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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056
Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072
© 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 1710
Study of Sustainable Sanitation System for Yadgir City using GIS and
Remote Sensing
Anand1, Dashrath Kolur2
1Student
2Professor
1,2Department of Civil Engineering
1,2Poojya Doddappa Appa College of Engineering ,Kalaburagi, Karnataka, India
---------------------------------------------------------------------***---------------------------------------------------------------------
Abstract - Water is the basic element of social and
economic infrastructure and is essential for healthy society
and sustainable development.
The natural resources like river, lake and ponds are
polluted due to the discharge of sewage water into the
sources without proper planning.
Due to the contamination of the sources by sewage
leads to surface water pollution, ground water pollution
resulting in serious health hazards, breakup of waterborne
diseases and in many instances the rivers getting fully
flooded with sewage flow.
The priority of the sanitation infrastructure system
is always in the last of all the development activity due to
the financial and power constraints, hence this live case
study is undertaken to design a technically and financially
self sustainable ecosanitation infrastructure system for
Yadgir city.
Key Words: Healthy society, Sewage water,
Pollution, health hazards, Infrastructure,
Ecosanitation etc.
1. INTRODUCTION
Sustainable sanitation recognizes that in order to
be sustainable, a sanitation approach must be socially
acceptable and economically viable.
In this way, sustainable sanitation is a loop-based
approach that differs fundamentally from the current
linear concepts of wastewater management as shown in
fig 1.a, and that does not only recognize technology, but
also social, environmental and economic aspects.
Sustainable sanitation is an approach that
considers sanitation holistically and it recognizes that
human excreta and wastewater are not waste product, but
a valuable resource.
This view is based on the fact that wastewater
and excreta contain significant amount of energy, plant
nutrients and also water that can be recycled and reused,
thus protecting natural resources.
Water and Sanitation is one of the primary
drivers of public health, this means that once we can
secure access to clean water and to adequate sanitation
facilities for all people, irrespective of the difference in
their living conditions, a huge battle against all kinds of
diseases will be won. These words, lent sanitation and
health.
This implies the following criteria
 Health and Hygiene
 Environmental and Natural Resources
 Technology and Operation
 Financial and economic issues
The view of general system of sustainable sanitation
system is shown in Fig,1.1.b. it is a simplified and idealized
technique for use of the treated water and nutrients
present in the treated effluent sludge.
It improves the yield of crop as well as revenue
generation and the system focuses on the
treated wastewater, the waste is not a waste, it’s a
important biological resources.
Fig 1.a. Sustainable Sanitation System
1.1 Study area
Yadgir is a city and the administrative
headquarters of Yadgir district in the state of Karnataka,
and the town covers an area of 5.6 square kilometers
(2.2 sq mi), the Bhima River flows through Yadgir city, and
it has an average elevation of 389m above mean sea level
(MSL).
The city municipal council jurisdiction extends up
to an area of 14.95 sq.km, population as per 2011 census
was 74,294, the city shown in map 1.1.a
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056
Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072
© 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 1711
Map.1.1.a. Location of Yadgir city map
Fig.1.1.b. General system of Sustainable Sanitation System
1.2 Catchment area of Doddanala tributary
Catchment area is a geo-hydrological unit of all land and
water within the confines of drainage divide which
contributes runoff to a common point.
The Doddanala tributary catchment area is covered by
40,692 hectares (406.92 km2), which is a basin shaped
area of land, bounded by natural features such as hills
from which surface and sub surface water flows into
streams, river and wetlands.
The system of streams which transport water,
sediment and other material from a catchment is called a
drainage network. No catchment is exactly like another.
Each has a different size, shape, drainage pattern and
features that are determined by natural processes,
particularly geology and climate as show in Fig 1.2.a.
Fig.1.2.a. Catchment area of Doddanala tributary
2. OBJECTIVES
a. To evaluate the sewage collection system by gravity
flow.
b. To evaluate providing treated effluent for agriculture
purpose by using GIS and Remote sensing techniques
for developing a sustainable sanitary infrastructure.
c. To make a detail analysis of cost benefit for self
sustainability of the treatment plant maintenance.
3. MATERIALS AND METHODOLOGY
In the present study, the toposheet in fig. no III.1
and contour line in fig.no III.2. show the details of the
boundaries of the catchment area and contours of
Doddanala’s tributary by using the GIS software.
Fig.III.1 Toposheet of Doddanala tributary Catchment
Area
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056
Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072
© 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 1712
Fig.III.2 Contour map of Yadgir city
3.1 Sampling
The collection of wastewater samples may seem a
relatively simple task and the collection of a
representative sample becomes much more complex.
In the case study, collection of samples carried
out once in a week.
3.2 Sewage Treatment Plant
Stabilization ponds are suggested for the
treatment of sewage as it is more suitable in tropical
climate with high efficiency in removal of BOD, Total solids
and nematodes.
It has been internationally recognized that the
effluent of the stabilization ponds are more suitable for
agriculture as it removes all the nematodes and some
more harmful activities present in it, effectively as
compete any other treatment methods. It is also very
economical and does not consume any energy in the
process, conventional single treatment unit is avoided and
provided with two smaller treatment plants unit to unable
the collection of city sewage by the gravity flow.
4. RESULT AND DISCUSSIONS
Table no IV.1 Population of Yadgir city as per census
department
S.
No.
Zones and Ward number Population
(2011)
01 Zone I population(ward no 01-24) 53,566
02 ZoneII population(ward no 25-31) 20,728
Population as per Census
department
74,294
4.1 Population Forecasting Methods
4.1.a. Arithmetic increase method
This method is based upon the assumption that, the
population increase at a constant rate, i.e. the rate of
change of population with time (ie. dp/dt) is constant. Pn=
[Po+nX]
Table.4.1.a. Population projection of Arithmetic method
Sl
no
Population Projection of Arithmetic Method
Year Population Forecasted
01 2011 74,294
02 2017 82,164
03 2047 1,15,889
4.1.b. Geometric increase method
In this method, the per decade percentage increase or
percentage growth rate (r) is assumed to be constant, and
the increase is compounded over the existing population
every decade. Pn= Po[1+(r/100)]n ,
Geometric average= √
Table.4.1.b. Population projection of Geometric increase
method
Sl
no
Population Projection of Geometric Increase
Method
Year Population Forecasted
01 2011 74,294
02 2017 85,874
03 2047 1,59,768
4.1.c. Incremental Increase Method
In this method, the per decade growth rate is not assumed
to be constant as in the arithmetic or geometric
progression methods, but in progressively increasing or
decreasing, depending upon whether the average of the
incremental increases (increment over the increase) in
the past data is positive or negative.
Pn = Po+nx+ ] y
Table.4.1.c. Population projection of incremental increase
method
Sl
no
Population Projection Incremental increase
Method
Year Population Forecasted
01 2011 74,294
02 2017 81,057
03 2047 1,11,039
Geometric increase method is adopted because Yadgir is
under developing city, recently it became the district due
to this many people migrate from nearby villages. Also
population is bound to increase for coming days.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056
Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072
© 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 1713
Table.4.2. Projected Population and Sewage Generation in
Sewerage Zones
Zones
of
city
Projected
Populatio
n
Quantity
of Sewage
Generatio
n
(MLD)
Quantity
of Sewage
Generatio
n
(MLD)
Treatment
plant
location
2047 2047 SAY RL in m
Zone
I 1,29,473 13.98
14 366
Zone
II 63,573 6.86
7 367
4.2. Doddanala tributary discharge and
Contamination
The volume of the discharge will be determined by factors
such as rainfall, climate, vegetation, soil type, drainage
basin relief and the activities of man.
In this case study it is observed that the tributary is
contaminated with 83% of sewage water as shown in fig
no, during 8 months of flow as shown in table no.
It is therefore seen that the major part of the flow in
Doddanala tributary constitute of sewage flow
contaminating the river Bhima.
This kind of scenario is seen all over the world with rapid
urbanization and large migration of rural population to
the city.
Hence it is envitable to develop a financially and
technically self sustainable sanitary infrastructure to
protect the precious water.
The calculated Doddanala’s peak discharge is 913.686
m3/sec and cross section required for peak discharge is
155.124 m2, and the width of Nala required for peak
discharge is 32.52 m.
Table no 4.2. Present scenario of Doddanala tributary from
October to May
Month
Runoff water discharge
(m3/month)
Sewage water
discharge (mL)
Jan 84.59 651
Feb 66.88 588
Mar 37.21 651
Apr 16.48 630
May 13.19 651
Oct 390.91 651
Nov 306.13 630
Dec 117.74 651
1033.12 5103
Chart no 4.2 Present scenario of Doddanala tributary
Fig 4.2: Doddanala view in Google earth
4.3 Storage pond for conserving of treated
effluent
The storage tanks volume is designed for initial output of
effluent for the design period of 15 years i.e 2032 having
two storage tanks for 14mld, a provision is also made for
providing one more storage tank of 7 mld for design
period of 30 years.
The RL of pond is kept in the 386 m, and distance from
treatment plants is 2KM, as per the analysis and study of
the topomaps, revenue maps, and RS data with analysis
made using GIS, the average RL of the agriculture field is
378 m hence gravity flow of the effluent to the field to
ensure that the treated water is providing to irrigation
purposes.
Diameter of the two proposed storage pond to conserve
treated effluent is 122 m and the effective depth is 6 m
with free board of 0.3 m extra.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056
Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072
© 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 1714
4.4 Requirement of treated effluent for irrigation
purposes
The following crops are sown in the Yadgir such as bajra,
toor, sugarcane, groundnut, sunflower, sesame, castor
bean, black gram, jowar, wheat, cotton, ragi, bengal gram,
and linsed are some of the major crops grown.
In this case study, the groundnut and cotton
which are cash crops can be grown in the available soil
conditions giving high returns.
The requirement of water and net area that can be
irrigated by the available treated effluent from the
treatment plants is shown in the following table no.4.4
Table:4.4. Requirement of treated water for irrigation
purposes
Crops Requirem
ent of
water in
(mm)
Crops
period
(days)
Net area
of land
irrigated
Required
water for 1
acre of
land in
MLD
Ground
nut
500-550
105
2 crops
/ year
122
acre/two
season
0.23
The groundnut can be grown in 122 acres per two season
of irrigated land.
The crop rotation can be made by this above mentioned
crop.
4.5 Revenue Generation from Wastewater
Treatment Plants
30 years plan period is considered and the amount of
input sewage to the sewage treatment plant and
consequently, the amount of productive wastewater is
increasing, the incomes of the plan are determined and the
general results are outlined in cost-benefit analysis (CBA).
We have expressed and brought this time factor with the
calculation of a period and income return in analysis. This
is the very time that should be spent for the return of
obtained incomes of a change in its costs.
Sl
n
o
Irrigation
land
(acres/tw
o season)
Treated
effluent
provide
d
(per
m3/two
season)
Cost
per
cubic
meter
(rupees
)
Cost
(rupees
)
Total
amount
charged
(rupees
)
0
1
1 460 12 5520
0
2
122 56,120 12 6,73,44
0
6,73,44
0
0
3
16,836 m3
(30 % of
sludge
from
16,836 12 2,02,03
2
2,02,03
2
treated
effluent)
0
4
Subscription fee 1500 rupees
per year
(1500 x 61 acres)
91,500 91,500
Total amount 9,66,97
2
Note : One acre of land requires 0.23mL of treated effluent.
So the duration of 245days (including two seasonal crops)
122 acres of land is irrigated. Cost of each cubic meter of
treated effluent is 12rupees.3
Sl
no
Object Cost
(rupees)
Total cost
(rupees)
01 Pumping cost 3,18,990 3,18,990
02 Labours (4 Nos ) charge
12000Rs x 4 x 12 months
5,76,000 5,76,000
Total Cost 8,94,990
Over all Income = Total Income in rupees - Total Cost in
rupees
= 9,66,972– 8,94,990
Over all Income = 71,982 rupees
5. CONCLUSION
 In our case study it was noted that Yadgir city does not
have any treatment unit and discharges the sewage
water directly into the Doddanala tributary which
ultimately joins river Bhima, so the river gets polluted,
hence by treating these sewage and providing the
effluent for the irrigation purpose pollution of the river
will be avoided, When the water demand for
agriculture is low during rainy season, the effluent can
be safely discharged into the river as the dilution factor
is high.
 The nutrient enriched effluent can be utilized for
increasing the productivity of the irrigated agriculture
land and generate financial resources for self
sustainability of treatment infrastructure.
 The population study was made as per the census and
population projection for the design period of thirty
years was 1,93,046, the total sewage discharge is 21
mld.
 The integrated application of Remote sensing data,
toposheets, revenue maps, wardwise maps and GIS
software clearly indicates the necessity of two
treatment plants of capacity 14 mld in zone-I of RL
366m, and 7 mld in zone-II of RL 367m, so that the
sewerage system of the whole city can be designed
under gravity flow with a zero energy consumption.
 The treated effluent is designed to be stored at an RL
386m, such that the water can be supplied for
irrigation of land by gravity flow.
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056
Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072
© 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 1715
 The storage tanks volume is designed for initial output
of effluent for the design period of 15 years i.e 2032
having two storage tanks for 14mld, a provision is also
made for providing one more storage tank of 7 mld for
design period of 30 years.
 The study was done for a particular groundnut crop
with a projected population for 2032, which works out
for providing treated effluent to 122 acres of
agriculture land in two seasons.
 The sludge generated in waste stabilization pond can
also be used for resource generation for economical
sustainability of treatment plants.
6. REFERENCES
[1] Susanaa .Thematic paper (October 2008).Sustainable
Sanitation alliance. Version 1.2
[2] Eeva Sundstrom (June 2010). Application and use of
GIS in Small Sanitation Projects in Developing Countries.
Tampere University of Applied sciences Department of
Environmental Engineering:
[3] Aime Tsinda, Pamela Abbott, Steve Pedley, Katrina
Charles, Jane Adogo , Kenan Okurut and Jonathan
Chenoweth:Challenges to Achieving Sustainable
Sanitation in Informal Settlements of Kigali, Rwanda.
Int.J.Environ.Res.Public Health 2013,10,6939-
6954;doi:10.3390/ijerph10126939
[4] Jennie Barron, Patric Buker, Guoyi Han, Charles Young.
Managing environmental systems:
supporting sustainable urbanization. Published by
Stockholm Environment Institute (2014)
[5] Linda S. Gaulke, Xiao Weiyang, Andrew Scanlon,
Amanda Henck, Tom Hinckley: Evaluation Criteria
for Implementation of a Sustainable Sanitation and
Wastewater Treatment System at Jiuzhaigou National
Park, Sichuan Province, China. Published (19 November
2009); DOI 10.1007/s00267-009-9398-1
[6] Emelie Walsund, Joseph Strahl (2013); Geographical
Information Systems as a Tool in Sustainable Urban
Development. Sustainable Urban Management Malmö
University:
[7] Christoph Luthi, Jennifer McConville, Anna Norstrom,
Arne Panesar, Rahul Ingle, Darren Saywell, Thorsten
Schutze: Rethinking Sustainable Sanitation for the
Urban Environment. 4th International Conference of
the International Forum on Urbanism (IFoU, 2009).
[8] Gikas G.D, Tsihrintzis V.A;Stabilization Pond Systems
for Wastewater Treatment: Facility costs and
Environmental Footprint Assessment.Global Nest
Journal, Vol 16, No 2, pp 374- 384,2014
[9] Phuntsho, H.K. Shon, S. Vigneswaran and J. Kandasamy;
Wastewater Stabilization Ponds (WSP) for Wastewater
Treatment. Vol II; Faculty of Engineering, University of
Technology, Sydney, Australia:
[10] Prof. Dr. Mohammed Ali I. Al-Hashimi Eng.
Hayder Talee Hussain; Stabilization Pond for
Wasteater Treatment. European Scientific Journal
May 2013 edition vol.9, No.14 ISSN: 1857 – 7881
(Print) e - ISSN 1857- 7431.
[11] Kudamnya, E. A. Schoeneich, K. Garba, M. L.
Remaining Storage of the Zaria Impounded
Reservoir and Rate of Erosion in Its Drainage
Basin. American International Journal of
Contemporary Research Vol. 3 No. 8; August 2013;
Department of Geology Ahmadu Bello
University Zaria.
[12] Ameen Rageh: Impacts Assessment of Treated
Wastewater Use in Agriculture Irrigation in
Amran Area, Republic of Yemen. Agricultural
Research and Extension Authority, Dhamar, Yemen
[13] Sources from Wikipedia of Sustainable sanitation
system, irrigation system, impounding reservoir,
sewage treatment plant, organic farming datas are
sourced.

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Study of Sustainable Sanitation System for Yadgir City using GIS and Remote Sensing

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 1710 Study of Sustainable Sanitation System for Yadgir City using GIS and Remote Sensing Anand1, Dashrath Kolur2 1Student 2Professor 1,2Department of Civil Engineering 1,2Poojya Doddappa Appa College of Engineering ,Kalaburagi, Karnataka, India ---------------------------------------------------------------------***--------------------------------------------------------------------- Abstract - Water is the basic element of social and economic infrastructure and is essential for healthy society and sustainable development. The natural resources like river, lake and ponds are polluted due to the discharge of sewage water into the sources without proper planning. Due to the contamination of the sources by sewage leads to surface water pollution, ground water pollution resulting in serious health hazards, breakup of waterborne diseases and in many instances the rivers getting fully flooded with sewage flow. The priority of the sanitation infrastructure system is always in the last of all the development activity due to the financial and power constraints, hence this live case study is undertaken to design a technically and financially self sustainable ecosanitation infrastructure system for Yadgir city. Key Words: Healthy society, Sewage water, Pollution, health hazards, Infrastructure, Ecosanitation etc. 1. INTRODUCTION Sustainable sanitation recognizes that in order to be sustainable, a sanitation approach must be socially acceptable and economically viable. In this way, sustainable sanitation is a loop-based approach that differs fundamentally from the current linear concepts of wastewater management as shown in fig 1.a, and that does not only recognize technology, but also social, environmental and economic aspects. Sustainable sanitation is an approach that considers sanitation holistically and it recognizes that human excreta and wastewater are not waste product, but a valuable resource. This view is based on the fact that wastewater and excreta contain significant amount of energy, plant nutrients and also water that can be recycled and reused, thus protecting natural resources. Water and Sanitation is one of the primary drivers of public health, this means that once we can secure access to clean water and to adequate sanitation facilities for all people, irrespective of the difference in their living conditions, a huge battle against all kinds of diseases will be won. These words, lent sanitation and health. This implies the following criteria  Health and Hygiene  Environmental and Natural Resources  Technology and Operation  Financial and economic issues The view of general system of sustainable sanitation system is shown in Fig,1.1.b. it is a simplified and idealized technique for use of the treated water and nutrients present in the treated effluent sludge. It improves the yield of crop as well as revenue generation and the system focuses on the treated wastewater, the waste is not a waste, it’s a important biological resources. Fig 1.a. Sustainable Sanitation System 1.1 Study area Yadgir is a city and the administrative headquarters of Yadgir district in the state of Karnataka, and the town covers an area of 5.6 square kilometers (2.2 sq mi), the Bhima River flows through Yadgir city, and it has an average elevation of 389m above mean sea level (MSL). The city municipal council jurisdiction extends up to an area of 14.95 sq.km, population as per 2011 census was 74,294, the city shown in map 1.1.a
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 1711 Map.1.1.a. Location of Yadgir city map Fig.1.1.b. General system of Sustainable Sanitation System 1.2 Catchment area of Doddanala tributary Catchment area is a geo-hydrological unit of all land and water within the confines of drainage divide which contributes runoff to a common point. The Doddanala tributary catchment area is covered by 40,692 hectares (406.92 km2), which is a basin shaped area of land, bounded by natural features such as hills from which surface and sub surface water flows into streams, river and wetlands. The system of streams which transport water, sediment and other material from a catchment is called a drainage network. No catchment is exactly like another. Each has a different size, shape, drainage pattern and features that are determined by natural processes, particularly geology and climate as show in Fig 1.2.a. Fig.1.2.a. Catchment area of Doddanala tributary 2. OBJECTIVES a. To evaluate the sewage collection system by gravity flow. b. To evaluate providing treated effluent for agriculture purpose by using GIS and Remote sensing techniques for developing a sustainable sanitary infrastructure. c. To make a detail analysis of cost benefit for self sustainability of the treatment plant maintenance. 3. MATERIALS AND METHODOLOGY In the present study, the toposheet in fig. no III.1 and contour line in fig.no III.2. show the details of the boundaries of the catchment area and contours of Doddanala’s tributary by using the GIS software. Fig.III.1 Toposheet of Doddanala tributary Catchment Area
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 1712 Fig.III.2 Contour map of Yadgir city 3.1 Sampling The collection of wastewater samples may seem a relatively simple task and the collection of a representative sample becomes much more complex. In the case study, collection of samples carried out once in a week. 3.2 Sewage Treatment Plant Stabilization ponds are suggested for the treatment of sewage as it is more suitable in tropical climate with high efficiency in removal of BOD, Total solids and nematodes. It has been internationally recognized that the effluent of the stabilization ponds are more suitable for agriculture as it removes all the nematodes and some more harmful activities present in it, effectively as compete any other treatment methods. It is also very economical and does not consume any energy in the process, conventional single treatment unit is avoided and provided with two smaller treatment plants unit to unable the collection of city sewage by the gravity flow. 4. RESULT AND DISCUSSIONS Table no IV.1 Population of Yadgir city as per census department S. No. Zones and Ward number Population (2011) 01 Zone I population(ward no 01-24) 53,566 02 ZoneII population(ward no 25-31) 20,728 Population as per Census department 74,294 4.1 Population Forecasting Methods 4.1.a. Arithmetic increase method This method is based upon the assumption that, the population increase at a constant rate, i.e. the rate of change of population with time (ie. dp/dt) is constant. Pn= [Po+nX] Table.4.1.a. Population projection of Arithmetic method Sl no Population Projection of Arithmetic Method Year Population Forecasted 01 2011 74,294 02 2017 82,164 03 2047 1,15,889 4.1.b. Geometric increase method In this method, the per decade percentage increase or percentage growth rate (r) is assumed to be constant, and the increase is compounded over the existing population every decade. Pn= Po[1+(r/100)]n , Geometric average= √ Table.4.1.b. Population projection of Geometric increase method Sl no Population Projection of Geometric Increase Method Year Population Forecasted 01 2011 74,294 02 2017 85,874 03 2047 1,59,768 4.1.c. Incremental Increase Method In this method, the per decade growth rate is not assumed to be constant as in the arithmetic or geometric progression methods, but in progressively increasing or decreasing, depending upon whether the average of the incremental increases (increment over the increase) in the past data is positive or negative. Pn = Po+nx+ ] y Table.4.1.c. Population projection of incremental increase method Sl no Population Projection Incremental increase Method Year Population Forecasted 01 2011 74,294 02 2017 81,057 03 2047 1,11,039 Geometric increase method is adopted because Yadgir is under developing city, recently it became the district due to this many people migrate from nearby villages. Also population is bound to increase for coming days.
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 1713 Table.4.2. Projected Population and Sewage Generation in Sewerage Zones Zones of city Projected Populatio n Quantity of Sewage Generatio n (MLD) Quantity of Sewage Generatio n (MLD) Treatment plant location 2047 2047 SAY RL in m Zone I 1,29,473 13.98 14 366 Zone II 63,573 6.86 7 367 4.2. Doddanala tributary discharge and Contamination The volume of the discharge will be determined by factors such as rainfall, climate, vegetation, soil type, drainage basin relief and the activities of man. In this case study it is observed that the tributary is contaminated with 83% of sewage water as shown in fig no, during 8 months of flow as shown in table no. It is therefore seen that the major part of the flow in Doddanala tributary constitute of sewage flow contaminating the river Bhima. This kind of scenario is seen all over the world with rapid urbanization and large migration of rural population to the city. Hence it is envitable to develop a financially and technically self sustainable sanitary infrastructure to protect the precious water. The calculated Doddanala’s peak discharge is 913.686 m3/sec and cross section required for peak discharge is 155.124 m2, and the width of Nala required for peak discharge is 32.52 m. Table no 4.2. Present scenario of Doddanala tributary from October to May Month Runoff water discharge (m3/month) Sewage water discharge (mL) Jan 84.59 651 Feb 66.88 588 Mar 37.21 651 Apr 16.48 630 May 13.19 651 Oct 390.91 651 Nov 306.13 630 Dec 117.74 651 1033.12 5103 Chart no 4.2 Present scenario of Doddanala tributary Fig 4.2: Doddanala view in Google earth 4.3 Storage pond for conserving of treated effluent The storage tanks volume is designed for initial output of effluent for the design period of 15 years i.e 2032 having two storage tanks for 14mld, a provision is also made for providing one more storage tank of 7 mld for design period of 30 years. The RL of pond is kept in the 386 m, and distance from treatment plants is 2KM, as per the analysis and study of the topomaps, revenue maps, and RS data with analysis made using GIS, the average RL of the agriculture field is 378 m hence gravity flow of the effluent to the field to ensure that the treated water is providing to irrigation purposes. Diameter of the two proposed storage pond to conserve treated effluent is 122 m and the effective depth is 6 m with free board of 0.3 m extra.
  • 5. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 1714 4.4 Requirement of treated effluent for irrigation purposes The following crops are sown in the Yadgir such as bajra, toor, sugarcane, groundnut, sunflower, sesame, castor bean, black gram, jowar, wheat, cotton, ragi, bengal gram, and linsed are some of the major crops grown. In this case study, the groundnut and cotton which are cash crops can be grown in the available soil conditions giving high returns. The requirement of water and net area that can be irrigated by the available treated effluent from the treatment plants is shown in the following table no.4.4 Table:4.4. Requirement of treated water for irrigation purposes Crops Requirem ent of water in (mm) Crops period (days) Net area of land irrigated Required water for 1 acre of land in MLD Ground nut 500-550 105 2 crops / year 122 acre/two season 0.23 The groundnut can be grown in 122 acres per two season of irrigated land. The crop rotation can be made by this above mentioned crop. 4.5 Revenue Generation from Wastewater Treatment Plants 30 years plan period is considered and the amount of input sewage to the sewage treatment plant and consequently, the amount of productive wastewater is increasing, the incomes of the plan are determined and the general results are outlined in cost-benefit analysis (CBA). We have expressed and brought this time factor with the calculation of a period and income return in analysis. This is the very time that should be spent for the return of obtained incomes of a change in its costs. Sl n o Irrigation land (acres/tw o season) Treated effluent provide d (per m3/two season) Cost per cubic meter (rupees ) Cost (rupees ) Total amount charged (rupees ) 0 1 1 460 12 5520 0 2 122 56,120 12 6,73,44 0 6,73,44 0 0 3 16,836 m3 (30 % of sludge from 16,836 12 2,02,03 2 2,02,03 2 treated effluent) 0 4 Subscription fee 1500 rupees per year (1500 x 61 acres) 91,500 91,500 Total amount 9,66,97 2 Note : One acre of land requires 0.23mL of treated effluent. So the duration of 245days (including two seasonal crops) 122 acres of land is irrigated. Cost of each cubic meter of treated effluent is 12rupees.3 Sl no Object Cost (rupees) Total cost (rupees) 01 Pumping cost 3,18,990 3,18,990 02 Labours (4 Nos ) charge 12000Rs x 4 x 12 months 5,76,000 5,76,000 Total Cost 8,94,990 Over all Income = Total Income in rupees - Total Cost in rupees = 9,66,972– 8,94,990 Over all Income = 71,982 rupees 5. CONCLUSION  In our case study it was noted that Yadgir city does not have any treatment unit and discharges the sewage water directly into the Doddanala tributary which ultimately joins river Bhima, so the river gets polluted, hence by treating these sewage and providing the effluent for the irrigation purpose pollution of the river will be avoided, When the water demand for agriculture is low during rainy season, the effluent can be safely discharged into the river as the dilution factor is high.  The nutrient enriched effluent can be utilized for increasing the productivity of the irrigated agriculture land and generate financial resources for self sustainability of treatment infrastructure.  The population study was made as per the census and population projection for the design period of thirty years was 1,93,046, the total sewage discharge is 21 mld.  The integrated application of Remote sensing data, toposheets, revenue maps, wardwise maps and GIS software clearly indicates the necessity of two treatment plants of capacity 14 mld in zone-I of RL 366m, and 7 mld in zone-II of RL 367m, so that the sewerage system of the whole city can be designed under gravity flow with a zero energy consumption.  The treated effluent is designed to be stored at an RL 386m, such that the water can be supplied for irrigation of land by gravity flow.
  • 6. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395 -0056 Volume: 04 Issue: 06 | June -2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 5.181 | ISO 9001:2008 Certified Journal | Page 1715  The storage tanks volume is designed for initial output of effluent for the design period of 15 years i.e 2032 having two storage tanks for 14mld, a provision is also made for providing one more storage tank of 7 mld for design period of 30 years.  The study was done for a particular groundnut crop with a projected population for 2032, which works out for providing treated effluent to 122 acres of agriculture land in two seasons.  The sludge generated in waste stabilization pond can also be used for resource generation for economical sustainability of treatment plants. 6. REFERENCES [1] Susanaa .Thematic paper (October 2008).Sustainable Sanitation alliance. Version 1.2 [2] Eeva Sundstrom (June 2010). Application and use of GIS in Small Sanitation Projects in Developing Countries. Tampere University of Applied sciences Department of Environmental Engineering: [3] Aime Tsinda, Pamela Abbott, Steve Pedley, Katrina Charles, Jane Adogo , Kenan Okurut and Jonathan Chenoweth:Challenges to Achieving Sustainable Sanitation in Informal Settlements of Kigali, Rwanda. Int.J.Environ.Res.Public Health 2013,10,6939- 6954;doi:10.3390/ijerph10126939 [4] Jennie Barron, Patric Buker, Guoyi Han, Charles Young. Managing environmental systems: supporting sustainable urbanization. Published by Stockholm Environment Institute (2014) [5] Linda S. Gaulke, Xiao Weiyang, Andrew Scanlon, Amanda Henck, Tom Hinckley: Evaluation Criteria for Implementation of a Sustainable Sanitation and Wastewater Treatment System at Jiuzhaigou National Park, Sichuan Province, China. Published (19 November 2009); DOI 10.1007/s00267-009-9398-1 [6] Emelie Walsund, Joseph Strahl (2013); Geographical Information Systems as a Tool in Sustainable Urban Development. Sustainable Urban Management Malmö University: [7] Christoph Luthi, Jennifer McConville, Anna Norstrom, Arne Panesar, Rahul Ingle, Darren Saywell, Thorsten Schutze: Rethinking Sustainable Sanitation for the Urban Environment. 4th International Conference of the International Forum on Urbanism (IFoU, 2009). [8] Gikas G.D, Tsihrintzis V.A;Stabilization Pond Systems for Wastewater Treatment: Facility costs and Environmental Footprint Assessment.Global Nest Journal, Vol 16, No 2, pp 374- 384,2014 [9] Phuntsho, H.K. Shon, S. Vigneswaran and J. Kandasamy; Wastewater Stabilization Ponds (WSP) for Wastewater Treatment. Vol II; Faculty of Engineering, University of Technology, Sydney, Australia: [10] Prof. Dr. Mohammed Ali I. Al-Hashimi Eng. Hayder Talee Hussain; Stabilization Pond for Wasteater Treatment. European Scientific Journal May 2013 edition vol.9, No.14 ISSN: 1857 – 7881 (Print) e - ISSN 1857- 7431. [11] Kudamnya, E. A. Schoeneich, K. Garba, M. L. Remaining Storage of the Zaria Impounded Reservoir and Rate of Erosion in Its Drainage Basin. American International Journal of Contemporary Research Vol. 3 No. 8; August 2013; Department of Geology Ahmadu Bello University Zaria. [12] Ameen Rageh: Impacts Assessment of Treated Wastewater Use in Agriculture Irrigation in Amran Area, Republic of Yemen. Agricultural Research and Extension Authority, Dhamar, Yemen [13] Sources from Wikipedia of Sustainable sanitation system, irrigation system, impounding reservoir, sewage treatment plant, organic farming datas are sourced.