Nahid Paper 1 Final ver 2 1 - Sudan University of Science ... · 1 Optimal Pipelines Sizing for...
Transcript of Nahid Paper 1 Final ver 2 1 - Sudan University of Science ... · 1 Optimal Pipelines Sizing for...
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Optimal Pipelines Sizing for Water Distribution Systems of Micro
Irrigation
Hassan Ibrahim Mohamed1, Nahid Ibrahim Ahmed El Haj
2, Haitham Ragab El Ramlawi
3,Abd
El Rahman Mohammed Nour4 , and Omran Musa Abbas
1
1-Department of agricultural engineering, College of agricultural studies Sudan University of science
and technology. 2- Department of Agricultural Engineering. Khartoum State- Ministry of Agriculture
and Water Resources 3-Centre of Dry land Farming Research and Studies, Faculty of Agricultural and
Environmental Sciences, University of Gadaref 4-Department of agricultural engineering, College of
agricultural Technology and Fish sciences -Neeleen University.
ABSTRACT
The main aim of the present study is to develop optimization process of water pipe networks
design through studying the effect of pipe and pump costs on the optimization process in a
network with a predetermined layout. Computer simulation and analytical solutions have
been used for minimizing the Capital cost of multiple-outlet pipelines of drip water
distribution system composed of many pipes with different diameters, while the variation in
pressure head is restricted to assure the required outlet discharge uniformity. The present
study focuses on developing a cost function design model for pump-pipelines system with
emitters distributed along the pipelines. The model has been developed to support the
design of micro irrigation systems and to advise farmers to improve drip system
performance .The procedure uses the linear programming, in which pipe length with
commercial pipe diameter is used as optimum variable and the factors affecting the pressure
head along multiple-outlet pipelines are considered. The objective function, to obtain the
optimal diameter of each pipe, is based on the capital cost of the piping system, pumps and
the cost of energy required for operating the system. The model consists of an objective
function that maximizes profit at the farm level, subject to appropriate geometric and
hydraulic constraints. The main items considered affecting cost were: operating pressure
within the network, the pipe diameter, and the pumping cost which include pumping station
and energy. The hydraulic and operational limitations imposed on the system are: limiting
maximum and minimum velocity, permissible pipe pressure, defined pressure at outlets, and
defined discharge at selected points.
Model solution employ WINQSB 6.0, and uses Excel database with information on emitters
and pipes available in the market, as well as on crops, soils and the systems under design.
The solution procedure is based on an iterative scheme and examined two case studies.
Results obtained indicate model capability to cut down costs of pipes as compared to
conventional design method.
Keywords: optimum network, water pipe network, water least annual cost principle, linear
programming, pump-pipelines system design, micro - irrigation network.
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1. INTRODUCTION
Sustainable irrigated agriculture requires irrigation practices that are environmentally
friendly, economically viable and lead to high irrigation performance (Pereira et al., 2002).
Micro irrigation systems have the potential for achieving high irrigation performance and
offer a large degree of control, enabling accurate water and fertilizer applications according
to crop water and nutrients requirements, thereby minimizing environmental impacts and
providing for increased performance and water productivity. Achieving this requires that
systems are designed and operated in a way that water is applied at a rate, duration and
frequency that maximize water and nutrient uptake by the crop, while minimizing the
leaching of nutrients and chemicals out of the root zone (Hanson et al., 2006). Highly
uniform and timely water application is therefore required (Mermoud et al., 2005; Santos,
1996; Hanson et al., 2006). Drip water distribution network is a system of hydraulic elements
contains (pipes, reservoirs, pumps, valves of different types), which are connected together
to provide the quantities of water within prescribed pressures from sources to the plant.
Hence, micro irrigation system need to be designed and operated based on the selection of
pipeline sizes which is directed to achieve high uniformity of water distribution and
minimum operating costs. The selection of a pipeline size to meet a specific criterion, such as
the minimum annual expenses, has been extensively treated by various researchers
(Haghighi et al., 1989; Barragan et al., 2006; Kang and Nishiyama, 1996; 2002; Demir et al.,
2007; Valiantzas, 2003; Valiantzas et al., 2007). The basic components of a micro -irrigation
system are: the pump/filtration station (consisting of the pump, filtration equipment,
controllers, main pressure regulators, control valves, water-measuring devices and chemical
injection equipment); the delivery system, (includes: the main and sub main pipelines to
transfer water from the source to the manifolds, (filters, pressure regulators, and control
valves); the manifolds, which in turn supply water to the laterals and the laterals that carry
water to the emitters (Pereira and Trout, 1999; Evans et al., 2007). Design of micro irrigation
systems is therefore complex considering the need to select and size all system components
and the need to design for a targeted uniformity of water application (Bralts et al., 1987;
Keller and Bliesner, 1990; Wu and Barragan, 2000).
Main advances in design of micro irrigation systems refer to pipe sizing and layout and to the
selection of emitters because these system components control the potential irrigation
performance and costs. The design options relative to the pump, valves, controllers, filters
and fertilizer devices are generally made after pipes and emitters are selected since they
depend upon related pressure and discharges at the various nodes of the system network
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(Keller and Bliesner, 1990). However, their appropriate selection also influences the
irrigation performance, and they also produce additional head losses that must be
considered when sizing the system. To support and ease design, a variety of models have
been developed such as that for the pump/filtration station (Haghighi et al., 1989), for
assessing emitter uniformity (Barragan et al., 2006), for pipe sizing (Kang and Nishiyama,
1996; 2002; Demir et al., 2007) and for economic optimization of systems (Valiantzas, 2003;
Valiantzas et al., 2007).
Optimization methods for pipe network analysis has been reviewed by Stephenson et al,
(1981) .Their extensive study showed that the dynamic programming schemes are suitable
for pipe size selection of main pipelines. Transportation programming is convenient for cases
in which the pipe routes and size are to be optimally selected. Because of the complex
network analysis schemes algorithms based on linear programming technique has been
developed to minimize system costs (Valiantzas, 2003; Valiantzas et al., 2007). With the
advances in optimization search methods, network analysis has been extended to include
network routes (Cembrowicz et al,. 1996) and other important parameters such as:
management of irrigation systems (Srinivasan and Guimaraes, 1996, Eduardo and Marino,
1990 and Mohtar et al 1991) where the effects of land topography, irrigation method and
land allocation, maximization of land yield, profit and/or management of wastewater reuse
(Afshar and Miguel, 1989) is included. Application of the genetic algorithms for pipe network
optimization is in progress where it may provide some advantages over the classical linear,
dynamic and/or nonlinear programming methods (Dandy et al, 1996, Simpson et al ,1994).
The present work is directed to the study of a single source pump-branching pipes micro
irrigation distribution system for optimum selection of the pipes diameters on the basis of
minimum cost function under limits of hydraulic constraints for achieving high irrigation
performance using linear programming technique.
2. THE MATHEMATICAL MODEL The decision support model was developed to design drip and micro sprinkling systems, and
as a tool to advice farmers about how to improve their micro irrigation systems when using
data obtained during field evaluation of systems under operation. It is employs WINQSP, and
Excel programs and runs in a Windows environment in a personal computer.
The conceptual structure of the model is in presented figure 1, where two main components
are identified: the database and the Hydraulic Procedure. The algorithm is mainly oriented
to design and select the pipe system and emitters for an irrigation sector. The computer
design model has been integrated into three principal modules: the database and layout
module, the design module and the evaluation module. The database module entails
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specifying details of the system alignments and contains information on emitters, pipes, and
crops, soils such as: the emitter and lateral spacing; the lengths of the laterals and the
manifold; and the elevations of the pipes. Once this has been done, then the actual pipe
design can be carried out in the design module. The design module is tailored to iteratively
size the pipe and emitters system for individual laterals using WINQSB algorithm. Output
from this procedure includes: a display of the pipe flow and pressure characteristics;
allowed pressure envelope and the pipe hydraulic grade-line; and a summary table of the
operations performed in the design process.
2.1 Characteristic of the model: The model has been developed for fields with known dimensions on flat terrain. The water
source is assumed to be groundwater provided by a pump located at the centre of field. All
sub main pipes that feed the sub-units via supply pipes are perpendicular to the main lines
and are fed from both sides of the main lines. All pipes are made from polyethylene, and
emitters are fixed on the laterals at a fixed spacing. Each supply, sub main and mainline pipe
is controlled by one independent valve, which is located just at the beginning of the
corresponding pipe. One filter unit is assumed to be located just after the pump. Water is
assumed to be extracted from groundwater by means of a turbine pump system. The main
and sub main pipes are buried while sub-unit pipes (laterals, manifold, supply) are laid on
the ground. Total system cost consists of capital and installation costs plus the present value
of the operating costs over the expected life of the project.
2.2 Formulation of the model:
2.2.1 Model assumption and data input: In the present optimization model the general
configuration of pipes within the field (main and sub main lines) and within the sub-units
(lateral, manifold and supply lines) is fixed. However, since the area and the dimensions of
sub-units in the both X and Y directions change in each iteration of the field division, the
length and the size of all pipes change as well. The model was developed for a field with
given area and known dimensions for which the water source is located at the centre of
field.
2.2.2 Optimization procedure: The model evaluates all combinations of pipe sizes, and shift
patterns. The system cost is evaluated for various pipe sizes. Optimization is carried out by
complete enumeration of all alternatives. The following values are assumed to be known:
(1) The dimensions of the field,,[Fx ,m and Fy, m];
(2) The depth of the water table [Hwt ,m];
(3) The potential evapotranspiration,[ETo mm/day], the crop coefficient, [Kc];
(4) The minimum and maximum percentage of wetted area,[Pw, %];
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(5) The application efficiency of drip irrigation, [Ea, %];
(6) The annual irrigation requirement for the crop, [Air, mm];
(7) The field capacity, FC and the permanent wilting point[ PWP], of soil;
(8) The depth of root zone, [R, m], soil infiltration rate, Isoil (mm/hr) and soil bulk
density Row S (g/cm2);
(9) The portion of the available moisture depletion f (%);
(10) The spacing between emitters,[ dx ], and laterals, dy, respectively (m);
(11) The pipe cost coefficients[ k1,k2, k3]; the pump, cost parameters[ k, a, b];
(12) Efficiencies for the electric motor,[Em], and pump,[ Ep], respectively;
(13) The discount rate,[ i ], and expected project life,[ n, years];
2.2.3 The decision variables in the design of irrigation:
1. The pipe diameters and locations.
2. Pump locations and sizes.
3. Valve and regulator locations.
4. Reservoir sizes and locations.
The objective function: The objective of this optimization is to establish the quantities of the
each of the decision variables that will be used in the irrigation network so as to minimize a
pre-selected criterion. As mentioned previously, the most common criterion for the
optimization of network design is that of minimum cost. In order to achieve this
optimization, the value of the selected criterion is expressed as a function of the quantities
of the decision variables being used in the design.
The decision variables: Normally the quantities of the decision variables that can be used will
be constrained by a number of pre-determined factors. When considering pipe diameters as
decision variables for the design of irrigation networks, the allowable diameters to be used
along a specific path in the network must be equal to or greater than the smallest possible
diameter that will result in the pre-determined allowable head loss along the path. So for
every optimization problem, a set of relationships can be formulated which govern the
quantities of the decision variables that may be incorporated into the objective function.
These relationships are referred to as the constraints of the optimization.
Thus the optimization of the design of single-source branching networks can be formulated
as an LP problem, and it is derived in accordance with Karmeli et al, (1968) as follows:
a- The links of a network are defined by the upstream node, i, and the downstream node, j,
respectively. Then for each link ij in the network being designed a candidate set of
diameters, m, is to be considered. One set of decision variables is given by the length of pipe
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for each of the candidate diameters to be used in each link ij. These lengths are expressed as
X��� and they have associated costs given by C��� per unit length.
b- A second set of decision variables is given by the operating head of the pump at the
source of the network, for each different network loading condition, ℓ. These operating
heads are expressed as XP (l). The discharge at the pump for loading ℓ is QP (ℓ), and k (ℓ) is
the present value of the operating cost of the pump per unit of head and discharge that it
delivers, multiplied by: (a) coefficients reflecting the units in which the head and discharge
are expressed, (b) the efficiency of the pump and (c) the fraction of the total pumping time
during which loading ℓ is operative. Then the cost of operating the pump during loading ℓ is
given by k (ℓ).XP (ℓ) QP (ℓ). Likewise, if we assume that the capital cost of the pump, kc per
unit of power, increases linearly with its maximum operating head XPM, then the overall
capital cost of the pump at the source is given by kc XPM.
The drip irrigation design model described in this paper consists of small permanent system
with semi-automation, thus labor cost is considered to be small.
2.2.4 The Objective Function: The drip irrigation design model described in this paper
consists of an objective function that minimizes the sum of the capital cost and present
value of operating cost subject to appropriate constraints. The system is assumed to be
permanent with semi-automation, thus labor cost is considered to be small. In order to
formulate and solve an optimization problem mathematically it is first necessary to define
the decision variables. The objective function of the LP is given by:
Minimize [K] = ∑ij ∑m
C ijm
Xijm +
∑l
K (l)*XP (l)
*QP (l) +
Kc XPM
----------------------------- (1)
Where: ∑
l the summation of all loading, ∑
m the summation of all candidate pipe diameters m in link ij, ∑
ij the summation of all links ij in the network,
K= the total (present value) cost of the system.
2.2.5 The Constraints: The number of constraints in many cases a large network will generate
a very large LP, consisting of many variables and constraints. In order to maintain the
problem within practical bounds so that it can be solved on readily available computers, it is
particularly necessary to limit the number of constraints. This can generally be done by
careful selection of the head constrains. It will not be necessary to specify these constraints
for each and every node in the network. Hence, the LP should be run initially with a small set
of constraints covering what the designer considers to be the most critical nodes. In many
cases, the combination of topographic effects and the minimum or maximum head
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requirements for ‘less critical’ nodes will ensure that these requirements are automatically
satisfied by specifying the constraints for the ‘more critical’ nodes. The designer should
always check that all the head requirements are met in the optimal solution. If they are not,
then constraints should be added for the nodes that do not meet their respective maximum
or minimum head requirements, and the LP should then be re-run. Four sets of constraints
can be derived for the LP problem:
A- The non-negativity constraints: It is a condition of the LP solution procedure that the
decision variables must all be non-negativity. Thus a set of constrains can be stated as:
XIJM ≥ 0 ------------------------------------------------------------------------------------------- (2)
XP (l) ≥ 0 ……………………………………………………………………………… (3)
B- Length constraints: The lengths of each diameter of pipe selection for a given link must
add up to the length of the link. This is stated by:
∑m X ijm = Lij ………………………………...………………………………………… (4)
Where: Lij= the length of link ij.
C- The head loss constraint: Assume that the head at a specific reference node is fixed and
known for loading (l) and that either the maximum or the minimum (or both) allowable
heads at a second node downstream of the reference node are also known for loading (l).
Then the total head loss in the network along the path from the reference node to the
second node must not result in the head at the second node being either greater than the
allowable maximum, or less than the allowable minimum. This is expressed by:
HMINn(l) ≤ Hs(l) ±∑ij∑mJijm (l) Xi jmHMAXn…………………………………………….(5)
Where: Hs (l) = the head plus elevation at the reference node, s, for loading (l).
HMINn (l); HMAXn (l) = the minimum and maximum allowable head plus elevation at the
second node, (n), for loading (l).
Jijm(l) = the head loss (or gain depending on the direction of flow) per unit length of pipe of
diameter m in link (ij) under load (flow)( l).
∑ij ∑m = the summation of all segments (Xijm) in all links (ij) along the path from node s to
node (n).
Jijm (l) is calculated from the Hazen-Williams (or some other appropriate) formula.
D- The pumping constrain: Since the operating head of the pump for each loading is a
decision variable in the LP, it must be constrained not to exceed the maximum possible head
that the pump is capable of producing, XPM. This is stated by:
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XP (l) ≤ PM……………………...………………………………………………………..……… (6)
Thus when the LP defined by the objective function and the four sets of constraints
described above is solved for a specific network, the solution provides the designer with the
pipe diameters and pumping head at the source that should be used so as to give the
cheapest possible network that will satisfy the pre-determined hydraulic requirements. It
should be noted that the LP solution provides a consistent hydraulic solution for the network
at the same time as it optimizes the design.
2.3 Model Assumptions:
A-Pump costs: In formulating the objective function of the LP, two assumptions were made
about the capital cost of installing pumps in an irrigation system.
I-Firstly it was assumed that the cost increases linearly with increasing capacity (as
measured in units of power) of the pumps. This assumption is in fact an incorrect one,
since the capital cost per unit of power decreases with increasing capacity, due to the
various economies of scale. This would suggest the use of a technique known as
separable programming, which uses linear approximations for separate portions of the
cost against capacity curve. However, Alperovits and Shamir (1977) have proposed a
simple iterative algorithm based on the LP solution.
II-Secondly it was assumed that the dominant parameter determining the required
capacity is the maximum head required at the pump. The second assumption implies
that the discharge at the pumps will be constant for all loading conditions. While there
are several advantages in trying to achieve this for an irrigation network, it will
normally not be feasible. The discharge requirements at the pump will usually vary
during the irrigation cycle. The objective function will therefore only be valid when
XPM is associated with the maximum power requirement at the pumps, i.e. when:
XPM*QP (L) > = XP (t).Qp (l) ………………………………...……… (7)
Where: L = the loading condition associated with XPM.
B-Candidate diameters: In setting up the LP for a network, the designer has to specify a set
of candidate diameters, m, for each link ij. This results in introducing an implicit constraint
into the LP since the optimal solution cannot include any segments, (Xijm) of a diameter m
that was not in the initial candidate set. However, this may be overcome by using the
iterative procedure of Alperovits and Shamir (1977).
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Fig
1 T
he
Flo
w c
har
t of
the
model
conce
ptu
al s
truct
ure
(Rev
ise
the
flo
w c
har
t w
ith D
r O
mra
n)
En
ter
No
min
al
Dis
cha
rge
of
Em
itte
r
(lit
/hr)
ST
AR
T
Ca
lcu
late
We
tte
d D
iam
ete
r-S
w (
m)
C
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te W
ett
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Ra
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)
Ca
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Dis
tan
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etw
ee
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ate
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-Se
(m
)
Dia
me
ter
of
Sh
ad
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(m
)
Pe
rce
nt
of
Gro
un
d C
ov
er
(%)
Le
ng
th o
f La
st L
ate
ral
(m)
Len
gth
of
Last
Ma
nif
old
(m
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A
A
Inp
ut
Da
ta o
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il
So
il C
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So
il M
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tte
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So
il T
ype
In
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t La
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De
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n
En
tae
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aily
Cro
p W
ate
r R
eq
. (m
m/d
ay
)
En
ter
Irri
ga
tio
n E
ffic
ien
cy (
%)
En
ter
Irri
ga
tio
n E
ffic
ien
cy (
%)
Est
ima
te:
Co
eff
icie
nt
of
Em
itte
r E
qu
ati
on
E
xpo
ne
nt
of
Em
itte
r E
qu
ati
on
Ma
nu
al
Inp
ut
Da
ta:
Allo
wa
ble
irr
iga
tio
n T
ime
(h
r)
No
. o
f P
lan
ts R
ow
s /
Ma
nif
old
Late
ral
&M
an
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ld l
ay
ou
t in
on
e s
ide
? m
an
ifo
ld
N
Est
ima
te f
rom
lo
ok
up
ta
ble
Ha
zen
-Willia
m C
oe
ffic
ien
t fo
r M
an
ifo
ld
Y
Ma
nu
al In
pu
t D
ata
:
Nu
mb
er
of
Ma
nif
old
/ S
ub
ma
in
Est
ima
te f
rom
lo
ok
up
ta
ble
H
aze
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illia
m C
oe
ffic
ien
t fo
r M
ain
Ne
t
Po
siti
ve S
uct
ion
He
ad
(m
)
C
E
10
Cal
cula
te:
B
reak
Hours
e P
ow
er o
f E
ngin
e& P
um
p (
HP
) T
ota
l D
ynam
ic H
ead o
f P
um
p (
m )
Tota
l L
oss
es i
n M
ain a
nd S
ub m
ain l
ines
C
Man
ual
In
put
Dat
a: P
um
p E
ffic
iency
(%
) E
ngin
e E
ffic
iency
(%
)
Des
ign P
oin
t R
ainfa
ll
P
Opti
miz
e R
esu
lt o
f D
rip
Irri
gat
ion P
aram
eter
s?
Man
ual
In
put
Dat
a: E
levat
ion
Dif
fere
nce
bet
wee
n P
um
p a
nd H
igh
est
Po
int
in M
ain L
ine
(m)
Cal
cula
te:
D
isch
arge
of
Sub
mai
n &
Mai
n (
m^3
/hr)
D
iam
eter
of
Lat
eral
(m
m)
No.
of
Em
itte
rs /
Tre
e
Tim
e o
f Ir
rigat
ion
(h
r)
Cal
cula
te:
D
isch
arge
for
Tre
e (l
it/h
r)
Aver
age
Oper
atin
g H
ead o
f E
mit
ter
(m)
All
ow
able
Hea
d D
iffe
rence
& L
ater
al &
Man
ifold
(m
)
Red
uct
ion
Fac
tor
in M
anif
old
(F
)
P
Dis
pla
y R
esult
of
Dri
p I
rrig
atio
n D
esig
n (
Lay
out)
Tota
l D
ynam
ic H
ead o
f P
um
p &
Engin
e
Hours
Pow
er o
f P
um
p &
En
gin
e
Dia
met
er o
f M
ain L
ine,
Sub m
ain,
Lat
eral
Dis
char
ge
of
Mai
n L
ine,
Sub
mai
n, L
ater
al, an
d E
mit
ters
Dis
pla
y R
esult
of
Dri
p I
rrig
atio
n D
esig
n
D
aily
cro
p w
ater
Req
.(m
m/d
ay)
(dep
et 5
mm
/day
T
ime
of
Irri
gat
ion (
hr)
N
um
ber
of
Em
itte
rs/L
ater
al
N
Y
R STO
P
11
Fig
ure
1:
Model
Con
ceptu
al F
low
Char
t
R
Input
Dat
a:
Cost
of
Mai
n L
ine
Pip
e &
Sub
m
ain P
ipe
and L
ater
al P
ipe
W
R
Dis
pla
y R
esult
of
Opti
miz
atio
n P
rogra
m
for
Dri
p I
rrig
atio
n D
esig
n:
O
utp
ut
Cost
of
Mai
n L
ine
Pip
e &
Sub
m
ain P
ipe
and L
ater
al P
ipe
Outp
ut
cost
les
s th
an
input
cost
?
W
STO
P
E
Sta
rt O
pti
miz
atio
n P
rogra
m
for
Dri
p I
rrig
atio
n D
esig
n
Cal
cula
te:
In p
ut
Tota
l C
ost
of
Dri
p i
rrig
atio
n D
esig
n
Est
imat
ed C
onst
rain
ts o
f L
P m
odel
: L
ength
of
Net
work
,
Hea
d L
oss
es a
nd N
ou
n n
egat
ive
val
ue
Eval
uat
e th
e val
ues
eac
h d
iam
eter
of
pip
e fr
om
the
Haz
en-W
illi
ams
equat
ion (
look t
able
)
Cal
cula
te:
Outp
ut
Tota
l C
ost
of
Dri
p i
rrig
atio
n D
esig
n
Sta
rt N
ew D
esig
n?
N
Y
N
Y
12
3. DATA COLLECTION AND ANALYSIS
3.1-Location of the Study Area: The study is conducted in A/Gabar Farm which located in
the Northern part of State of Khartoum (Alkadaro), is located at eastern side of the River
Nile and at 13km north Khartoum (Bahri).It lies between latitudes 15º 37´ 40" and longitude
32º 31´51".
3.2-Drip System in Abd elgabar Farm: The first numerical case study is A/Gabar Farm which
consist of a2-branch system with 6 draw-off points along each branch (Fig 1).A/Gabar Farm
Input Data includes:
a- Well and Tank: The drip irrigation system under study was applied with water from
a well in the farm, through storage tank. Then pumped into a fish pond of capacity of
2890 m3.
b- Pump unit: A centrifugal pump operated by electric motor (7.5 kW), was used to
draw the irrigation water from the storage tank to supply the system. This setup gave
pressure of 3 bars in the main line.
c- Control unit: the control unit consist of the following:
1. Discharge valve to control the water follow in the system.
2. Pressure-reducing valve to control the pressure in the system.
3. Cleaning or flushing valve.
d- Filtration system: The water was conveyed from the fish pond by 75 mm (3")
diameter, pipe and then paned through two sand filters.
e- Fertilizer unit: Fertilizer and chemical injectors were incorporated with the drip
system to supply fertilizers. Herbicides, insecticides, fungicides, trace elements,
nutrient solution and acid at frequent or nearly continuous application with the
irrigation water.
f- The main line: the main pipe line was mad of polyvinyl chloride (PVC). It was 240 m
long and 75 mm (3") in diameter.
g- Sub main line: the sub-main pipe was also made of polyvinyl chloride (PVC) the sub-
main line was 240 m and 63 mm( 2.5") in diameter
h- The lateral lines: the lateral pipes were made of black linear low density
polyethylene (LLDPE). There were 80 laterals, each 40 m long and 16 mm inside
diameter. Laterals were joined to the sub main at 1 m spacing.
i- Emitters (drippers): Emitter with 40 cm spacing along the laterals, each with
average discharge of 1.08 I/h.
13
Figure 2: Schematic diagram for case one: A/Gabar Farm.
The following data was collected from the farm:
(1) The dimensions of the field, F� (m) and F� (m);
(2) The depth of the water table H� (m);
(3) The potential evapotranspiration, ET� (mm/day), the crop coefficient, K�;
(4) The minimum and maximum percentage of wetted area, P, (%);
Water
Source
Pum
p Filte
rs
Magneti
c
23 m 87 m
2.3
m
40 m
3 in
1.5 in
3 in
2.5
in
14
(5) The application efficiency of drip irrigation, E� (%);
(6) The annual irrigation requirement for the crop, A��, (mm);
(7) The field capacity, FC and the permanent wilting point PWP, of soil;
(8) The depth of root zone, R, (m), soil infiltration rate, I���� (mm/hr) and soil bulk
density γ� (g/cm�);
(9) The portion of the available moisture depletion f (%);
(10) The spacing between emitters, d�, and laterals, d�, respectively (m);
(11) The pipe cost coefficients k�,k ,k� �; the pump, cost parameters k, a, b;
(12) Efficiencies for the electric motor, η�, and pump, η", respectively;
(13) The discount rate, i , and expected project life, n, (years);
3.3-Climate: The study site is within the semi-desert it receives rain fall about(150-
170mm/year),The seasonality and variability both characterize the rainfall in time and space
.Generally in January the average temperature rises from (14cº) at dawn to (30cº) in after
noon, while in May the hottest month it rises from (25cº to 42cº) rainfall start in(June - July),
and may continue up to September in dry years, Winter is know with it is prevailing strong
northerly wind, which causes serious sand and dusty storms. Meteorological data reported
by Khartoum North Meteorological Station at Shambat ,concerning precipitation, P (mm)
and weather data (maximum and minimum temperature, rainfall, wind speed, bright
sunshine hours and relative humidity were taken for the period of 30 years (1961 – 2006)) is
used to compute reference evapotranspiration, ETo (mm), using FAO Penman-Monteith
methodology described by James (1988).
3.4-Soil: The soil is sandy -clay to clay. Soil moisture is one of the most limiting factors in the
area. The soil of study area is predominantly Aridisols with pockets of Vertisols formed on
old alluvium deposits and Entisols on recent alluvium and Aeolian deposits .Most of the soils
of the site are salt-affected (Ali et al 2009).
The soil of A/Gabar farm can be described according to United State Department of
Agriculture Soil Classification Chart as sandy clay loam soil. The soil is alkaline with 7.8 pH,
and characterized with low water holding capacity (36% moisture at field capacity, 26 %
permanent wilting point on volume basis and 1.3 gm/cm^3 bulk density. The measured and
collected input data is as follows:
3.5-Soil mechanical analysis: Two locations were randomly selected to represent the soil
under study. Three soil samples were taken from each location at depths 0-30, 30-60, 60-90
cm. Soil texture was determined using the hydrometer method as described by Blake (1965).
Chemical analysis: Two samples of water were taken to study their chemical properties.
15
3.6-Infiltration characteristics: Three representative sites were selected for measuring
infiltration rate using the double ring infiltrometer as described by James (1988).The average
initial infiltration rate is 12.3 cm/h and the final rate is 1.8 cm/h. The relation between intake
rate and elapse time can be approximated by the power relation of the form:
Y = 12.48X ^ 0.84 ……………………………………………...…………….. (8)
Where: y = infiltration rate and X = time in minutes. According to James (1988) the high final
intake rate values exhibited by the soil indicates that the farm is more suitable to be
irrigated by drip irrigation than by other surface methods.
3.7-Determination of crop water requirement (CWR): Crop water requirements are usually
expressed in units of water volume per unit land area (m3/ha), depth per unit time
(mm/day). Crop water requirement, which is equal to crop evapotranspiration, is estimation
according to the following equation (Jensen, 1983):
Etc = ETo x Kc x Kr -------------------------------------------------------------------------------- (9)
Where:
ETc = Crop evapotranspiration (mm / day).
ETo = Reference crop evapotranspriration (mm/day).
Kc = Crop coefficient.
Kr = Reduction coefficient
The crop water requirement for each month is calculated using the following equation:
CWR = Etc x days of the month………………………………………………… (10)
Where: ETc = Crop water requirement (mm/day).
The net crop water requirement (NCWR): The net crop water requirement was calculated by
subtracting the monthly effective rainfall (ERF) as:
NCWR = CWR – ERF …………………………………….……………………………….……… (11)
The effective monthly rainfall (EFR, mm) was calculated from the total rainfall (TRF, mm)
according to the USDA soil conservation service empirical relationships.
3.8-The uniformity of the drip system: Field data was collected from the drip system
installed at A/Gabar Farm (Figure 2). The discharge from 70 emitters (randomly selected)
was used to test the uniformity of the system. The uniformity of the system (Eu%) was then
calculated using the following formula:
Eu% = 100#$
#%&' -------------------------------------------------------------------------------------- (12)
3.9-Crop water use efficiency: The water utilization by the crop is generally described by the
following formula (Karmeli et al, 1968):
WUE (kg/halm3) = Crop yield (kg/ha)/ water supply (m3) ---------------------------------- (13)
16
Measurement of water discharge in the drip system: Measurements were taken from 14
laterals using catch cans, a measuring cylinder and a stop watch. The pressure was adjusted
at 1bar over all laterals, and was replicated at least three times for each emitter. This
application was done every 0, 10, 20, 30, 40 meters along the lateral lines, one hour after
the system operation.
3.10-Measurement of water discharge in the drip system of A/Gabar Farm.: Measurements
were taken from 14 laterals using catch cans, a measuring cylinder and a stop watch. The
pressure was adjusted at 1bar over all laterals, and was replicated at least three times for
each emitter. This application was done every 0, 10, 20, 30, 40 meters along the lateral lines,
one hour after the system operation. The collected data was then expressed by a linear
regression as described by Gomez and Gomez (1984).
3.11-Summary of Farm Input Data: The input data collected from A/Gabar farm is
summarized in table 1, 2.3, 4 and 5.
Table 1: Summary of Farm Input Data
No. Particulars Unit Farm Data
1. Nominal Discharge of Emitter lit/hr 4.00
2. Soil Saturated Hydraulic Conductivity mm/hr 25
3. Initial Soil Moisture Content % 14.00
4. Final Soil Moisture Content % 35.00
5. Wetted Depth m 1.50
6. Chose Soil Type 5.70
7. Distance Between Trees m 0.4x1
8. Max. Daily Crop Water Req. mm/day 5
9. Diameter Of Shading m 0.4
10. Irrigation Efficiency % 85
11. Percent Of Ground Cover % 85
12. Coefficient Of Emitter Equation -- 0.855
13. Exponent Of Emitter Equation -- 0.67
14. Length Of Last Lateral m 40
15. Length Of Last Manifold m 40
16. Length Of Last Sub Main m 327
17. Allowable Irrigation Time hr 4
18. No. of Plants Rows/Manifold No 40
19. No. of Plants/Lateral No 100
20. Distance of First Emitter Full Space
21. Lateral Layout One Side
22. Manifold Layout One Side
23. Available Size Of Lateral (Internal Diameter) mm 13.6
24. Distance Of First Lateral Full Space
25. Available Size Of Manifold (Internal Diameter) mm 46.4
26. Available Size Of Sub Main (Internal Diameter) mm 84.6
27. Number of Manifold / Sub Main Mo 6
28. Number of Sub Main / Mainline No 1
29. Available Size Of Mainline (Internal Diameter) mm 84.6
30. Length Of Mainline m 23
31. Static Suction Head m 0
32. Net Positive Suction Head m 4
17
33. Head Losses in Control Head m 15
34. Pump Efficiency % 35
35. Engine Efficiency % 65
Table 2: Input Data of A/Gabar Farm for LP optimization Model
Link 12 D Q K* 108
C Q(lit/sec) J (m/m) FL (m)
Length (m) 121 101.6 28.236 121 150 7.8 0.00854 0.19642
23 122 76.2 28.236 121 150 7.8 0.03465 0.79695
123 63.5 28.236 1121 150 7.8 0.0842 1.9366
Link 23 D Q K C Q(lit/sec) J (m/m) FL (m)
Length (m) 231 101.6 23.53 121 150 6.5 0.00609 0.2436
40 232 76.2 23.53 121 150 6.5 0.02472 0.9888
233 63.5 23.53 121 150 6.5 0.06007 2.4028
Link 34 D Q K C Q(lit/sec) J (m/m) FL (m)
Length (m) 341 101.6 18.824 121 150 5.2 0.00403 0.1612
40 342 76.2 18.824 121 150 5.2 0.01635 0.654
343 63.5 18.824 121 150 5.2 0.03974 1.5896
Link 45 D Q K C Q(lit/sec) J (m/m) FL (m)
Length (m) 451 101.6 14.118 121 150 3.9 0.00236 0.0944
40 452 76.2 14.118 121 150 3.9 0.0096 0.384
453 63.5 14.118 121 150 3.9 0.02332 0.9328
Link 56 D Q K C Q(lit/sec) J (m/m) FL (m)
Length (m) 561 76.2 9.412 121 150 2.6 0.00453 0.1812
40 562 63.5 9.412 121 150 2.6 0.01101 0.4404
563 50.8 9.412 121 150 2.6 0.03263 1.3052
Link 67 D Q K C Q(lit/sec) J (m/m) FL (m)
Length (m) 671 76.2 4.706 121 150 1.3 0.00125 0.05
40 672 63.5 4.706 121 150 1.3 0.00305 0.122
673 50.8 4.706 121 150 1.3 0.00904 0.3616
Link 28 D Q K C Q(lit/sec) J (m/m) FL (m)
Length (m) 281 101.6 28.236 121 150 7.8 0.00854 0.74298
87 282 76.2 28.236 121 150 7.8 0.03465 3.01455
283 63.5 28.236 121 150 7.8 0.0842 7.3254
Link 89 D Q K C Q(lit/sec) J (m/m) FL (m)
Length (m) 891 101.6 23.53 121 150 6.5 0.00609 0.2436
40 892 76.2 23.53 121 150 6.5 0.02472 0.9888
893 63.5 23.53 121 150 6.5 0.06007 2.4028
Link 910 D Q K C Q(lit/sec) J (m/m) FL (m)
Length (m) 9101 101.6 18.824 121 150 5.2 0.00403 0.1612
40 9102 76.2 18.824 121 150 5.2 0.01635 0.654
9103 63.5 18.824 121 150 5.2 0.03974 1.5896
Link 1011 D Q K C Q(lit/sec) J (m/m) FL (m)
Length (m) 10111 101.6 14.118 121 150 3.9 0.00236 0.0944
40 10112 76.2 14.118 121 150 3.9 0.0096 0.384
10113 63.5 14.118 121 150 3.9 0.02332 0.9328
Link 1112 D Q K C Q(lit/sec) J (m/m) FL (m)
Length (m) 11121 76.2 9.412 121 150 2.6 0.00453 0.1812
40 11122 63.5 9.412 121 150 2.6 0.01101 0.4404
11123 50.8 9.412 121 150 2.6 0.03263 1.3052
18
Link 1213 D Q K C Q(lit/sec) J (m/m) FL (m)
Length (m) 12131 76.2 4.706 121 150 1.3 0.00125 0.05
40 12132 63.5 4.706 121 150 1.3 0.00305 0.122
12133 50.8 4.706 121 150 1.3 0.00904 0.3616
Table 3: The elevation of irrigation system (A/Gabar Farm
Point Elevation
Proposed
Elevation m383
1 0.253 383.253 m
2 1.52 384.52 m
3 1.46 384.46 m
4 1.49 384.49 m
5 1.51 384.51 m
6 1.52 384.52 m
7 1.6 384.6 m
8 1.58 384.58 m
9 1.53 384.53 m
10 1.57 384.57 m
11 1.6 384.6 m
12 1.61 384.61 m
13 1.63 384.63 m
Price Int. Diam. Ex. Diam. (mm)
Ex. Diam.
(Inch)
7 101.6 4
5 76.2 3
4 63.5 2.5
3 50.8 2
2.5 25.4 1
Table 4: The head losses of drip irrigation system (A/Gabar Farm)
Item Value Unit
Average Operating Head of Emitter: 0.600 m
Total Head Losses in Lateral 0.030 m
Friction Losses in Manifold 0.199 m
Head Losses in Submain 6.960 m
Head Losses in Main 0.488 m
Minor Losses in Submain 1.390 m
Minor Losses in Main 0.098 m
Static Suction Head 0.000 m
NPSHR 4.000 m
Head Losses in Control 15.000 m
Difference in elevation between Pump and Highest Point in Main Line 1.327 m
Total Dynamic Head of Pump 28.705 m
Table 5: The head required at nodes (A/Gabar Farm)
Item Value Unit
Head required at node 1 28.705 m
Head required at node 2 13.119 m
19
Head required at node 3 12.130 m
Head required at node 4 11.476 m
Head required at node 5 11.092 m
Head required at node 6 10.652 m
Head required at node 7 10.530 m
Head required at node 8 10.104 m
Head required at node 9 9.116 m
Head required at node 10 8.462 m
Head required at node 11 8.078 m
Head required at node 12 7.637 m
Head required at node 13 7.515 m
3.11- Hypothetical case study- Karmeli, Peri and Todes Farm (Irrigation system design and
operation, 1985):
The schematic diagram for case two- Karmeli Farm is depicted in figure3.Data collected from
the farm includes: pipe length at each link, alternative diameters to use and their respective
costs-and shown in table6. The values of friction factors (J) are calculated for each diameter
of pipe from the Hazen Williams equation.
Figure 3: Schematic diagram for case two- Karmeli Farm
Table 6: Length of pipes at each link and pipe cost for Karmeli Hypothetical Farm
Link Length Candidate Diameter Pipe Cost
ij (m) 3 2 1 Diameter (mm)
Cost ($/m)
12 1000 500 450 400 100 16
23 1000 250 200 150 200 23
24 1000 450 400 350 250 32
45 1000 300 250 200 300 50
46 1000 450 400 350 350 60
67 1000 300 250 200 400 90
450 130
500 170
The values of friction factors (J) are calculated for each diameter of pipe using Hazen
Williams's equation. For example, for link 12, the values are as follows:
Candidate Diameter
Number
Diameter
(mm)
Q
(m3/hr)
J
(m/m)
NODE 1
ELEVATION.E1= 150 m
Water
Source
1 Pump
P =60 m
Q = 1120 m 3/hr
DISHARGE.d2 = 100 m3/hr d3 =100 m
3/ hr
E3 = 160
d4 = 120 m3/hr d5= 270 m3/hr
E5 = 150 m
d7 = 200 m3/hr d6 = 330 m
3/hr
E6 = 165 m E7 = 160 m
2 3
4 5
6 7
20
1 500 1120 0.00406 (J121)
2 450 1120 0.00678 (J122)
3 400 1120 0.01202 (J123)
3.10-Hydraulic Procedure for determining Pipe Diameters: The pipe diameters are
established using the allowed pressure variation in the system as a design parameter. The
general procedure for a given pipe involves first of all establishing a pressure envelope,
defined by the topographic elevations along the length of the pipe and the allowable
pressure variation within the pipe. The upper and lower limits of the envelope represent the
maximum and minimum allowable hydraulic grade lines respectively, along the pipe being
designed. Then, starting at the furthest end of the pipe with the smallest available diameter,
the pressure head in the pipe is calculated for points along its length, working back towards
its inlet. This pressure head will increase exponentially as the flow in the pipe increases
because more and more outlets are included along the length being considered. Considering
this curve in the other direction {i.e. in the direction of flow in the pipe), the exponential
shape represents the decreasing rate of head loss due to friction, per unit length, as the flow
in the pipe decreases. As soon as the actual hydraulic grade line for the diameter of pipe
being considered starts to rise steeply towards the upper limit of the allowed envelope, the
pipe is replaced by a larger diameter, thereby reducing the rate of pressure loss due to
friction. The process then continues until the inlet is reached. In this way a set of diameters
and their respective lengths are determined, such that the pressure variation in the lateral is
contained within the allowable limits (Karmeli et al, 1968).
3.12-Data Analysis: Statistical package for social sciences (SPSS) is used for analysis of
variance, regression, t-test, and Chi-squire test.
4. RESULTS AND DISCUSSIONS Model Application: Two case studies namely: Abd elgabar Farm (A/Gabar) and - Karmeli
Hypothetical Farm were investigated for purpose of model applications.
4.1- Abd elgabar Farm:
For purpose of model application to Abd elgabar Farm the LP problem is formulated as
shown in table 7.
Table7: Formulation of the LP problem for Abd elgabar Farm
21
Analysis of the input data as generated by QSB computer model is depicted in table 8.
Table 8: Results of analysis of linear optimization generated by using QSB - computer
program (A/Gabar Farm)
No. Constraint Left Hand Side Direction Right Hand Side Slack or Surplus Shadow Price
1 C1 390 >= 0 390 0
2 C2 610 >= 0 610 0
3 C3 0 >= 0 0 0
4 C4 0 >= 0 0 0
5 C5 331 >= 0 331 0
6 C6 669 >= 0 669 0
7 C7 1,000.00 >= 0 1,000.00 0
8 C8 0 >= 0 0 0
9 C9 0 >= 0 0 0
10 C10 0 >= 0 0 0
11 C11 518 >= 0 518 0
12 C12 482 >= 0 482 0
13 C13 0 >= 0 0 -57.1003
14 C14 1,000.00 >= 0 1,000.00 0
15 C15 0 >= 0 0 0
16 C16 126 >= 0 126 0
17 C17 874 >= 0 874 0
18 C18 0 >= 0 0 -20.8388
19 C19 1,000.00 = 1,000.00 0 127.3526
20 C20 1,000.00 = 1,000.00 0 16
21 C21 1,000.00 = 1,000.00 0 109.7519
22 C22 1,000.00 = 1,000.00 0 23
23 C23 1,000.00 = 1,000.00 0 77.9033
24 C24 1,000.00 = 1,000.00 0 47.1822
25 C25 53.5252 >= 30 23.5252 0
26 C26 40.0038 >= 40 0.0038 0
27 C27 48.3222 >= 35 13.3222 0
28 C28 30.0098 >= 30 0.0098 0
29 C29 45.0002 >= 45 0.0002 0
30 C30 40 >= 40 0 2,811.00
31 C31 59.9979 <= 60 0.0021 0
22
Application of linear programming optimization using QSB - computer program for A/ Gabar
farm is made using input data given in tables 1 to 5. The result is given in table 9 and
indicates that costs of all type of pipes are reduced significantly. This resulted in significant
reduction of total cost from 2390 to 1905 SDG.
Table 9: Significant Reduction of Total Cost (A/ Gabar Farm)
Parameter Cost of A/ Gabar Farm
Significance
Level Actual Model
Main Line Pipe 550 465.045 Sig
Sub main Pipe 1200 960 Sig
Lateral Pipe 640 480 Sig
Total Cost 2390 1905 Sig
4.2- Case Two: Karmeli Farm
When applying the model for the hypothetical farm of Karmeli the LP objective and
constraint are formulated as:
Minimize [K] = ∑ijCijmXijm for all ij e.g. ∑12 Cm X12 = 170 X121 + 130X122 + 90X123.
The constraints: 1- non-negativity: Xijm≥ 0 for all ij,m. 2- Length ∑mXijm = 1000 0 for all ij.
Head loss:
At node 2: 180 ≤ 210 - ( )� *+� **
At node 3: 190 ≤ 210 - ( ) �*+ �** − ( )� *+� **
At node 4: 185 ≤ 210 - ( ) .*+ .** − ( )� *+� **
At node 5: 180 ≤ 210 - ( )./*+./** − ( ) .*+ .** − ( )� *+� **
At node 6: 195 ≤ 210 - ( )./*+./** − ( ) .*+ .** − ( )� *+� **
At node 7: 190 ≤ 210 - ( J12�X12�� − ( J./�X./�� − ( J .�X .�� − ( J� �X� ��
Formulation the LP problem in typical QSB –model format is shown in table 10.
Table 10: Karmeli Farm LP Model Formulation
23
The results of analysis of linear optimization generated by using QSB - computer program for
Karmeli Farm is shown in table 11. The result indicates that the constraint for node 2 can be
left out because the constraint for node 3 will ensure that the node 2 constraint holds.
Similarly the constraint at node 6 ensures that the constraint at node 4 holds.
In the solution given above both links 12 and 24 have full lengths (1000 m) of only one
diameter. For link 12 this is the 450 mm diameter which was the middle candidate (m = 2)
for the link. Thus for this link the implicit constraint is not binding. However, for link 24 the
diameter chosen (450 mm) is for the candidate m = 1. In this case it is possible that the LP
wanted to look for possible diameters larger than 450 mm to get to a better optimum. In
order to eliminate the constraint we must re-run the LP with the candidate diameters for
link 24 changed to 500, 450 and 400 mm respectively.
Table 11: Results of analysis of linear optimization generated by using QSB - computer
program for Karmeli Farm
Combined Report for Karmeli 10% minor losses
Decision Solution Unit Cost or Total Reduced Basis
Variable Value Profit c(j) Contribution Cost Status
1 X121 390 170 66,300.00 56.3651 at bound
2 X122 610 130 79,300.00 23.7046 at bound
3 X123 0 90 0 0 basic
4 X231 0 32 0 16 at bound
24
5 X232 331 23 7,613.00 7 at bound
6 X233 669 16 10,704.00 0 basic
7 X341 1,000.00 130 130,000.00 34.8737 at bound
8 X342 0 90 0 6.2218 at bound
9 X343 0 60 0 0 basic
10 X1451 0 50 0 27 at bound
11 X452 518 32 16,576.00 9 at bound
12 X453 482 23 11,086.00 0 basic
13 X461 0 130 0 0 basic
14 X462 1,000.00 90 90,000.00 21.4349 at bound
15 X463 0 60 0 0 basic
16 X671 126 50 6,300.00 9.0582 at bound
17 X672 874 32 27,968.00 0 basic
18 X673 0 23 0 0 basic
19 MPX 59.9979 2,811.00 168,654.10 0 basic
20 X20 1 705.6 705.6 705.6 at bound
Objective Function (Min.) = 615,206.80
The overall results of analysis of linear optimization generated by using QSB - computer
program is given in table 12 .The results indicates that costs of all type of pipes is reduced
significantly and this resulted in significant reduction of total cost from 1235 to 649 SDG
given in Table 4.7. The results in Table 4.7 show that the increase in the cost of electricity is
associated with increase in pipe diameters but the relation is not linear. This case illustrates
the applicability of the analysis and software to handle a system with a large number of
draw-off points.
Table 12: Significant Reduction of Total Cost (Karmeli Farm)
Parameter Costs of Karmali farm Significant
Level Without optimization With LP optimization
Main Line Pipe 390 130 Sig
Sub main Pipe 560 370 Sig
Lateral Pipe 285 149 Sig
Total Cost 1235 649 Sig
5. CONCLUSIONS
The proposed model is based on the cost of piping system, pump and the energy consumed
to operate the system. The least annual cost principle is employed to determine the optimal
diameters of all piping segments.
Application of LP optimization model revels that there is significant reduction in the sizes of
main, sub main lines and lateral in all tested cases. This resulted in significant reduction in
total costs and improvement in the final designs.
25
The model is employed for a simple two parallel pipelines with 4000 emitters. A second case
study is also presented which considers the micro irrigated farm of Keramli et al (19187).It is
thus, highly recommended to apply the LP optimization module after hydraulic design for
purpose of reducing cost of pipes.
Practicability of the solution: Once the various iterative procedures and adjustments
described by the model have been carried out, and a satisfactory optimal solution has been
obtained, it should be checked for its practicability. For example, the solution may contain
segments for which the optimal length is too small to be practically significant, and these
should be eliminated in the final design specifications. The tendency in the past has been to
design irrigation networks with only one diameter pipe in each link. This will not normally be
the optimal design. In some cases, a particular link may be extremely long and the optimal
solution from the LP will be limited to specify only two segments of a different diameter
along its length. In this case it may be advantageous to specify a ‘dummy’ node at some
suitable point along the length of the link (e.g. at a sudden change of topography or at the
mid-point of the link).
6. REFERENCE
Ali M. S. M., Saeed A. B., and Mustafa M. A. (2009) Appraisal of spatial and temporal
variation of the soil moisture profile in the long furrow irrigation system in Kenana
Sugarcane Plantation. Journal of Science and Technology - Sudan University of Science and
Technology Vol.10 No.1 Jan pp 71-81.
Alperovits , E. and U. Dhamir, 1977, Design of optimal water distribution system. Water
Resources,13(6) 1977, pp 885-900.
Afshar A. and Miguel, A. M., 1989 Optimization Models for Wastewater Reuse in Irrigation, J.
Irrig. and Drainage Eng., 115, 2, pp 185-202 (1989).
Barragan, J., Bralts, V., Wu, I.P., 2006. Assessment of emission uniformity for micro-irrigation
design. Biosyst. Eng. 93 (1), 89–97.
Blake, G.R. (1965). Soil Bulk Density. In: Methods of Soil Analysis, Part 1. C.A. Black, D.D.
Evans, L.E. Ensminger, J.L. White and F.E. Clark (eds). No. 9 in the Series Agronomy.American
Society of Agronomy, Inc. Madison, Wisconsin, U.S.A.
Bralts, V.F., Edward, D.M., Wu, I.P., 1987. Drip irrigation design and evaluation based on the
statistical uniformity concept. In: Hillel, D. (Ed.), Advances in Irrigation, vol. 4. Academic
Press, New York, pp. 67–117.
Bralts, V.F., Kelly, S.F., Shayya, W.H., Segerlind, L.J., 1993. Finite element analysis of micro
irrigation hydraulics using a virtual emitter system. Trans. ASAE 36 (3), 717–725.
26
Cembrowicz, R. G., Ates, S. and Nguyen K. M.,1996 Mathematical Optimization of Main
Water Distribution System, City of Hanoi, Vietnam 6th Int. Conf. on Hydraulic Eng.
Software.Editor, Blain, W. R. Computational Mechanics Publications, Southampton, pp 163-
172 (1996).
Dandy, G. C., Simpson, A. R., and Murphy, L. J., 1996 An improved Genetic Algotithm for Pipe
Network Optimization, Water Resources Research, 32, 2, pp 449-458 (1996)
Dantzig, G. 1962. Linear programming and extension.Princeton University Press 1962.
Demir, V., Yurdem, H., Degirmecioglu, A., 2007. Development of prediction models for
friction losses in drip irrigation laterals equipped with integrated in-line and on-line emitters
using dimensional analysis. Biosyst. Eng. 96 (4), 617–631
Eduardo, A. H. and Marino, M. A.,1990 Drip Irrigation Nonlinear Optimization Model. J. Irrig.
and Drainage Eng., 116, 4, pp 479-495 (1990).
Evans, R.G., Wu, I.-P., Smajstrala, A.G., 2007.Micro irrigation systems. In: Hoffman, G.J.,
Evans, R.G., Jensen, M.E., Martin, D.L., Elliot, R.L. (Eds.), Design and Operation of Farm
Irrigation Systems.2nd edition. ASABE, St. Joseph, MI, pp. 632–683.
Gonc¸alves, J.M., Pereira, L.S., Fang, S.X., Dong, B., 2007.Modelling and multicriteria analysis
of water savingscenarios for an irrigation district in the Upper Yellow RiverBasin. Agric.
WaterManage. 94 (1–3), 93–108.
Haghighi, K., Bralts, V.F., Mohtar, R.H., Segerlind, L.J., 1989.Modelling
expansion/contraction, valve and booster pumpin hydraulics pipe network analysis: a finite
elementapproach. Trans. ASAE 32 (6), 1945–1953.
Hanson, B.R., Sˇ imu° nek, J., Hopmans, J.W., 2006. Evaluation ofurea–ammonium–nitrate
fertigation with drip irrigationusing numerical modelling. Agric. Water Manage. 86 (1–
2),102–113.
Kang, Y., Nishiyama, S., 1996. A simplified method for design ofmicro irrigation laterals.
Trans. ASAE 39 (5), 1681–1687.
Karmili, D., Peri, G., and Todes, M., 1987.Irrigation system design and operation.Oxford
University Press Cape Town 1985, pp 187.
Karmili, D., Gadish, Y., and Myers, S., 1987.Design of optimal water distribution networks
proceedings of the ASCE., 94(PLI) ,(1968); pp1-10.
Keller, J., Bliesner, R.D., 1990. Sprinkle and Trickle Irrigation.Van Nostrand Reinhold, New
York.
Li, J., Meng, Y., Li, B., 2007. Field evaluation of fertigationuniformity as affected by injector
type and manufacturingvariability of emitters. Irrig. Sci. 25 (2), 117–125.
27
Liu, Y., Teixeira, J.L., Zhang, H.J., Pereira, L.S., 1998. Modelvalidation and crop coefficients for
irrigation schedulingin the North China Plain. Agric. Water Manage. 36, 233–246.
Mermoud, A., Tamini, T.D., Yacouba, H., 2005. Impacts ofdifferent irrigation schedules on
the water balancecomponents of an onion crop in a semi-arid zone. Agric.Water Manage. 77
(1–3), 282–295.
Mohammad H. Afshar and EbrahimJabbari 2008 Simultaneous layout and pipe size
optimization of pipe networks using genetic algorithm The Arabian Journal for Science and
Engineering, Volume 33, Number 2B.
Mohtar, R. H., Bralts, V. F. and Shayya, W. H.,1991 A Finite Element Model for the Analysis
and Optimization of Pipe Networks.” Trans. Am. Soci. Of Agric. Engrs.34, 2, pp 393-401
(1991).
Oster, J.D., Wichelns, D., 2003. Economic and agronomic strategies to achieve sustainable
irrigation.Irrig. Sci. 22, 107–120.
Pedras, C.M.G., Pereira, L.S., 2008. Multi-criteria analysis for design of micro irrigation
systems.Application and sensitivity analysis.Agric. Water Mange. 96 (4), 702–710.
Pereira, L.S., Trout, T.J., 1999. Irrigation methods. In: Van Lier, H.N., Pereira, L.S., Steiner, F.R.
(Eds.), CIGR Handbook of Agricultural Engineering. Vol. I: Land and Water Engineering. ASAE,
St. Joseph, pp. 279–379.
Pereira, L.S., Oweis, T., Zairi, A., 2002.Irrigation management under water scarcity. Agric.
Water Manage. 57, 175–206.
Simpson, A. R., Dandy, G. C., and Murphy L. J., 1994 Genetic Algorithm Compared to Other
Techniques for Pipe Optimization, J. Water Resources, Planning and Management. Div.
American Soc. Civ. Eng., 120, 4, pp 423- 443 (1994)
Srinivasan, V. S. and Guimaraes, J. A. 1996. Criteria for the Economic Design of Sub-unit of a
Trickle Irrigation System, , 6th Int. Conf. on Hydraulic Eng. Software. Editor, Blain, W. R.
Computational Mechanics Publications, Southampton, pp 173-180 (1996).
Stephenson, D., 1981Pipelines Design for Water Engineers, in Developments in Water
Science, Vol.15, 2nd edition, Elsevier Sci., pp 34-52 (1981).
James, L.G. (1988). Principles of FarmIrrigation System Design. John Wiley & Sons, New
York, 543 pp.
Saldivia, L.A., Bralts, V.F., Shayya, W.H., Segerlind, L.J., 1990.Hydraulic analysis of sprinkler
irrigation systemcomponents using the finite element method. Trans. ASAE 33 (4), 1195–
1202.
28
Santos, F.L., 1996. Quality and maximum profit of industrialtomato as affected by
distribution uniformity of dripirrigation system. Irrig. Drain. Syst. 10, 281–294.
Saldivia, L.A., Bralts, V.F., Shayya, W.H., Segerlind, L.J., 1990. Hydraulic analysis of sprinkler
irrigation system components using the finite element method. Trans. ASAE33 (4), 1195–
1202.
Valiantzas, J.D., 1998. Analytical approach for direct drip lateral hydraulic calculation. J. Irrig.
Drain. Eng. 124 (6), 300–305.
Valiantzas, J.D., 2002. Hydraulic analysis and optimum design of multidiameter irrigation
laterals. J. Irrig. Drain. Eng. 128 (2), 78–86.
Valiantzas, J.D., 2003. Inlet pressure, energy cost, and economic design of tapered irrigation
sub main s. J. Irrig. Drain. Eng. 129 (2), 100–107.
Valiantzas, J.D., Dercas, N., Karantounias, G., 2007. Explicit optimum design of a simple
irrigation delivery system. Trans. ASABE 50 (2), 429–438.
Vincke, P., 1992. Multicriteria Decision-Aid. John Wiley & Sons, Chichester. Wichelns, D.,
Oster, J.D., 2006. Sustainable irrigation is necessary and achievable, but direct costs and
environmental impacts can be substantial. Agric. Water Manage. 86, 114–127.
Wu, I.P., Barragan, J., 2000. Design criteria for micro irrigation systems. Trans. ASAE 43 (5),
1145–1154
Wu, I.P., Gitlin, H.M., Solomon, K.H., Saruwatari, C.A., 1986.System design. In: Nakayama,
F.S., Bucks, D.A. (Eds.), Trickle Irrigation for Crop Production: Design, Operation and
Management. Elsevier, Netherlands, pp. 53–92.