Accepted Manuscript Research papers Exact solution of the Linear Parabolic Approximation for flow-depth based diffusive flow routing Luigi Cimorelli, Luca Cozzolino, Andrea D'Aniello, Domenico Pianese PII: DOI: Reference:
S0022-1694(18)30448-7 https://doi.org/10.1016/j.jhydrol.2018.06.026 HYDROL 22875
To appear in:
Journal of Hydrology
Received Date: Revised Date: Accepted Date:
19 February 2018 4 June 2018 11 June 2018
Please cite this article as: Cimorelli, L., Cozzolino, L., D'Aniello, A., Pianese, D., Exact solution of the Linear Parabolic Approximation for flow-depth based diffusive flow routing, Journal of Hydrology (2018), doi: https:// doi.org/10.1016/j.jhydrol.2018.06.026
This is a PDF file of an unedited manuscript that has been accepted for publication. As a service to our customers we are providing this early version of the manuscript. The manuscript will undergo copyediting, typesetting, and review of the resulting proof before it is published in its final form. Please note that during the production process errors may be discovered which could affect the content, and all legal disclaimers that apply to the journal pertain.
1
Exact solution of the Linear Parabolic Approximation for flow-depth based diffusive flow
2
routing
3
Luigi Cimorellia*, Luca Cozzolino b, Andrea D’Anielloa, Domenico Pianesea.
4 5 6
a
Department of Civil, Architectural and Environmental Engineering, Univ. of Naples Federico II.
7
b
Department of Engineering, Univ. of Naples Parthenope
8
*Corresponding author, mail to
[email protected]
9 10
Keywords: Diffusive wave; Analytical solution; Backwater effects; Boundary conditions; Channel routing;
11
Simplified model.
12 13
Abstract
14 15
The Linearized Parabolic Approximation of the Saint Venant Equations is often used for flood
16
routing, but the corresponding analytic solutions usually neglect the downstream boundary
17
conditions. This is an issue because the presence of hydraulic structures at the end of a river reach,
18
or natural morphologic conditions, may influence the wave propagation. In order to take into
19
account realistic boundary conditions, namely a stage-hydrograph upstream and a stage-discharge
20
relationship downstream, a new set of exact solutions of the Linearized Parabolic Approximation of
21
the Saint Venant Equations with uniformly distributed lateral inflows is presented. This exact
22
solution is demonstrated by using it as a building block in a simplified flood routing model, whose
23
numerical results are compared with those supplied by laboratory experiments from literature.
24
Finally, the new solutions are used to analyze the range of validity of semi-infinite channel models.
25
The comparison shows that semi-infinite channel models are accurate when convective effects are
26
prevailing on diffusive effects, and the downstream boundary condition corresponds to uniform flow
27
conditions. In addition, the results show that semi-infinite channel models based on the knowledge 1
28
of the upstream stage-hydrograph can predict flow depths better than those making use of a flow
29
hydrograph, while being practically equivalent in predicting flow rates.
30 31
1 Introduction
32
The Saint Venant Equations (SVEs) are commonly used for the description of one-dimensional
33
unsteady flow in rivers or artificial channel networks (Cunge et al. 1980). The exact solution of the
34
SVEs is available for schematic cases only, and appropriate numerical methods, such as the Finite
35
Difference method (Vukovic and Sopta 2003, Xing and Shu 2006), the Finite Element method
36
(Szymkiewicz 1991), and the Finite Volume method (Garcia-Navarro and Vazquez-Cendon 2001,
37
Liang and Marche 2009, Cozzolino et al. 2012), can be used for real world applications. Despite the
38
availability of reliable numerical procedures, the application of the full one-dimensional Saint-
39
Venant numerical models may suffer from a number of drawbacks, such as the lack of cross-section
40
topographic data, obtained by traditional ground or LiDAR surveys (Hutton et al. 2012), the
41
incorrect application of internal and external boundary conditions (Cunge et al. 1980, Sobey 2001),
42
the arbitrariness in the choice of cross-sections location and orientation, and the uncertainties of the
43
friction coefficients (Hunter et al. 2007). These practical issues may overshadow the advantage of
44
an accurate physical representation. In addition, the Courant-Friedrichs-Lewy restriction of the time
45
step in explicit time-marching numerical models (Murillo et al. 2006) may advice against the use of
46
the SVEs in the case of forecasting applications, control problems, and design applications
47
involving Monte Carlo approaches (Neal et al. 2012). To overcome these drawbacks, simplified
48
models are considered an attractive alternative to fully dynamic models (Hunter et al. 2007, Bates et
49
al. 2010, Cheviron and Moussa 2016).
50
The Parabolic Approximation (PA) is a non-linear simplification of the SVEs, obtained by
51
neglecting inertial terms, which are often negligible in practical hydrologic applications (Chow et
52
al. 1988, Kazezyılmaz-Alhan 2012). The PA model has been used in numerous applications, as
53
river flow propagation (Cappelaere 1997), flood events simulation (Moussa and Bacquillon 2009), 2
54
drainage systems simulation (Xu and Schwanenberg 2016), flow propagation with significant lateral
55
contributions (Spada et al. 2017), optimal design of rural drainage systems (Cimorelli et al. 2013a).
56
Moreover, the applicability limits of the non-linear model have been actively studied (Ponce and
57
Simons 1977, Ponce et al. 1978, Fread 1985, Ferrick 1985, Dooge and Napiorkowski 1987, Chung
58
et al. 1993, Moussa and Bocquillon 2000, Tsai 2003, 2005, Fan and Li 2006, Prestininzi 2008,
59
Cimorelli et al. 2014).
60
In practical cases requiring massive and fast calculations, the Linearized Parabolic
61
Approximation (LPA), obtained by linearization of the non-linear PA model, may help to reduce the
62
computational burden. The analytic solutions of the LPA model have been used as a building block
63
in numerous applications, such as non-linear flow routing with simplified backwater modelling
64
(Todini and Bossi 1986, Cimorelli at al. 2013b), multilinear approaches (Becker and Kundzewicz
65
1987, Perumal et al. 2008, Perumal et al. 2010), flow routing modeling in semi-distributed rainfall-
66
runoff model (Todini 1996, Moussa et al. 2007), flow routing in non-uniform channels by means of
67
a cascade of diffusive linear models (Cimorelli et al. 2015), propagation of the uncertainty (Chang
68
and Yeh 2016a,b), river flow modelling in karstic areas (Charlier et al. 2015a,b), optimal
69
management of small agricultural catchments (Colin et al. 2011), influence of rainfall spatial
70
variability on rainfall–runoff modelling (Emmanuel et al. 2015). The main advantage of analytical
71
solutions is the unconditional stability of the associated numerical models, thus allowing for long
72
time steps, especially when accuracy is not an issue (Wang et al. 2014). Interestingly, the LPA is
73
related to other widely used simplified models such as the Muskingum-Cunge (MC) model (Cunge
74
1969, Weinmann and Laurenson 1979), that can be transformed into an equivalent LPA by
75
matching physical and numerical diffusion (Cunge 1969), even though it was originally derived
76
from the Kinematic Wave simplification of the SVEs.
77
In the literature, many efforts have been spent to develop simplified stage-hydrograph
78
routing models because upstream gauge information is usually available in the form of stage-
79
hydrographs. This is also convenient because upstream flow-hydrograph boundary conditions 3
80
require the evaluation of the rating curve, which is often lacking or inaccurate (Spada et al. 2017).
81
Following this approach, physically based stage-hydrograph models, such has the variable
82
parameter Muskingum stage-hydrograph, are now available (Perumal and Ranga Raju 1998a,b,
83
Perumal et al. 2007, 2009, 2010a,b). Unfortunately, the analytic solutions of the LPA with stage-
84
hydrograph imposed upstream do not take into account downstream boundary conditions (see the
85
review in Cimorelli et al. 2014), and the semi-infinite channel analytic solution by Hayami (1951) is
86
usually assumed in practical applications. The only exception is the model by Tingsachali and
87
Manandhar (1985), whose applicability is limited because it is based on the knowledge of the
88
downstream stage-hydrograph. As pointed out by numerous authors (Chung et al. 1993, Munier et
89
al. 2008, Cimorelli et al. 2014, 2015, Cozzolino et al. 2014), structures or channel geometric
90
singularities (weirs, sluice gates, bridge piles), which influence the stage-discharge relationship
91
downstream, may significantly affect the flow dynamics. This makes the semi-infinite channel
92
solution by Hayami (1951) inadequate in many cases.
93
Therefore, it is clear that the construction of the LPA analytic solution in finite-length
94
channels, with stage-hydrograph upstream boundary condition and given rating curve imposed
95
downstream, is an attractive task. Following the approach used in Cimorelli et al. (2014) for the
96
case of discharge-hydrograph upstream boundary conditions, this analytical solution is supplied in
97
the present work by applying the Laplace transform technique. The findings are compared with the
98
experimental results of a laboratory test, showing the suitability of the finite-length channel
99
analytical solution in simplified flow routing models.
100
Only the flow depth response of the semi-infinite channel LPA, with stage-hydrograph
101
imposed upstream with lateral inflow, is available in the literature (Hayami 1951). For this reason,
102
this solution is complemented in the present work by the corresponding discharge response to the
103
stage-hydrograph imposed upstream with lateral inflow. This allows the comparison with the new
104
finite-length channel solution, in order to evaluate the applicability limits of the Hayami (1951)
105
solution. The results of this comparison are of interest not only for the LPA-based flow routing 4
106
models, but also for those MC models (Perumal and Ranga Raju 1998a,b, Perumal et al. 2007,
107
2009, 2010a,b) where a stage-hydrograph is considered upstream.
108
The paper is organized as follows: in Section 2, the novel finite-length channel analytical
109
solutions are presented; in Section 3, the complete semi-infinite channel solution is derived for
110
upstream stage-hydrograph and lateral inflow; in Section 4, the finite-length and the semi-infinite
111
channel analytical solutions are compared by considering the results of a laboratory experiment
112
from the literature; in Section 5, the applicability limits of the semi-infinite channel solution is
113
accomplished by comparing its unit-step response with that of the finite-length channel; finally, the
114
conclusions are drawn in Section 6.
115 116
2 Finite-length channel analytical solution with stage-hydrograph imposed upstream
117 118
In the present section, the LPA model is presented, and the corresponding analytic solution in finite-
119
length channels, with stage-hydrograph upstream boundary condition and given rating curve
120
imposed downstream, is derived.
121 122
2.1 LPA governing equations
123
The Parabolic Approximation (PA) of the Saint Venant Equations for a prismatic channel can be
124
written as (Cunge et al. 1980)
125
126
h Q B q x t h S S 0 0 f x
,
(1)
127 128
where Q(x,t) is the discharge, h(x,t) is the flow depth, B(x,h) is the channel width, S 0 x is the bed
129
slope, and S f Q, h, x is the friction-slope. If Eq. (1) is linearized around a uniform state 5
130
characterized by flow depth hr, discharge Qr, and width Br, the Linearized Parabolic Approximation
131
(LPA) is obtained. With reference to a channel of length L, the dimensionless form of the LPA
132
model is (Cimorelli et al. 2014, 2015)
133
134
Q* h* q* x* t * , * h r Q* r h* 0 1 2 x*
(2)
135 136
where
137 138
t * tC r L , x * x L , h* h' hr , Q* Q' Qr , q * qL Qr ,
(3)
139 140
are the dimensionless expressions of the time variable t, the space coordinate x, the first order flow
141
depth increment h’(x,t) = h(x,t) - hr , the first order discharge increment Q’(x,t) = Q(x,t) - Qr, and the
142
lateral inflow per unit of length q(x, t), respectively. The dimensionless coefficients appearing in
143
Eqs. (2) and (3) are defined as
144
145
Cr
1 Br
S f h S , hr Br C r , r1 L f Q S Q Qr f r
Qr S f L , r2 r hr h r
(4)
146 147
where the partial derivatives of the slope friction Sf are calculated with reference to the flow depth
148
hr, the discharge Qr, and the reference abscissa xr. The celerity Cr is related to the hydraulic
149
diffusivity coefficient
150 151
Dr
1
Br S f Q r
(5) 6
152 153
through the Pèclet number
154 155
Pe Cr L Dr ,
(6)
156 157
which expresses the relative importance of flow advection and diffusion. It is easy to see from (4)
158
and (5) that Pe = r1.
159 160
2.2 Finite-length channel general solution in the Laplace domain
161 162
The Laplace transform of Eq. (2) is
163
164
Q s h h0* q * x , h r Q r h 0 2 x * 1
(7)
165 166
where s is the complex Laplace variable, Qx* , s , h x* , s , and q x* , s , are the Laplace transforms
167
of Q* x* ,t * , h* x* ,t * , and q* x* ,t * , respectively, while h0* x * h * x * ,0 is the initial condition of
168
the first order flow depth increment. Under the assumption that the lateral inflow is uniform in
169
space and the initial condition h0* x * is null, the general solution of Eq. (7) is (Cimorelli et al.
170
2014)
171 172
Q x* , s * * x ,s h x , s
Q0, s * 1 x , s qˆ s , h 0, s
(8)
173 7
174
T T where Qx* , s h x* , s is the frequency domain solution vector, Q0, s h 0, s is the
175
frequency domain upstream boundary condition vector, and q (s) q ( x * , s) . In Eq. (8), the matrix
176 177
x* , s 12 x* , s x* , s 11 * * 21x , s 22 x , s
(9)
178 179
is the state-transition matrix, while x * , s 11 x * , s 11 x * , s is a vector taking into account
180
the lateral inflow contribution. The expressions of x* , s and x * , s are deduced in Cimorelli et
181
al. (2014) and are reported in the Appendix A of the present work for the reader’s ease.
T
182
The Eq. (8) represents the Laplace domain general solution of Eq. (7), and it must be
183
complemented with the correct boundary conditions and lateral inflows to obtain the desired
184
particular solutions.
185 186
2.3 Particular solutions with upstream stage-hydrograph and downstream stage-discharge function
187 188
A stage-hydrograph h0, t is assumed as upstream boundary condition, while the stage-discharge
189
relationship QL, t f SG hL, t is assumed downstream. In order to derive the analytical solution
190
of Eq. (7), the linearized dimensionless expressions of these boundary conditions are needed.
191
Upstream, the first order increment h' 0, t h0, t hr of the stage-hydrograph function is
192
considered, and the corresponding dimensionless form h* 0, t h' 0, t hr
193
obtained. Downstream, the stage-discharge relationship is linearized around the flow depth hr and is
194
then reduced in dimensionless form. The corresponding expression is
is immediately
195 196
Q* 1, t *
* * h 1, t ,
(10) 8
197 198
where the dimensionless abscissa x* = 1 corresponds to x = L. The parameter Br Cr k , where
199
k df SG hr dh , quantifies how much the downstream boundary conditions deviates from the
200
steady uniform flow along the channel. The Laplace transform of Eq. (10) finally leads to the
201
Laplace domain downstream boundary condition
202 203
Q 1, t * h 1, t * .
(11)
204 205
The substitution of Eq. (11) into Eq. (8) for x* = 1 supplies:
206 207
1, s 1 22 1, s 11 1, s 121 1, s Q0, s 12 h 0 , s q s . 11 1, s 1 21 1, s 11 1, s 1 21 1, s
(12)
208 209
The Eq. (12) represents the unique relationship between upstream flow depth and upstream
210
discharge that is compatible in a finite-length channel where Eq. (11) describes the downstream
211
boundary condition. The substitution of Eq. (12) into the first of Eq. (8) allows to eliminate Q0, s ,
212
leading to the flow depth response of a finite-length channel to a stage-hydrograph imposed
213
upstream, with lateral inflow contribution:
214 215
h x * , s wu x * , s h 0, s wl x * , s q s .
(13)
216 217
In Eq. (13), the function wu x * , s represents the flow-depth Laplace-domain response to an
218
upstream stage-hydrograph unit-pulse, while wl x * , s represents the flow-depth Laplace-domain
219
response to a lateral inflow unit-pulse. These functions are defined as: 9
220
221
wu x , s e *
Pe x* 2
1 x* 1 x* Pe 2 sinh Z Z cosh Z 2 2 , 1 1 Pe 2 sinh Z Z cosh Z 2 2
(14)
222
1 x* 1 x* Pe 2 sinh Z Z cosh Z 1 e 2 2 wl x * , s 1 1 s s Pe 2 sinh Z Z cosh Z 2 2
223
Pe x* 2
Pe x * 1 2
* 1 sinh x Z 2 Pe e 1 2 s 1 1 Pe 2 sinh Z Z cosh Z 2 2
,
(15)
224 225
where Z Pe 2 4Pe s .
226
In a similar manner, the substitution of Eq. (12) into the second of Eq. (8) leads to the
227
discharge response of a finite-length channel to a stage-hydrograph imposed upstream, with lateral
228
inflow contribution:
229 230
Qx * , s yu x * , s h 0, s yl x * , s q s .
(16)
231 232
In Eq. (16), yu x * , s is the Laplace-domain discharge-response to an upstream stage-
233
hydrograph unit-pulse, while yl x * , s is the response corresponding to a lateral inflow unit-pulse.
234
These functions are defined as:
235
10
236
y u x , s e *
Pe x * 2
1 x* 1 x* Pe 2s sinh Z Z cosh Z 2 2 , 1 1 Pe 2 sinh Z Z cosh Z 2 2
(17)
237
1 x* Z Z cosh Z 1 e 2 2 yl x * , s s s 1 1 Pe 2 sinh Z Z cosh Z 2 2 . * * x x * Pe x 1 Z Pe sinh Z Z cosh 1e 2 2 2 s 1 1 Pe 2 sinh Z Z cosh Z 2 2
238
Pe x * 2
Pe 2s sinh 1 x
*
(18)
239 240
The time domain expressions of Eqs. (14)-(15) and (17)-(18) are
241 242
(19)
(20)
(21)
(22)
wu x * , t * c1,n x * exp s n t * , n 0
243 244
wl x * , t * c2,n x * exp s n t * , n 0
245 246
yu x * , t * c3,n x * exp s n t * , n 0
247 248
yl x * , t * c4,n x * exp s n t * . n 0
249
11
250
where sn is the n-th pole of the corresponding Laplace-domain expression. The technique used to
251
obtain the coefficients ci ,n x * (i = 1,..,4; n = 0, 1, 2…) and to calculate the poles is described in
252
Appendix B.
253
The unit-step response, frequently used to discretize inputs of any shape by means of
254
rectangles (Chow et al., 1988; Wang et al., 2014), is defined as the primitive of the unit pulse
255
response. Therefore, the Laplace Transform Inversion theorem (Ahlfors 1979) can be used to show
256
that the unit-step responses corresponding to the unit-pulse responses of Eqs. (19)-(22) are:
257
258
* c e Pe 1e Pe x 1, n x Wu x , t wu x , d exp s n t * , Pe sn e 1 n 0 0
*
*
t*
t*
*
*
*
*
*
*
(23)
259
260
Wl x , t wl x , d *
*
*
0
x*
e
Pe x*
P 1 c x exp s t ,
1
e
e 1 Pe
n 0
*
2,n
*
n
sn
(24)
261 * c e P 3, n x Yu x , t y u x , d P exp s n t * , e 1 n 0 s n 0 t*
262
*
e
*
*
*
*
(25)
e
263
264
* 1 e Pe Pe 1 c 4,n x Yl x , t yl x , d x exp s n t * . Pe sn Pe e 1 n 0 0
*
*
t*
*
*
*
*
(26)
265 266
The Eqs. (23) and (25) represent the flow-depth and the discharge response, respectively, to
267
the stage-hydrograph unit-step input at the upstream end of the channel. Similarly, Eqs. (24) and
268
(26) represent the flow-depth and the discharge response, respectively, to the lateral-inflow unit-
269
step input when the upstream flow depth is given. The Eqs. (23)-(26) are valid under the condition
270
2 . If 2 , the hyperbolic sines at the denominators of Eqs. (14)-(15) and (17)-(18) vanish,
271
and the time domain solutions are simplified (see Appendix B). 12
272 273
Remark 1. It is important to note that the Eqs. (24) and (26) differ from the Eqs. (38) and
274
(36) in Cimorelli et al. (2014), that represent the flow-depth and discharge response, respectively, to
275
the lateral-inflow unit-step input when the upstream discharge is given. The expressions of Eqs.
276
(23)-(26) are totally new.
277 278 279
3 Analytical solution in semi-infinite channel with stage-hydrograph imposed upstream
280 281
The flow-depth response of Eq. (7) is already known in the semi-infinite channel when a stage-
282
hydrograph is imposed upstream (Hayami 1951). In particular, the function
283
284
*
Wu , x , t
*
x* t * 1 erfc * 2 4t
1 Pe x* x* t * Pe e erfc * 2 4t
Pe
(27)
285 286
represents the flow-depth response to the upstream stage-hydrograph unit-step input. The
287
corresponding discharge response is not available in the literature, and it is derived in the present-
288
section. First, the linearized parabolic rating curve is obtained from the second of Eq. (2):
289 290
Q * h*
h* . Pe x*
(28)
291 292 293
If the position h * x * , t * Wu , x * , t * is made in Eq. (27), and the Eq. (27) is substituted in Eq. (28), the expression
294
13
295
Yu ,
x t x* t * * x , t erfc Pe e 4t * 2 Pe t * 4t
*
*
*
* 2
Pe
(29)
296 297
Is obtained after the position Yu , x * , t * Q * x * , t * . The Eq. (29) represents the discharge response
298
to the stage-hydrograph unit-step imposed upstream.
299 300
The substitution of the second of Eq. (7) into the first supplies the following flow-depth advection-diffusion equation (Hayami 1951)
301 302
1 2 h* h* h* * * q* , 2 * Pe x x t
(30)
303 304
which formally coincides with the discharge advection-diffusion equation (ADE) by Cunge (1969).
305
For this reason, the solutions of Eq. (30) can be borrowed from the solutions of the discharge ADE
306
form. If the analytic derivation contained in Franchini and Todini (1988) is applied to Eq. (30), it
307
can be shown that the function
308
309
Wl , x * , t * t *
x* t * 1 * t x * erfc * 2 4t
1 x* t * * Pe t * x * e Pe x erfc * 2 4t
Pe
(31)
310 311
is the flow-depth response to the uniform lateral-inflow unit-step input in the semi-infinite channel
312
for given flow-depth imposed upstream. If the position h * x * , t * Wl , x * , t * is made in Eq. (31),
313
the substitution in Eq. (28) supplies the expression
314
14
*
Yl , x , t 315
*
* t x * e P x 2 Pe e
*
x t
* 2
x* t * * 1 * t t x erfc P e * 2 2 Pe 4t x* t * erfc Pe * 4t
t* e Pe
*
4t
*
Pe
*
(32)
316 317
which represents the discharge response to the unit-step uniform lateral inflow in the semi-infinite
318
channel for given flow-depth imposed upstream.
319 320 321
Remark 2. The discharge responses of Eqs. (29) and (32) are novel and complement the flow-depth responses of Eqs. (27) and (31), which are already available in the literature.
322 323 324
4. Numeric application of the finite-length and semi-infinite channel analytical solutions
325 326
A simple linear flood routing model, based on the analytic findings of the preceding sections, is
327
here presented. The flood routing model is then used to reproduce the results of a laboratory test
328
case from the literature.
329 330
4.1 A simple linear flood routing model
331 332
In the case of uniform linear channel, a simplified version of the ILTDFR model (Cimorelli et al.
333
2015)
334
I t * h * 0, t * h 0, t * hr hr be the dimensionless stage-hydrograph at the inlet of the channel.
335
This function is represented by the sequence of rectangular pulses
can
be
used
to
route
a
stage-hydrograph
336
15
imposed
upstream.
Let
337
1 Ik * t
kt *
I d k 1, 2, ... ,
(33)
k 1t *
338 339
where t * is the dimensionless time interval. The flow-depth response of the channel at the station
340
x* and time t n* nt * (n = 1, 2, …) is immediately calculated as
341 342
n
h * x * , t n* I k W x * , n k 1t * W x * , n k t * ,
(34)
k 1
343 344
where W x * , t * Wu x * , t * when the downstream boundary condition is taken into account, while
345
W x * , t * Wu , x * , t * whether the effect of the downstream boundary condition is neglected
346
(semi-infinite channel)
347 348
4.2 Numeric application
349 350
The linear model of Eq. (33) is applied to the experimental results by Rashid and Chaudrhy (1995).
351
The original experimental setup consisted of a flume, Lf = 21 m long, with uniform longitudinal bed
352
slope, compound rectangular cross-section (rectangular main channel with rectangular floodplains),
353
and Manning’s roughness coefficient dependent on the flow depth. An inclined sluice gate with bed
354
sill was present at the downstream end of the laboratory flume, and the corresponding stage-
355
discharge relation was expressed by
356 357
f SG h C h a , m
(35)
358
16
359
where a is the sill height. In Eq. (35), the constants C = 9.35 and m=1.14 were experimentally
360
determined by Rashid and Chaudhry (1995). Nine gauging stations were located at different
361
distances from the flume inlet (Table 1), and the actual channel length used in the computations is L
362
= 18.6 m, because the upstream boundary condition is given by the flow-depth record at the
363
Gauging Station 1. The geometric characteristics of the flume and the initial conditions of the
364
experiments are reported in Rashid and Chaudrhy (1995), and their complete description is not
365
repeated here.
366 367
[Insert Table 1 about here]
368 369
First, the model of Eq. (33) is applied with W x * , t * Wu x * , t * (finite-length channel
370
model) to the Test 1, where the flow occupies the entire compound cross-section. The parameters
371
(Pe, α, and β), needed for the calculation of the finite-length channel response function Wu x * ,t *
372
of Eq. (25), are evaluated with respect to the initial condition of Test 1, and no calibration is
373
performed. In particular, hr is computed as the average value of the initial backwater profile, Qr is
374
set equal to the initial discharge, and the reference conditions used for the downstream boundary
375
conditions are those corresponding to the reference discharge Qr. The results of the simulation with
376
time step t =10 s (thin continuous line) are compared in Figure 1 with the experimental results
377
(circles). From the figure, it is evident that the uniform linear channel model reproduces nicely the
378
flow-depth hydrograph at the Gauging Station 2 (Fig. 1a), which is close to the inlet, while the
379
essentials of the flow propagation phenomenon are captured at the Gauging Station 5 (Fig. 1b),
380
located at the middle of the channel. It is very important to observe that better results could be
381
obtained if a cascade of uniform diffusive channels were used, after a calibration of the parameters
382
(Cimorelli et. al. 2015).
17
383
In Figure 1, the results of a full Saint Venant finite-difference model by Rashid and
384
Chaudrhy (1995) are also reported. The comparison with the experimental results shows that the
385
parabolic linear model does not behave worse than the full Saint Venant equations. For this test
386
case, the discrepancy between the experimental results and the numerical results at the Gauging
387
Station 5 can be explained recalling that the cross-section is compound, with initial conditions
388
corresponding to more than 0.20 m of flow-depth in the main channel and less of 0.01 m of flow-
389
depth over the lateral floodplains.
390
The finite-length model is then applied to the Test 2, where the flow is entirely contained
391
into the main rectangular channel. The close inspection of Figure 2 shows that the uniform linear
392
channel model reproduces nicely the flow-depth hydrograph at both the Gauging Stations 2 (Fig.
393
2a) and 5 (Fig. 2b). The improvement of the numerical results can be explained recalling that now
394
the wetted area corresponds to a compact cross-section. In the same figure, the results of the
395
numerical model by Rashid and Chaudrhy (1995) are also reported. Again, the comparison shows
396
that the results supplied by the finite-length linear model are of comparable quality to those
397
supplied by the full Saint Venant model.
398 399
[Insert Figure 1 about here]
400
[Insert Figure 2 about here]
401 402 403
Tests
1
and
2
are
repeated
considering
the
semi-infinite
channel
model
404
W x * , t * Wu , x * , t * in Eq. (33). The results are represented in Figures 1 and 2, respectively, with
405
symbol. The comparison with the experimental results clearly shows that the semi-infinite channel
406
model behaves worse than the finite-length model.
407
18
408
5. Comparison between semi-infinite channel and finite-length channel analytical solutions
409 410
The findings of the previous section suggest that the finite-length channel analytical solutions are
411
more accurate than the semi-infinite channel analytical solutions in reproducing real flows.
412
Therefore, the applicability of the semi-infinite channel solutions is discussed by comparison with
413
the corresponding finite-length channel solutions. The analysis is accomplished considering the
414
unit-step responses, because these functions are used as a building block in practical numerical
415
methods where input hydrographs are represented by means of rectangular pulses sequences (Todini
416
and Bossi 1986, Chow et al. 1988, Cimorelli et al 2013b, 2015, 2016, Wang et al. 2014). Values of
417
Pe and representative of realistic situations are considered, while the constant = 1 is taken as
418
this coefficient is just a scaling factor. First, the dependence of the flow depth responses on Pe and
419
is commented, and finally the Nash-Sutcliffe Efficiency Index is used for an objective
420
comparison.
421 422
5.1 Flow-depth response to a unit-step stage-hydrograph imposed upstream
423 424
The Eqs. (23) and (27) represent the flow-depth responses of finite-length and semi-infinite
425
channels, respectively, to a unit-step stage-hydrograph imposed upstream. The functions are plotted
426
in the plane (t*, h*) of Figure 3 for different values of the parameters Pe (0.5, 2.5 and 5) and (0.5,
427
1, and 1.5), and at different locations x* (0.2, 0.4, 0.6, 0.8, 1). A continuous line is used for the
428
finite-length channel response, while a dashed line is used for the finite-length channel response.
429
First, the finite-length channel flow-depth response h* Wu x* , t * of Eq. (23) is considered.
430
The value 0.5 (panels in the left column of Figure 3) is representative of a downstream
431
boundary condition where a free fall or a critical flow depth occurs at the downstream end.
19
432
Congruently with the physical meaning of the downstream boundary condition, the flow depth
433
decreases with x* at a given t* , for every value of Pe.
434
For 1 (panels in the central column of Figure 3), as time increases, the flow-depth tends
435
asymptotically to h* 1 everywhere. This behavior is consistent with 1 being representative of
436
a normal depth downstream boundary condition.
437
The value 1.5 (panels in the right column of Figure 3), is representative of an obstacle
438
downstream, such as a sluice gate or a weir. In this case, the Eq. (23) exhibits a noticeable
439
backwater effect propagating from downstream with increasing t*. Correspondingly, h* Wu x* , t *
440
has a twisted behavior because the flow-depth decreases with x* for smaller values of t* (when the
441
wave entering upstream has not reached the downstream boundary condition), and increases with x *
442
for greater values of t* (because the wave is reflecting at the downstream boundary conditions).
443 444
[Insert Figure 3 about here]
445 446
The response h* Wu , x* , t * of Eq. (30) depends on Pe only, and not on . For this reason,
447
the corresponding plots in the left column of Figure 3 are equal to those of the central and the right
448
column, and no twisted behavior is exhibited. A closer inspection shows that lower values of Pe
449
cause a faster growth of h* Wu , x* , t * , but the asymptotic value of h* obtained for increasing t*
450
is not affected. In addition, h* decreases with x* at a given time t*.
451 452
4.2 Flow-depth response to a unit-step uniformly distributed lateral inflow
453 454
The functions h* Wl x* , t * of Eq. (24) and h* Wl x* , t * of Eq. (31) are plotted in the plane (t*,
455
h*) of Figure 4 with the same parameters Pe, , and x*, used for Figure 3. The finite-length channel
20
456
response to the lateral inflow is quite different from the response to the upstream stage-hydrograph.
457
When 0.5 (free fall condition at the downstream end), the time-asymptotic flow-depth value of
458
* * * h* Wl x* , t * increases from x 0 to a maximum in x 0.8 , and then decreases from x 0.8
459
to x * 1 . This differs from the case of h* Wu x* , t * in Figure 3, where the flow-depth is always
460
decreasing. When 1 (uniform flow at the downstream end), the time-asymptotic value of
461
h* Wl x* , t *
462
value h* = 1 at every cross-section. Finally, when 1.5 (sluice gate or weir at the downstream
463
end), h* Wl x* , t * increases regularly with x* at any instant t*, while h* Wu x* , t * exhibits a
464
twisted behavior.
increases along the channel, while h* Wu x* , t * exhibits the same asymptotic
465 466
[Insert Figure 4 about here]
467
468
The semi-infinite channel response h* Wl , x* , t * can reproduce the results of Eq. (24)
469
only for high values of Pe, and close to the upstream channel end. When Pe 5 , the two solutions
470
behave similarly for x* from 0.2 to 0.6, and for each value of . When Pe 2.5 , the two solutions
471
exhibit similar behaviors for x* from 0.2 to 0.4, and for 1. Finally, the plots of Eqs. (24) and
472
(31) are very different at any position along the channel and for any value of when Pe 0.5 .
473 474
4.3 Discharge response to a unit-step stage-hydrograph imposed upstream
475 476
The functions Q* Yu x* , t * of Eq. (25) and Q* Yu , x* , t * of Eq. (29), are plotted in the plane
477
(t*, Q*) of Figure 5 with the same parameters of Figures 3 and 4. From Figure 5, it is evident that
478
the function Q* Yu x* , t * exhibits a peak, originated at the channel inlet, that moves and decays 21
479
along the channel. Actually, when the inlet flow depth h* increases instantly from 0 to 1 (unit step
480
stage-hydrograph), the linearized looped rating curve of Eq. (28) prescribes that the derivative at the
481
right-hand side is a negative delta function. For this reason, the second term at the right-hand side of
482
Eq. (28) is a positive delta function that sums up with the first term (a unit step). For t > 0, this delta
483
function is convected and diffused along the channel, while the discharge entering upstream tends
484
to an asymptotic value that depends on h* and its space derivative. A closer inspection of Eq. (28)
485
shows that the inlet discharge peak weakens when Pe increases, and vanishes when Pe tends to
486
infinity, while the dependency on of the time-asymptotic discharge value decreases with Pe.
487 488
[Insert figure 5 about here]
489 490
The function Q* Yu , x* , t * of Eq. (29) is inadequate to mimic the finite-channel model
491
when Pe = 0.5. Conversely, the solution is well reproduced almost everywhere along the channel,
492
with exclusion of x* = 1, when Pe 5 . Finally, the correspondence between Eqs. (25) and Eq. (29)
493
is strongly influenced by when Pe 2.5 , but there is a reasonable correspondence for x * 0.6 .
494 495
4.4 Discharge response to unit-step lateral inflows.
496 497
A plot of the functions Q* Yl x* , t * of Eq. (26) and Q* Yl , x* , t * of Eq. (32) is
498
reported in Figure 6 with the same parameters considered in the preceding subsections. The
499
inspection of the figure shows that the infinite-length and semi-infinite channel solutions exhibit
500
negative discharges in the vicinities of x* = 0, for low values of Pe, when uniform lateral inflow is
501
imposed This feature can be easily explained recalling that Eqs. (26) and (32) are found under the
502
assumption h*(0, t*) = 0 for t* > 0, which allows the separation of effects from the case of a stage-
503
hydrograph boundary condition imposed upstream. According to Eq. (28), this implies that the 22
504
discharge Q* along the channel is negative when Pe h * h * x * . This is precisely what happens
505
for low values of Pe in the vicinities of x* = 0, where h* is small and h * x * 0 . Physically
506
speaking, the conditions in which these new solutions are derived can be representative of a water
507
body in the upstream cross section (a lake or the sea, a tank served by a pump) where the constant
508
level allows the lateral discharge injected along the channel to partly flow upstream. When a null or
509
positive discharge is expected at the upstream end, Eqs. (26) or (32) are not autonomous andmust be
510
complemented by a proper upstream stage-hydrograph. Interestingly, this also means that the
511
upstream stage-hydrograph cannot be assigned arbitrarily if lateral inflows are present. Therefore,
512
when the lateral inflow is the only input, the exact solution with discharge imposed upstream
513
(Cimorelli et al. 2014) should be preferred.
514 515
[Insert Figure 6 about here]
516 517
The Figure 6 shows that the function Q* Yl , x* , t * of Eq. (32) does not match the
518
function Q* Yl x* , t * of Eq. (26) for Pe 0.5 . When Pe 2.5 , the two solutions behave
519
qualitatively in a similar manner, but there are significant differences for 0.5 and 1 , while
520
the differences are small for 1.5 . For Pe 5 the results given by the two solutions are similar
521
except for the location x* 1 .
522 523 524
4.5 Backwater effect analysis
525 526
To establish the range of validity of the semi-infinite channel solutions presented in Section 3, the
527
Efficiency Index (NS) by Nash and Sutcliffe (1970)
528 23
f t f t NS 1 f t f I max
529
2
i 1 I max i 1
i
o
i
(36)
2
o
i
o
530 531
is used. In Eq. (36), f t i and f o t i are the approximating and the true function, respectively,
532
evaluated at the time instant ti (with i = 1, 2,..,Imax), while f o is the mean value of the true function.
533
The index NS ranges in ( , 1], where NS = 1 indicates a perfect match between the two models,
534
while NS 0 means that the prediction made by the approximating model has the same accuracy
535
of the time-averaged value of the true one. In this subsection, the values in x* = 1 of the semi-
536
infinite channel solutions are taken as the approximating models, while the step responses of Eqs.
537
(23)-(26) at the same abscissa are taken as the true models. All the computations are performed
538
considering Pe 0, 10 and 0, 3 . In the following, the interval NS > 0.7 is considered as
539
representative of a satisfactory matching (Moriasi et al., 2007).
540
The contour plot in Figure 7 represents the results of Eq. (36) when Eqs. (23) and (27) are
541
compared. It is evident from the figure that there is a region Pe , 1, 10 0.6, 1.4 where
542
h* Wu , x* , t * , (Eq. [27]) provides a good approximation of h* Wu , x* , t *
543
practical point of view, this is significant because the interval 0.6 1.3 is wide enough to
544
represent the downstream boundary conditions usually encountered in river applications. This result
545
is consistent with the numerical application of Section 4: in experiment 1, Pe = 1.04 and = 0.126,
546
while in experiment 2 Pe = 0.016 and =0.0124, and in both cases the semi-infinite solution failed
547
to reproduce the numerical experiment.
548
The outcomes are quite different (Figure 8) when h* Wl x* , t * (Eq. [24]) and h* Wl , x* , t *
549
(Eq. [31]) are compared, because in this case the region of validity of h* Wl , x* , t * is reduced to
550
Pe , 2, 10 1.1, 1.5.
551 24
(Eq. [23]). From a
552
[Insert Figure 7 about here]
553
[Insert Figure 8 about here]
554 555
The contour plot of Eq. (36), computed using
Q* Yu x* , t *
(Eq. [25]) and
556
Q* Yu , x* , t *
557
boundary condition, the discharge response Q* Yu , x* , t * matches the finite-length channel
558
response Q* Yu x* , t * better than the flow-depth response h* Wu , x* , t * matches the finite-
559
length model h* Wu x* , t * , because the area of validity starts from a point Pe , 0.5, 0.5 and
560
spreads up covering the whole range of considered at Pe 2 . Actually, the propagation of the
561
discharge by means of semi-infinite channels model seems more robust than the propagation of the
562
flow depth, which is greatly influenced by the downstream boundary condition. A similar
563
conclusion can be deduced by looking at the contour plot of Figure 10, where Eq. (36) is calculated
564
considering Q* Yl x* , t * (Eq. [26]) and Q* Yl , x* , t * (Eq. [32]).
(Eq. [29]), is depicted in Figure 9. Despite the use of the flow depth as upstream
565 566
[Insert Figure 9 about here]
567
[Insert Figure 10 about here]
568 569
5 Discussion
570 571
The exact solutions of Eq. (7) for the cases of finite-length and semi-infinite channels have been
572
systematically compared in Section 4, showing that the Péclet number Pe and the downstream
573
boundary condition coefficient are the parameters controlling the suitability of the semi-infinite
574
channel solutions. The lower values of Pe correspond to short channels, or to cases where diffusivity
25
575
effects are not negligible with respect to the convection effects. Conversely, the higher values of Pe
576
correspond to long channels or to cases where the convection effects are predominant.
577
Congruently with the physical interpretation of Pe, the comparison between the finite-length
578
and the semi-infinite channel solutions shows that the downstream boundary conditions cannot be
579
neglected when Pe is low, or is far from 1. Conversely, the use of the semi-infinite channel model
580
is reliable when Pe is high and is close to 1. In addition, the analysis has shown that the semi-
581
infinite channel model with flow depth imposed upstream predicts Q*(x*, t*) better than h*(x*, t*),
582
because the flow depth is more directly influenced by the downstream boundary condition, but the
583
range of validity of h*(x*, t*) is satisfactory for large Pe. These results can be compared with the
584
findings contained in Cimorelli et al. (2014), where the range of validity of semi-infinite channel
585
solutions was considered when discharge was imposed upstream. For that case, it was concluded
586
that the range of validity of semi-infinite channel models for the prediction of h*(x*, t*) was very
587
narrow, while the range of validity for the prediction of Q*(x*, t*) was larger.
588
In conclusion, semi-infinite channel models that use a stage-hydrograph as upstream
589
boundary condition are able to predict the flow depths better than the semi-infinite channel models
590
where the upstream flow hydrograph is routed, while minor differences are found when the
591
prediction of the discharge is considered. For this reason, semi-infinite channel models with stage-
592
hydrograph imposed upstream should be used when an accurate prediction of the flow depth is
593
required.
594
These conclusions are not limited to the LPA model only, since the downstream boundary
595
conditions are neglected in many of the approximate flood routing models that are used in the
596
hydrology practice. One of the most employed of these models is the MC model, which is
597
equivalent to the Advection Diffusion Equation (ADE) form of the LPA in semi-infinite channels if
598
its parameters are properly chosen (Cunge et al., 1969; Tang et al., 1999; Wang et al., 2006). For
599
this reason, the applicability limits studied here also supply useful indications about the range of
26
600
applicability of the MC model with a stage-hydrograph boundary condition (Perumal and Ranga
601
Raju 1998a,b, Perumal et al. 2007, 2009, 2010a,b).
602 603 604
5 Conclusions
605 606
A novel set of analytical solutions for the linearized parabolic approximation (LPA) of the SVE has
607
been derived in this paper, considering a stage-hydrograph upstream boundary condition, uniform
608
lateral inflows, and a stage-discharge relationship as downstream boundary condition. These
609
solutions are motivated by the fact that downstream boundary conditions (control structures,
610
obstructions such as bridge piles, sills, jumps) can modify significantly the flow dynamics. For
611
further comparison, these analytical solutions have been complemented by the corresponding
612
analytical solutions in the semi-infinite channel.
613
The numerical results of a numerical application have suggested that a simple flood routing
614
model equipped with the finite-length channel exact solution behaves better than the semi-infinite
615
channel solution in reproducing the experimental results obtained in a laboratory channel. This
616
finding has suggested a systematic comparison of finite-length and semi-infinite channel analytic
617
solutions, in order to analyze the applicability of the routing models based on the semi-infinite
618
channel length assumptions. From the comparison, it is evident that the downstream boundary
619
conditions can be neglected only when the Péclet number is high, and the downstream rating curve
620
is not far from a normal depth one. Conversely, the semi-infinite channel models should not be used
621
if the Péclet number is low. In addition, the finite-length channel analytic solutions have shown that
622
the upstream stage-hydrograph and the lateral inflows concur in determining the discharge at the
623
upstream end of the channel. In particular, this means that the upstream stage-hydrograph and the
624
lateral inflows cannot be assigned autonomously if the discharge upstream is assumed positive.
27
625
Finally, when the semi-infinite channel assumption is made in flood routing models, the use of a
626
stage-hydrograph upstream should be preferred for the calculation of flow depths.
627
The authors hope that these results will encourage researchers to develop simplified models
628
based on the imposition of a stage-hydrograph upstream, rather than a flow-hydrograph, possibly
629
accounting for the downstream boundary conditions.
630 631 632
Acknowledgements
633 634
This research was partially funded by the University of Naples Parthenope through the funding
635
programs “Sostegno alla Ricerca individuale 2015-2017” and "Ricerca competitiva triennio 2016-
636
2018".
637 638
Appendix A
639
The components of the state transition matrix x * , s are defined as (Cimorelli et al. 2014)
640
641
11x* , s
e
Pe x* 2
x* x* Z cosh Z P sinh Z , e Z 2 2
(A.1)
642
643
12 x* , s
Pe x* 2
2se Z
x* sinh Z , 2
(A.2)
x* sinh 2
(A.3)
644
645
21 x * , s
2 Pe e
Pe x * 2
Z
Z ,
646 28
647
22 x* , s
e
Pe x* 2
x* x* Z cosh Z P sinh Z , e Z 2 2
(A.4)
648 649
where the complex variable Z is introduced in Sub-section 2.3.
The components of the complex vector x * , s are defined as (Cimorelli et al. 2014)
650 651
652
11 x* , s
Pe x* 2
x 1 e Pe 2 Pe s sinh s sPe Z 2 2
*
Pe x* 2
e x* Z cosh Z , s 2
(A.5)
653
654
Pe x* 2
Pe x*
x* Pe 2 x* 1 e 21 x* , s cosh Z e sinh Z . s s 2 s Z 2
(A.6)
655 656 657
Appendix B
658
In order to find the time domain expressions of Eqs. (15)-(16) and (18)-(19), the inverse Laplace
659
formula
660 661
f t
1 f s e st ds 2i b
(B.1)
662 663
is used. In Eq. (B.1), f t is a generic function in the time domain, while f s is the corresponding
664
image in the Laplace complex domain. The integration contour b is a line parallel to the imaginary
665
axe, at the right of all the singularity of the function f s . It can be proven that Eqs. (15)-(16) and
666
(18)-(19) are analytic in the complex domain, with the exception of a countable set of singular
667
points that are called poles sn (n = 0, 1, 2…). For this reason, the Eq. (B.1) can be computed by 29
668
means of the residue theorem, which states that the integral at the right hand of Eq. (B.1) is equal to
669
the summation of residues at the singularities of f s times e st (Ahlfors, 1979):
670
671
f t res e st f s ; s s n .
(B.2)
n 0
672 673 674
Since the poles of the functions in Eqs. (15)-(16) and (18)-(19) are simple, the residues can be evaluated by means of
675 676
res e st f s ; s s n lim s s n f s e st .
(B.3)
s sn
677
When 2 , the application of Eqs. (B.2)-(B.3) to Eqs. (15)-(16) and (18)-(19) leads to the
678 679
expression of the coefficients that appear in the sums of Eqs. (20)-(23):
680
681
c1,n x * e
Pe x 2
*
Zn
1 x* 2
sin
Z
2 n
1 x* Z n Z n cos Z n 2 1 2 Pe cos Zn 2
(B.4)
682
683
684
c 2,n x *
e
Pe x * 2
Zn s n
1 x* 2
sin
1 x* Z n Z n cos 2
Z
2 n
P e x* Z n 2 Pe e 2 1 1 sin 2 1 2 Pe cos Zn 2
(B.5)
685
30
Z n ,
686
e
c 3, n x *
Pe x* 2
Zn
1 x* Z n Z n cos 2 2 1 2 Z n 2 Pe cos Zn 2
Pe 2s n sin 1 x
*
Z n ,
(B.6)
687
c 4,n x * 688
e
Pe x * 1 2
e
Pe x * 2
Zn s n
1 x* Z n Z n cos 2 2 1 2 Z n 2 Pe cos Zn 2
Pe 2s n sin 1 x
*
x Pe sin 1 Z n 2 s n 2
x* Z n Z n cos Zn 2 1 2 Pe cos Zn 2 *
Z
n
Z n
.
(B.7)
689
In Eqs. (B.4)-(B.7), Pe 2 1 1 and Z n 4 Pe sn Pe 2 , while the poles sn are the roots
690 691
of the transcendental equation (see Appendix C):
692 693
1 1 Pe 2 sin Z n Z n cos Zn 0 . 2 2
(B.8)
694 695
The Eqs. (B.4)-(B.7) are null for n 0 when 0 , while preserve their expressions when
696
2 0 . When 2 there is a pole in s Pe 4 , and the coefficients corresponding to n = 0
697
are defined by
698
699
e
Pe x* 2
Pe x* 1 2
c1,0 x
*
3x * , Pe
(B.9)
700
701
c 2, 0 x * e
Pe
P 1 e 2 6x* e Pe Pe
,
(B.10)
31
702
703
Pe x* 2
e
c3, 0 x
*
2 x* 1 , 2 Pe
3
(B.11)
704
705
c4,0 x * 3e
2 Px 1 e 2 x
Pe x* 1 2
Pe 2
*
Pe Pe
*
.
1
(B.12)
706 707
When 2 there is a pole for 0 s Pe 4 . In this case, the Eqs. (B.4)-(B.7) modify for
708
n 0 by exchanging the hyperbolic functions with their corresponding trigonometric functions, and
709
the minus sign is taken before Z n2 at the denominator. When 2 , the Eqs. (B4)-(B.7) must be replaced by:
710 711
712
e
c1,n x
*
2n 1 sin x * 2n 1
Pe x* 2
Pe
2
(B.13)
713
714
c 2,n
Pe x* 2
P e 2n 1 sin x * 2n 1 n 1 x (1) e 2 s n Pe 2
e
*
(B.14)
715
716
c3,n x *
e
Pe x* 2
2n 1 2n 1
2 Pe
Pe
2n 1 2n 1 cos x * sin x * 2 2
(B.15)
717
c 4,n x * 718
2 1
2e
Pe x* 2
2n 1 2n 1
2 2n 1 Pe
n 1
2
Pe x 1 2 *
2
Pe
2n 1 2n 1 cos x * sin x * 2 2
* 2n 1 2n 1 2n 1 cos x * Pe sin x 2 2 2n 1 Pe 2
e
2
2
32
.
(B.16)
719 720
Note that Eqs. (B.13)-(B.16) are identically null for n 0 .
721 722
Appendix C
723 724
Recalling the expression of Z defined in 3.1, the denominator of Eqs. (17)-(20) can be written as:
725 726
1 1 2 2 2 4 Pe s Pe 4 Pe s Pe cosh 4 Pe s Pe 2 2
sinh
(C.1)
727 728
with defined in Appendix B.
729
With the exception of few cases, the roots of Eq. (C.1) exist when the terms in the square root is
730
negative,
731 732
that
is,
when
s Pe 4 .
Reminding
that
sinh x i sin x
and
2 x cosh x i x cos x (with i 1 ), and making the position z 4 Pe s Pe , Eq. C.1
can be written as
733 734
1 iA sin z z 2
(C.2)
735 736
z where A z 2 2 and z arctan . Therefore, the poles correspond to the roots of the
737
equation
738 739
1 z z arctan n 2
(C.3)
740 33
741
with n N .
742
Attention should be paid to the following situations:
743
1. when 0 , the poles of Eqs. (17)-(20) are given by the roots of Eq. (C3) with n 1 and the
744 745
residuals by Eqs. (B.4)-(B.7); 2. when 0 the poles of Eqs. (17)-(20) are analytical and corresponds to
746 747
sn
2n 12 2 Pe 4 Pe
(C.4)
4
748 749 750 751 752 753
with n 1 , and the residuals are given by Eqs. (B.9)-(B.12); 3. when 2 0 , the poles of Eqs. (17)-(20) are given by the roots of Eq. (C.3) with n 0 and the residuals are still given by Eqs. (B.4)-(B.7); 4. when 2 there is a pole in sn Pe 4 , while the other poles are still given by the roots of Eq. (C.3) with n 1 ;
754
5. when 2 , there is a pole corresponding to the root of Eq. (C.1), in the interval
755
s Pe 4 ; 0, with residual given by modifying Eqs. (B.4)-(B.7) as specified in Appendix B,
756
while the other poles are still given by the roots of Eq. (C.3) with n 1 and residuals
757
corresponding to Eqs. (B.4)-(B.7).
758 759 760
References
761 762 763
Ahlfors LV. (1979) Complex analysis: an introduction to the theory of analytic functions of one complex variable. New York: McGraw-Hill.
34
764
Bates P.D., Horritt M.S., Fewtrell T.J. (2010) A simple inertial formulation fo the shallow
765
water equations for efficient two-dimensional flood inundation modelling, Journal of Hydrology
766
387, 33-45. DOI: 10.1016/j.jhydrol.2010.03.027.
767 768 769 770 771
Becker A, Kundzewicz ZW. (1987) Nonlinear flood routing with multilinear models. Water Resour Res; 23(6):1043–8. Cappelaere B. (1997) Accurate Diffusive Wave routing. ASCE Journal of Hydraulic Engineering 123(3), 174-181. DOI: 10.1061/(ASCE)0733-9429(1997)123:3(174). Chang C.M., Yeh H.D. (2016a) Probability density functions of the stream flow discharge in
772
linearized
773
10.1016/j.jhydrol.2016.10.033.
diffusion
wave
models.
Journal
of
Hydrology
543,
625-629.
DOI:
774
Chang C.M., Yeh H.D. (2016b) Stochastic modeling of variations in stream flow discharge
775
induced by random spatiotemporal fluctuations in lateral inflow rate. Stochastic Environmental
776
Research and Risk Assessment 30(6), 1635-1640. DOI: 10.1007/s00477-015-1170-x.
777
Charlier J. B., Moussa R., Bailly-Comte V., Desprats J.F., Ladouche B. (2015a). How Karst
778
Areas Amplify or Attenuate River Flood Peaks? A Response Using a Diffusive Wave Model with
779
Lateral Flows. In Hydrogeological and Environmental Investigations in Karst Systems (pp. 293-
780
301). Springer Berlin Heidelberg.
781
Charlier J. B., Moussa R., Bailly-Comte V., Danneville L., Desprats J.F., Ladouche B.,
782
Marchandise A. (2015b). Use of a flood-routing model to assess lateral flows in a karstic stream:
783
implications to the hydrogeological functioning of the Grands Causses area (Tarn River, Southern
784
France). Environmental Earth Sciences 74(12), 7605-7616. DOI: 10.1007/s12665-015-4704-0.
785
Cheviron B., Moussa R. (2016) Determinants of modelling choices for 1-D free-surface flow
786
and morphodynamics in hydrology and hydraulics: a review. Hydrology and Earth System Sciences
787
20, 1-32. DOI: 10.5194/hess-20-1-2016.
788
Chow VT, Maidment DR, Mays LW., (1988). Applied hydrology. McGraw-Hill.
35
789 790
Chung WH, Aldama AA, Smith JA., (1993). On the effects of downstream boundary conditions on diffusive flood routing. Adv Water Resour; 16:259–75.
791
Cimorelli L., Cozzolino L., Covelli C., Mucherino C., Palumbo A., Pianese D. (2013a)
792
Optimal design of rural drainage networks. ASCE Journal of Irrigation and Drainage Engineering
793
139(2), 137-144. DOI: 10.1061/(ASCE)IR.1943-4774.0000526.
794
Cimorelli L., Cozzolino L., Della Morte R., Pianese D. (2013b) An improved numerical
795
scheme for the approximate solution of the Parabolic Wave model. Journal of Hydroinformatics
796
15(3), 913-925. DOI: 10.2166/hydro.2013.130.
797
Cimorelli L., Cozzolino L., Della Morte R., Pianese D. (2014) Analytical solutions of the
798
linearized parabolic wave accounting for downstream boundary condition and uniform lateral
799
inflows. Advances in Water Resources 63, 57-76.
800
Cimorelli, L., Cozzolino, L., Della Morte, R., Pianese, D., & Singh, V. P. (2015) A new
801
frequency domain analytical solution of a cascade of diffusive channels for flood routing. Water
802
Resources Research, 51(4), 2393-2411.
803
Colin F., Guillome S., Tisseyre B. (2011) Small catchment agricultural management using
804
decision variables defined at catchment scale and a Fuzzy Rule-based system: a Mediterranean
805
vineyard case study. Water Resources Management 25(11), 2649-2668. DOI: 10.1007/s11269-011-
806
9831-0.
807
Cozzolino L., Della Morte R., Del Giudice G., Palumbo A., Pianese D. (2012) A well-
808
balanced spectral volume scheme with the wetting–drying property for the shallow-water equations.
809
Journal of Hydroinformatics, 14(3), 745-760.
810
Cozzolino, L., Cimorelli, L., Covelli, C., Della Morte, R., & Pianese, D. (2014). Boundary
811
conditions in finite volume schemes for the solution of shallow-water equations: The non-
812
submerged broad-crested weir. Journal of Hydroinformatics, 16(6), 1235-1249.
813 814
Cunge J.A, Holly F.M., Verwey A., (1980). Practical aspects of computational river hydraulics. Pitman, Boston. 36
815 816 817 818
Cunge, J.A. (1969). On the subject of a flood propagation computation method (Muskingum Method), IAHR Journal of Hydraulic Research 7(2), 205-230. Dooge J.C.I., Napiorkowski J.J. (1987). Applicability of diffusion analogy in flood routing. Acta Geophysica Polonica 35(1), 66-75.
819
Emmanuel I., Andrieu H., Leblois E., Janey N., Payrastre O. (2015) Influence of rainfall
820
spatial variability on rainfall–runoff modelling: Benefit of a simulation approach?. Journal of
821
Hydrology 531(Part 2), 337-348. DOI: 10.1016/j.jhydrol.2015.04.058.
822 823 824 825
Fan P, Li JC. (2006). Diffusive wave solutions for open channel flows with uniform and concentrated lateral inflow. Adv Water Resour;29(7):1000–19. Ferrick M.G. (1985) Analysis of river wave types, Water Resources Research 21(2), 209220. DOI: 10.1029/WR021i002p00209.
826
Todini, E., & Bossi, A. (1986). PAB (Parabolic and Backwater) an unconditionally stable
827
flood routing scheme particularly suited for real time forecasting and control. Journal of Hydraulic
828
Research, 24(5), 405-424.
829 830
Franchini, M., & Todini, E. (1988). PABL: A parabolic and backwater scheme with lateral inflow and outflow. In Fifth IAHR international symposium on stochastic hydraulics, Birmingham.
831
Fread D.L. (1985) Applicability criteria for kinematic and diffusion routing models,
832
Laboratory of Hydrology, National Weather Service, NOAA, U.S. Dept. of Commerce, Silver
833
Spring, Md.
834
Garcia-Navarro P., Vazquez-Cendon M.E. (2001) On numerical treatment of the source
835
terms in the shallow water equations, Computer & Fluids 29(8), 951-979. DOI: 10.1016/S0045-
836
7930(99)00038-9.
837
Hayami S. (1951). On the propagation of flood waves. Disaster Prev Res Inst Bull; 1:1–16.
838
Hunter N.M., Bates P.D., Horritt M.S., Wilson M.D. (2007) Simple spatially-distributed
839
models for predicting flood inundation: A review. Geomorphology 90(3-4), 208-225. DOI:
840
10.1016/j.geomorph.2006.10.021. 37
Kazezyılmaz-Alhan, C.M., (2012). An improved solution for diffusion waves to overland
841 842
flow. Appl. Math. Model. 36 (9), 4165–4172.
843
Liang Q., Marche F. (2009) Numerical resolution of well-balanced shallow water equations
844
with
845
10.1016/j.advwatres.2009.02.010.
complex
source
terms,
Advances
in
Water
Resources
32(6),
873-884.
DOI:
846
Moriasi, D. N., Arnold, J. G., Van Liew, M. W., Bingner, R. L., Harmel, R. D., & Veith, T.
847
L. (2007). Model evaluation guidelines for systematic quantification of accuracy in watershed
848
simulations. Transactions of the ASABE, 50(3), 885-900.
849 850 851 852
Moussa R. (1996) Analytical Hayami solution for the diffusive wave flood routing problem with lateral inflow. Hydrol Process; 10:1209–27. Moussa, R., Bocquillon, C. (2009). On the use of the diffusive wave for modelling extreme flood events with overbank flow in the floodplain. Journal of Hydrology, 374(1), 116-135.
853
Moussa R., Chahinian N., Bocquillon C. (2007) Distributed hydrological modelling of a
854
Mediterranean mountainous catchment – Model construction and multi-site validation. Journal of
855
Hydrology 337(1-2), 35-51. DOI: 10.1016/j.jhydrol.2007.01.028.
856 857
Munier S, Litrico X, Belaud G, Malaterre PO. (2008). Distributed approximation of openchannel flow routing accounting for backwater effects. Adv Water Resour;31(12):1590–602.
858
Murillo J., Garcìa-Navarro P., Brufau P., Burguete J. (2006) Extension of an explicit finite
859
volume method to large time steps (CFL>1): application to shallow water flows. International
860
Journal of Numerical Methods in Fluids 50(1), 63-102. DOI: 10.1002/fld.1036.
861 862
Nash, J. E. and J. V. Sutcliffe (1970). River flow forecasting through conceptual models part I - A discussion of principles, Journal of Hydrology.
863
Neal J., Villanueva I., wright N., Willis T., Fewtrell T., Bates P. (2012) How much physical
864
complexity is needed to model flood inundation?, Hydrological processes 26(15), 2264-2282. DOI:
865
10.1102/hyp.8339.
38
866 867 868 869
Perumal M, Ranga Raju KG (1998a). Variable parameter stage-hydrograph routing method: II. Evaluation. J Hydrol Eng ASCE 3(2):115–121 Perumal M, Ranga Raju KG (1998b). Variable parameter stage-hydrograph routing method: I. Theory. J Hydrol Eng ASCE 3(2):109–114
870
Perumal M, Moramarco T, Sahoo B, Barbetta S (2007). A methodology for discharge
871
estimation and rating curve development at ungauged river sites. Water Resour Res W02412
872
43(2):1–22. doi:10.1029/2005WR004609.
873
Perumal M., Moramarco T., Sahoo B., Barbetta S. (2008) Multilinear Diffusion Analogy
874
Model for Real-Time Streamflow Routing. 9th International Congress on Environmental Modelling
875
and Software. 3. https://scholarsarchive.byu.edu/iemssconference/2008/all/3.
876
Perumal M, Moramarco T, Sahoo B, Barbetta S (2010a). On the practical applicability of the
877
VPMS routing method for rating curve development at ungauged river sites. Water Resources
878
Research 46(3), W03522. doi: 10.1029/2009WR008103.
879
Perumal M., Moramarco T., Sahoo B., Barbetta S., Melone F. (2010b) Multilinear Diffusion
880
Analogy Model for Stage Hydrograph Routing. 9th International Congress on Environmental
881
Modelling and Software. 508. https://scholarsarchive.byu.edu/iemssconference/2010/all/508.
882
Perumal M, Sahoo B, Moramarco T, Barbetta S (2009). Multilinear Muskingum method for
883
stage-hydrograph routing in compound channels. J Hydrol Eng ASCE 14(7):663–670.
884
doi:10.1061/(ASCE)HE.1943-5584.0000029.
885 886 887 888
Ponce V.M., Simons D.B. (1977) Shallow wave propagation in open channel flow, ASCE Journal of the Hydraulic Division 103(HY12), 1461-1476. Ponce V.M., Li R.-M., Simons D.B. (1978) Applicability of kinematic and diffusion models, ASCE Journal of the Hydraulic Division 104(HY3), 353-360.
889
Prestininzi P. (2008) Suitability of the diffusive model for dam break simulation:
890
Application to a CADAM experiment, Journal of Hydrology 361(1-2), 172-185. DOI:
891
10.1016/j.jhydrol.2008.07.050. 39
892 893
Rashid, R. M., & Chaudhry, M. H. (1995). Flood routing in channels with flood plains. Journal of Hydrology, 171(1-2), 75-91. DOI: doi.org/10.1016/0022-1694(95)02693-J
894
Sobey R.J. (2001) Evaluation of numerical models of flood and tide propagation in
895
channels, ASCE Journal of Hydraulic Engineering 127(10), 805-824. DOI: 10.1061/(ASCE)0733-
896
9429(2001)127:10(805).
897
Spada, E., Sinagra, M., Tucciarelli, T., Barbetta, S., Moramarco, T., & Corato, G. (2017).
898
Assessment of river flow with significant lateral inflow through reverse routing modeling.
899
Hydrological Processes.
900
Szymkiewicz R. (1991) Finite-element method for the solution of the Saint Venant
901
equations in an open channel network, Journal of Hydrology 122(1-4), 275-287. DOI:
902
10.1016/0022-1694(91)90182-H.
903 904
Tang, X., Knight, D. W., & Samuels, P. G. (1999). Variable parameter Muskingum-Cunge method for flood routing in a compound channel. Journal of hydraulic research, 37(5), 591-614.
905 906
Tingsanchali T, Manandhar SK. (1985). Analytical diffusion model for flood routing. J Hydraul Eng;111:435–54.
907
Todini E, Bossi A. (1986). PAB (Parabolic and Backwater), an unconditionally stable flood
908
routing scheme particularly suited for real time forecasting and control. J Hydraul Res; 24(5):405–
909
24.
910
Todini E (1996) The Arno rainfall-runoff model. J Hydrol 175:339–382
911
Tsai, C.W. (2003). Applicability of kinematic, noninertia, and quasi-steady dynamic wave
912
models to unsteady flow routing. Journal of Hydraulic Engineering, 129(8), 613-627.
913
Vukovic S., Sopta L. (2003) Upwind schemes with exact conservation property for one-
914
dimensional open channel flow equations, SIAM Journal on Scientific Computing 24(5), 1630-
915
1649. DOI: 10.1137/S1064827501392211.
916 917
Wang, G. T., Yao, C., Okoren, C., & Chen, S. (2006). 4-Point FDF of Muskingum method based on the complete St Venant equations. Journal of hydrology, 324(1), 339-349. 40
918
Wang, L., Wu, J. Q., Elliot, W. J., Fiedler, F. R., and Lapin, S. (2014). Linear diffusion-
919
wave channel routing using a discrete Hayami convolution method. Journal of Hydrology, 509,
920
282-294.
921 922
Weinmann P.E., Laurenson E.M. (1979). Approximate flood routing methods: A review, ASCE Journal of the Hydraulic Division 105(HY12), 1521–1526.
923
Xing Y., Shu C.-W. (2006) High order finite difference WENO schemes with the exact
924
conservation property for the shallow water equations, Journal of Computational Physics 208(1),
925
206-227. DOI: 10.1016/j.jcp.2005.02.006.
926
Xu M., Schwanenberg D. (2017) Sequential and simultaneous model predictive control of a
927
drainage canal network using an implicit Diffusive Wave model. ASCE Journal of Irrigation and
928
Drainage Engineering 143(3), B4016003. DOI: 10.1061/(ASCE)IR.1943-4774.0001082.
929 930 931
41
932
List of Tables
933 934
Table1. Experimental Flume characteristics.
935 936
List of figures
937
Figure 1. Test 1 by Rashid and Chaudrhy (1995): Gauging Station 2 (a), Gauging Station 5 (b).
938
Figure 2. Test 2 by Rashid and Chaudrhy (1995): Gauging Station 2 (a), Gauging Station 5 (b).
939
Figure 3. Flow depth responses to an upstream unitary step stage-hydrograph: Eq. (23), continuous
940
line, and Eq. (27), dashed line.
941
Figure 4. Flow depth responses to a uniform lateral inflow: Eq. (24), continuous line, and Eq. (31),
942
dashed line.
943
Figure 5. Flow rate responses to an upstream unitary step stage-hydrograph: Eq. (27), continuous
944
line, and Eq. (33), dashed line.
945
Figure 6. Flow rate responses to a uniform lateral inflow: Eq. (28), continuous line, and Eq. (34),
946
dashed line.
947
Figure 7. Nash-Sutcliffe contour plot of flow depth responses to an upstream unitary step stage-
948
hydrograph.
949
Figure 8. Nash-Sutcliffe contour plot of flow depth responses to uniform lateral inflow.
950
Figure 9. Nash-Sutcliffe contour plot of flow depth responses to an upstream unitary step stage-
951
hydrograph.
952
Figure 10. Nash-Sutcliffe contour plot of flow depth responses to a uniform lateral inflow.
953 954 955
42
956
Gauge Station distance from inlet [m]
X [m]
Boundary conditions Upstream boundary
1
1.22
0
2 3 4 5 6 7 8 9
3.35 6.09 7.61 11.3 15.2 16.8 18.9 19.8
2.13 4.87 6.39 10.1 14 15.5 17.7 18.6
Inclined gate sill
957 958
Table1. Experimental Flume characteristics.
959
43
Figure 1
Figure 2
Figure 3
Figure 4
Figure 5
Figure 6
Figure 7
Figure 8
Figure 9
Figure 10
Highlights
960 961 962 963 964
Diffusive wave analytical solutions requiring upstream stage-hydrograph (flow depth based) are provided;
965
Downstream boundary conditions are accounted for;
966
Flow depth based simplified models requiring upstream stage-hydrograph predict the flow
967 968 969
depth better than those requiring an upstream flow hydrograph; Flow depth-based solutions for lateral inflows are not suitable for flood propagation when upstream boundary conditions are not used;
970
44