment of water
quality of Upper Lake, Bhopal (MP). Int J Env Sci, 7(2): 164-173.
xxix. Stone, N.M. and Thomforde, H.K., 2004. Understanding your fish
pond water analysis report. Cooperative Extension Program,
University of Arkansas at Pine Bluff, US Department of
Agriculture and county governments cooperating. pp. 1-4.
xxx. Svobodová, Z., Lloyd, R., Máchová, J., Vykusová B., 1993. Water
quality and fish health.