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Study on Tidal Resonance in Severn Estuary and Bristol Channel 1
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Dongfang Liang *, §, Junqiang Xia †, Roger A Falconer ‡ and Jingxin Zhang * 3
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* State Key Laboratory of Ocean Engineering, School of Naval Architecture, Ocean and 6
Civil Engineering, Shanghai Jiao Tong University, Shanghai 200240, China 7
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† State Key Laboratory of Water Resources and Hydropower Engineering Science, 9
Wuhan University, Wuhan 430072, China 10
11
‡ Cardiff School of Engineering, Cardiff University, 12
The Parade, Cardiff CF24 3AA, UK 13
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§ [email protected] 15
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Abstract 17
A horizontal hydrodynamic model was applied to predict the response characteristics 18
of the Severn Estuary and Bristol Channel to regular long waves, in an effort to gain 19
insight into the tidal behaviour of this area. A boundary-fitted curvilinear mesh of high 20
resolution was generated, covering the downstream reach of the River Severn, the 21
Severn Estuary and the Bristol Channel, with the seaward boundary set from Milford 22
Haven to Hartland Point on the west and the riverine boundary at Gloucester towards 23
the east. The simulation was first calibrated against the observed tidal levels and 24
currents at various sites, for typical spring and neap tides. Subsequently, water surface 25
oscillations inside the domain were excited by sinusoidal long waves of different 26
periods at the open boundary to find the fundamental mode of oscillation. The 27
amplitude-frequency relationships were calculated at numerous sites. It was found that 28
the primary resonant mode of oscillation in the Severn Estuary occurred at the tidal 29
period of around 8 hours. Although not exactly coinciding with this resonant mode, the 30
M2 tide still observed a relatively high amplification factor, which helps explain why 31
this water body experiences one of the largest tidal ranges in the world. 32
33
Keywords: Long waves; Tide; Severn Estuary; Bristol Channel; Resonance 34
35
1. Introduction 36
The Severn Estuary is situated between South East Wales and South West England 37
and forms the mouth of the River Severn, which is the longest river in the UK. 38
Conventionally, the River Severn is identified as the Severn Estuary after either the 39
Severn Bridge (M48 Bridge) or the second Severn Crossing (M4 Bridge), both south of 40
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Gloucestershire. However, the normal tidal limit is at Maisemore on the West Channel 41
just north of Gloucester, and at Llanthony Weir on the East Channel. The lower limit of 42
the Estuary is defined by a transection connecting Lavernock Point to the south of 43
Cardiff and Sand Point near Weston-super-Mare, which is near to the proposed site for 44
the Cardiff-Weston Barrage. The Estuary is about 3.2 km wide at the M48 Bridge, and 45
about 14 km wide between Cardiff and Weston-super-Mare. The Severn Estuary 46
discharges into the Bristol Channel, which then discharges into the Irish Sea and the 47
wider North Atlantic Ocean. The Channel is over 50 km across at its widest point, with 48
an average angle of latitude of around 51.35o. 49
The Bristol Channel and Severn Estuary constitute one of the largest, semi-enclosed 50
water basins in the UK. The Severn Estuary is well known for having a large tidal 51
range, regarded as one of the highest in the world and one of the most famous fluvial 52
landmarks in Europe. The dominant component is the principal lunar M2 tide. The 53
typical mean spring tidal range is 12.2 m, with the high spring tidal range approaching 54
14.0 m at Avonmouth, located just upstream of the port of Bristol. There are large areas 55
of intertidal mudflats, and the spring tidal currents in the Estuary are in excess of 2 m/s. 56
Such high tidal ranges make the Estuary a famous scenic spot, and also place it at the 57
centre of the widely publicised and controversial debate concerning the large-scale 58
development of the marine renewable energy. The hydrodynamic processes in the 59
Bristol Channel and Severn Estuary have been studied extensively (e.g. Uncles, 1981; 60
Kirby and Shaw, 2005; Falconer et al., 2009; Xia et al., 2010a, 2010b). 61
Not much research can be found on the underlying nature of the tidal behaviour in the 62
Severn Estuary and Bristol Channel. Some researchers have attributed the high tidal 63
range to the funnel shape and continuously upward slope of the basin (e.g. Pan et al. 64
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2007). The contraction in width from the mouth to the head concentrates the tidal 65
energy, and the shallowing effect due to the reduction in the water depth forces the 66
wave height to rise. However, it has long been pointed out by Marmer (1922) that even 67
the combination of those two effects is not enough to produce the enormous tidal ranges 68
observed in reality. Marmer (1922) used the standing wave theory to explain the natural 69
resonance in the Bay of Fundy, Canada, which boasts the world’s largest tidal range. It 70
was concluded that the tidal period was very close to the natural period of oscillation in 71
the Bay of Fundy, which was the primary reason for its high tides. Previous approaches 72
in deriving the natural period of oscillation of a water body are often crude. Marmer 73
(1922) simply estimated according to the characteristic scales of the problem. 74
Proudman (1953) took a constant-depth assumption. Xing et al. (2008) based their 75
numerical estimation on the mild slope equation in the frequency domain, which 76
disregard the bottom friction and Coriolis effects. 77
This paper aims to ascertain the natural oscillation period and amplification factor of 78
the Severn Estuary and Bristol Channel through a time-domain study, based on a fully-79
dynamic shallow water solver (Liang et al. 2007a, 2007b, Liang et al. 2013). One 80
challenge of the present numerical simulation is the coexistence of multiple scales. On 81
the seaward side, the flow expands as wide as over 100 km; on the upstream side, the 82
river is as narrow as less than 50 m at some sections. Typically, the semidiurnal tidal 83
period is around half a day, so the time to be simulated needs to be tens or hundreds of 84
hours long in order to capture the harmonic dynamics. Corresponding to such a long 85
period, the tidal wavelength can be hundreds of kilometres. Yet, the steep water level 86
rise in front of the river tidal bore can be accomplished over just tens of meters, i.e. 87
several times the river depth, which may pass a river section in less than 1 minute. Such 88
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a disparity in spatial and temporal scales by several orders of magnitude poses an 89
obstacle to numerical simulations. Moreover, natural topographies are inherently 90
complex and irregular, making it difficult to accurately represent them. 91
The paper first set up a computational model for the Severn Estuary and Bristol 92
Channel based on the shallow water equations, which was then calibrated and validated 93
by comparing the predictions with field observations. Subsequently, this model was 94
used to examine the frequency response characteristics of the Severn Estuary and 95
Bristol Channel. 96
97
2. Shallow water solver 98
The shallow water equations have been widely used in modelling unstratified coastal 99
and estuarine waters. In Cartesian coordinates, these depth-integrated equations can be 100
written as: 101
0
y
q
x
p
t
(1) 102
fqCH
qpgp
xgH
yH
pq
x
H
p
t
p
22
22
2
(2) 103
fpCH
qpgq
ygH
y
H
q
xH
pq
t
q
22
22
2
(3) 104
where t is time; ζ is the water surface level above datum; p and q are the volumetric 105
discharges per unit width in the x and y directions, respectively; g is the acceleration due 106
to gravity; H is the total water depth; C is the Chezy coefficient; and f (= sin2 ) is the 107
parameter of the Coriolis acceleration, with the angular speed of the Earth’s rotation 108
and the geographical angle of latitude. 109
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With the help of boundary-fitted coordinate transformation, these governing 110
equations are reformulated, so that the curvilinear mesh in the physical domain is 111
mapped onto the uniform rectangular mesh in the computational domain, which 112
simplifies the finite difference discretisation. Operator-splitting technique and TVD-113
MacCormack scheme are employed in constructing the solution method. An empirical 114
wetting/drying treatment has been developed to track the moving interface between the 115
dry ground and the water-occupied area. All these numerical algorithms have been 116
extensively tested to be valid in past studies. Readers are referred to Liang et al. (2007a, 117
2007b, 2010) for details. The latest refinements to the model include the improved 118
introduction of the open boundary conditions and the enforcement of the exact mass 119
conservation during wetting/drying (Liang et al. 2013). Compared to the widely-used 120
commercial software packages, such as Delft3D and MIKE 21, the present model has 121
the advantage of simultaneously possessing the shock-capturing capability, high 122
accuracy and high efficiency. 123
124
3. Model Setup 125
Due to the large tidal range and relatively small river discharge, the flow in the 126
Severn Estuary and Bristol Channel does not display any significant stratification, 127
which justifies the use of the shallow water equations in the hydrodynamic analyses. As 128
shown in Figure 1, the model domain stretched from the outer Bristol Channel, close to 129
Lundy Island, to Apperley near Gloucester, and thereby included the entire expanse of 130
water from the open sea to the tidal limit. The domain was approximately 200 km long, 131
narrowing down dramatically towards the head of the Estuary, from about 72 km at the 132
seaward boundary to about 50 m at the landward boundary. The computational mesh 133
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was superimposed over the map and contained 3650×350 cells in total. Only every 134
tenth grid point is plotted in Figure 1 in order to achieve a good visual effect. Although 135
the solution was performed in an arbitrary curvilinear coordinate system, more 136
computational accuracy can be gained if the two families of grid lines are perpendicular 137
to each other. As seen in Figure 1, most of the quadrilateral cells had sides of similar 138
lengths and the four corner angles in a cell were close to 90o. The computational mesh 139
generally followed the shape of the domain, so the resolution corresponded well with 140
the width of the water body. Figure 1(b) reveals the extremely high grid density 141
towards the upstream end. The resolution was controlled such that at least 10 grid 142
points were guaranteed within each river cross-section, so that the flow structure in the 143
channel was sufficiently resolved. The transition between the coarse and fine grids in 144
different regions of the domain was smooth. 145
Upstream of the Severn Bridge, the River Severn becomes very narrow and 146
meandering. Various numerical studies, including Yang et al. (2008) and Ahmadian et 147
al. (2010), have divided the region into two parts, with the upstream and downstream 148
parts simulated with one-dimensional and two-dimensional models, respectively. The 149
two models were dynamically linked at the interface, with a specifically designed data 150
exchange mechanism. The high quality curvilinear mesh adopted in this study allowed 151
the two-dimensional computation to be extended to cover the entire region – from 152
Bristol Channel, through the Severn Estuary, up to the downstream reach of the River 153
Severn. Coupled with the high tidal range, this study domain presents a severe 154
challenge to any numerical model, in terms of the computational efficiency, robustness 155
and the ability to handle extreme wetting and drying phenomena. 156
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The bathymetry of the Bristol Channel and lower Severn Estuary were obtained via 157
interpolation of the bathymetric data from the digitised Admiralty Charts 1179, 1166, 158
1165 and 1152, with the elevations converted from Chart Datum to Ordnance Datum at 159
Avonmouth. The bed elevations of the river were interpolated from surveyed cross-160
sectional profiles, upstream of the Severn Bridge. The elevations obtained in these two 161
ways overlapped between the old and new Severn Bridge crossings for a distance of 162
about 4-5 km. The two elevations at each point in this overlap portion were merged into 163
a final elevation using a weighted average algorithm, based on the point’s distances to 164
the two bridge crossings. The consequent bed levels in the whole computational 165
domain are demonstrated in Figure 2, from which it is seen that the upstream and 166
downstream beds have been seamlessly integrated together. 167
Figure 2 also shows the many bends along the river in the upstream portion of the 168
domain. At Upper Parting, near Gloucester, the Severn River splits into two channels, 169
namely the East Channel and West Channel, and at Lower Parting the two channels 170
rejoin. In addition, the studied area is characterised by steep seabed slopes. The 171
average bed level increases upstream from about -60 m near the entrance to about -10 m 172
near Avonmouth, 150 km away from the seaward boundary. Further upstream near 173
Gloucester, the bed levels are about +5 m above the datum. 174
175
4. Model Verification 176
The model was verified against the observations recorded on Admiralty Chart No. 177
1179 and the field data collected by Stapleton et al. (2007). The tidal flow in 178
consideration spanned a period of over 300 hours, commencing at 5.30pm on 20 July 179
2001 and finishing at 5.30am on 2 August 2001. This period was chosen to cover the 180
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time of the field survey, and it also lasted for almost a complete spring and neap tidal 181
cycle. The water levels at the seaward boundary in this period were clamped to values 182
according to the time series shown in Figure 3, which was generated by POLPRED 183
software – a Proudman Oceanographic Laboratory product based on the tidal harmonics 184
model for the Bristol Channel (POL, 2004). At the landward boundary, the average 185
flow rate of the River Severn at Apperley was specified, which was 61.2 m3/s. Water 186
level oscillations at the downstream boundary were the main driving force of the flow 187
inside the domain, so the river flow was unimportant to this study. 188
The initial velocities were set to zero across the domain. The initial water levels were 189
set at 2 m above either the datum or the river bed, whichever was greater. The 190
simulation was pre-run for 3 identical tidal cycles with the same amplitude as the first 191
tide shown in Figure 3, thus obtaining what might be considered more realistic water 192
elevations and the non-zero velocities. Limited by the small grid size in the upstream 193
portion of the domain, the computation used a time step of 0.2 s. 194
The locations of the calibration and validation sites are labelled in Figure 4. At these 195
monitoring points, the values of variables were recorded once every 60 seconds. Here, 196
the main hydrodynamic parameter to be calibrated was the bed resistance, which was 197
quantified using the equivalent roughness height. The Colebrook-While equation was 198
used to relate the Chezy coefficient to the bottom roughness height. The equivalent 199
roughness height accounts for physical features of the bed, including bed forms and 200
vegetations. It is obvious that this parameter varies from point to point in reality; 201
however acceptable results may be achieved using a fixed value across the domain. It 202
would be extremely complex and unnecessary to calibrate over one million free 203
parameters, if non-uniform roughness values were adopted. A number of tests were 204
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conducted, and desirable solutions were attained with the bottom roughness height set to 205
35 mm everywhere. The same value has been used by some previous studies (Falconer 206
et al., 2009). 207
Comparisons between the model predictions and field measurements were made at all 208
of the sites where data were available, for both spring and neap tides. The degree of 209
agreement at the various sites was similar, so only the results at sites South Wales and 210
Minehead were presented herein. Field surveys at these two sites were carried out using 211
an Acoustic Doppler Current Profiler (ADCP) intermittently between 24/7/2001 and 212
1/8/2001. Figure 5 compares the model predictions with the four sets of observed 213
velocities and water depths. It can be seen that there is generally a good match in terms 214
of the period, phase and amplitude of the water depth and velocity variations for all sets 215
of results, even though the current speed and direction were sensitive to local 216
disturbances during measurement. In some flow direction graphs, the artefacts of the 217
flow suddenly switching direction by 180º should be ignored. This occurred when 218
velocity was close to zero, and therefore the flow direction was vulnerable to rounding 219
errors etc. The agreement was improved at some sites compared with previous studies 220
(Yang et al., 2008; Xia et al., 2010; Ahmadian et al., 2010). Therefore, the accuracy of 221
the model was deemed satisfactory, particularly considering the complexity of the tidal 222
flows in such a large domain. 223
A snapshot of the predicted tidal current at the mean ebb tide is illustrated in Figure 6, 224
which highlights the disparate hydrodynamic scales captured by the model. In order to 225
simultaneously simulate the flow at the open sea near Lundy Island and the narrow 226
River Severn reaches near Apperley, there is a hundredfold difference between the sizes 227
of the largest and smallest grids. Because of the high density of the grid points, only 228
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every tenth vector was drawn in Figure 6(a) to avoid clutter. As a result, the flow in the 229
River Severn can hardly be identified. In order to distinguish the individual velocity 230
vectors in the river, the overall flow field needs to be magnified multiple times. 231
The instant of these graphical outputs was chosen when the tidal currents were 232
relatively strong. The predicted flow field in Figure 6 captured the ebb-tide feature in 233
the Bristol Channel, when water was flushing out of the basin. Corresponding to the 234
vast difference between the downstream and upstream widths, the unit-width discharges 235
also exhibit large variations, as is noted by the change in the magnitude of the reference 236
vectors in sub-figures. 237
238
5. Tidal response of Severn Estuary and Bristol Channel 239
After verifying the reliability of the hydrodynamic model, parametric studies were 240
undertaken to investigate the resonance characteristics of the Bristol Channel and 241
Severn Estuary. A simple thesis might first be put forward, which supposed that the 242
tidal range in the Severn Estuary was large because the tidal period of 12.42 hours 243
coincided with the resonant peak of the water body. This thesis was herein tested by 244
varying the tidal period at the seaward boundary and monitoring the water surfaces at 245
some monitoring points, which served as the virtual tidal gauge stations. This study 246
only examined the oscillations that had become repetitive after some spin-up period. 247
The monitoring points defined in Figure 7 were supposed to be representative of the 248
water surface variations over the whole region. In this study, 13 points spread over the 249
domain, among which P1 ~ P8 were located in the Bristol Channel and P9 ~ P13 were 250
within the Severn Estuary. They were also chosen to be close to some well-known 251
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geographical sites, and the correspondence between them and the actual places are listed 252
in the first two columns of Table 1. 253
In modelling the tidal response, the computational condition was identical to that 254
used in the model verification, except the seaward boundary condition. In this pilot 255
investigation, the mean water level was held at 0 m, and the amplitude of the input 256
sinusoidal wave was maintained at 1 m, but the period of oscillation was varied. In total, 257
sixteen scenarios were run, with periods of 1, 2, 4, 5, 6, 7, 8, 9, 10, 11, 12, 16, 20, 24 258
and 28, respectively. 259
Some sample water surface variations at monitoring point P12 are shown in Figure 8, 260
which are the water level time series after the formation of stabilised oscillations. They 261
demonstrate how the water level oscillation at this location responds to the excitation at 262
the sea boundary of various frequencies. In order to easily distinguish the curves of 263
different periods, the results of neighbouring periods are plotted in two separate sub-264
figures. The response curves with periods of 1, 4, 8 and 16 hours are plotted in Figure 265
8(a), and those with periods of 2, 6, 12 and 24 hours in Figure 8(b). It is clear that the 266
wave amplitudes with periods of 1 and 24 hours are relatively small, and resonance 267
occurs at some intermediate period, which gives the maximum amplitude. 268
At each monitoring point under each excitation period, an amplification factor, 269
defined as the ratio between the wave height at the indicated location and that at the 270
open boundary, can be calculated from a curve similar to those shown in Figure 8. A 271
response curve for each monitoring point can then be constructed by plotting the 272
amplification factor versus the wave period. Figure 9 shows the response curves for all 273
the thirteen monitoring points, from which a major resonance peak at 8 hours is seen for 274
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most parts of the basin. Therefore, it seems that the eight-hour tide is the first mode of 275
the basin, instead of the M2 tide with a period of 12.42 hours. 276
At short wave periods, e.g. less than 6 hours, the amplification factor varies 277
drastically, both with periods and among points. The amplification factor can also be 278
much less than unity at some points with very small tidal periods. At longer periods, e.g. 279
greater than 6 hours, the amplification factor continually increases in the order P1, 280
P2 …, until P12, which is generally in the direction towards the head of the basin. The 281
tidal ranges at these twelve sites reach their peaks at the same period of 8 hours. This 282
implies that the tide is most amplified over the inner part of the computational domain 283
in the Severn Estuary, which is consistent with the observations in real life. Monitoring 284
point P13 shows a distinctive trend, as its wave height is much smaller than that at P12, 285
and its resonance period shifts to 9 hours. This implies that the maximum tidal range 286
across the estuary occurs somewhere between P12 and P13, under the assumption of the 287
presently-used mean water level and tidal amplitude at the open boundary. Beyond the 288
resonance at 8-9 hours, the amplification factor gradually decreases with the further 289
increase of the wave period. 290
Although resonance is experienced by all of the points at around 8 hours, a double-291
peak structure appears in the amplification factor curves at some points located in the 292
outer domain. The local maximum amplification factors and the periods at which these 293
factors were recorded, as given in brackets, are listed in the third column of Table 1. 294
Table 2 classifies the monitoring points in terms of the resonance peak periods. It can 295
be seen from the tables that there are in fact several distinct resonance peaks in different 296
regions of the domain. Major resonance in the Bristol Channel occurs at periods shorter 297
than 8 hours. The north side of the Channel, where points P1, P4 and P5 reside, sees the 298
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maximum tidal range occur at a period of 2 hours. On the south side of the Channel, P2, 299
P3, P6 and P8 experience resonance when the period is 4 hours. Whilst the overall first 300
mode of resonance seems to correspond to a universal period of around 8 hours across 301
the entire region, some regions in the Bristol Channel also experience significant, if not 302
greater, resonance when the wave frequency doubles or quadruples. 303
Figure 10 illustrates the three-dimensional water surface positions when the tide at 304
the seaward boundary is at the mid-flood phase. These graphs can be used to explain 305
how the tide is amplified inside the domain. At shorter wave periods, e.g. in the case of 306
Figure 10(a), water surface undulations can be clearly noticed, with the greenish-307
coloured contours separated by the bluish-coloured contours along the basin. The 308
interval of the separation continually reduces towards the upstream direction. At longer 309
wave periods, e.g. in the case of Figure 10(f), the water surface is almost flat across the 310
domain except in the upstream river reaches. The tide is less dynamic, and the 311
propagation towards the head of the basin cannot be clearly traced any more. 312
In the water surface plots, the greenish colour indicates the tidal wave crests, whilst 313
the bluish colour indicates wave troughs. The horizontal distance between them reflects 314
half the wave length. The longer tidal period leads to a longer tidal length, as 315
demonstrated in Figure 10. One main mechanism of resonance in this water body seems 316
to comply with the quarter-wavelength resonator theory, which states that the tidal 317
resonance is most striking when the length of the water basin is about a quarter of the 318
incident tidal wavelength. For a natural water basin with irregular geometry and 319
bathymetry, however, it is not easy to underpin exactly the length of the basin. Roughly 320
speaking, the characteristic length of the Severn Estuary and Bristol Channel is of the 321
same order of magnitude as the wavelength associated with a two-hour-period tidal 322
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wave, as evident in Figure 10(b). By quadrupling the tidal period, the wavelength also 323
increases approximately fourfold. Hence, the characteristic length of the studied water 324
body is approximately equal to a quarter of the eight-hour tidal wavelength, which 325
corresponds well to the occurrence of maximum amplification factor at 8 hours 326
observed among most of the monitoring points shown in Figure 9. The above analyses 327
only give a gross picture of the tidal behaviour in the region, when the integrated water 328
body in the Bristol Channel and Severn Estuary is taken as a whole. Hence, the overall 329
resonance occurs at a period of around 8 hours in the central part of the estuary, e.g. 330
between P6 and P12, where the amplification factor is the greatest. The maximum 331
amplification factor decreases towards the open boundary and towards the tidal limit. 332
When examining some smaller semi-enclosed water bodies inside the studied domain, 333
e.g. the Carmarthen Bay, the resonant motions occur at smaller periods and wavelengths, 334
which explains some of the shorter resonance periods at some monitoring points 335
observed in Figure 9 and listed in Tables 1 and 2. 336
337
6. Conclusions 338
A high-quality curvilinear mesh was generated to cover the Bristol Channel, Severn 339
Estuary and downstream reach of the River Severn, which accommodates grid cells 340
with two orders of magnitude difference in size. The landward boundary was set 341
slightly upstream of the tidal limit close to Gloucester. The seaward boundary was set at 342
the downstream end of the Bristol Channel. Rigorous model verifications were 343
undertaken using field observations of tidal levels and currents. 344
Long-wave-induced hydrodynamic processes in the Severn Estuary and Bristol 345
Channel have been studied using the established model. The frequency response 346
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characteristics of the water body were assessed when subjected to sinusoidal-wave 347
excitation at the open sea boundary. By normalising the predicted wave heights with 348
reference to the input wave height, the amplification factors were determined as a 349
function of the location and wave period. The consequent periods obtained for the first 350
mode of resonance across the whole region ranged from 8 to 9 hours. The 351
hydrodynamic processes in the Bristol Channel and Severn Estuary were highly 352
complex, owing to the large area, irregular land boundaries, complicated bathymetry, 353
and existence of extensive intertidal flats. In some small semi-enclosed bays in the 354
Bristol Channel, large water surface oscillations might be excited at periods no more 355
than 4 hours. The maximum tidal range was confirmed to occur in the upper part of the 356
Severn Estuary, where the input wave was amplified by up to three times. 357
It should be noted that this is a preliminary research. The maximum tidal range has 358
been found to occur between P12 and P13, which are two points rather far apart. More 359
monitoring points will be required to investigate the flow behaviour in a greater detail, 360
especially in the regions that have proved to be of interest in this paper. Further studies 361
are also being undertaken to relate the present type of analyses more closely to the real 362
tidal spectrum and to examine the Severn River bore. The present method can also be 363
used to examine the fundamental mode of resonance in harbours and bays in response to 364
the attack of long waves, such as tsunamis, which have periods from many minutes to 365
an hour and may cause unexpected damage. 366
367
Acknowledgements 368
We acknowledge the financial support from the State Key Laboratory of Ocean 369
Engineering, Shanghai Jiao Tong University (Grant No. GKZD010061), and from the 370
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Open Research Fund Program of the State Key Laboratory of Water Resources and 371
Hydropower Engineering Science, Wuhan University (Grant No. 2011A005). 372
373
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[17] Yang L, Lin B, Falconer RA. (2008). Modelling enteric bacteria levels in coastal 418
and estuarine waters, Proceedings of the Institution of Civil Engineers, 419
Engineering and Computational Mechanics , 161(4): 179-186 420
421
Page 20
20
List of Figures 422
Figure 1. Map of the studied area with computational mesh superimposed 423
Figure 2. Bathymetry of the Bristol Channel and Severn Estuary 424
Figure 3. Water elevations at seaward boundary in model verification 425
Figure 4. Locations of the verification sites 426
Figure 5. Model verification examples, where lines are predicted values and symbols are 427
measured values 428
Figure 6. Predicted tidal currents in the ebb tide at t = 227.5 hours 429
Figure 7. Locations of the monitoring points 430
Figure 8. Water elevation oscillations at Site P12 due to tides of different periods 431
Figure 9. Relationship between amplification factor and tidal period 432
Figure 10. Water surface positions at mean flood tide at seaward boundary 433
434
List of Tables 435
Table 1. Resonance periods and amplification factors at monitoring points 436
Table 2. Categorisation of the monitoring points according to the resonance period 437
438
439
440
441
Page 21
21
442
(a) Overall view (b) Close-up view of the upstream part 443
Figure 1. Map of the studied area with computational mesh superimposed 444
445
446
447
(a) Overall domain (b) Close-up view of the upstream part 448
Figure 2. Bathymetry of the Bristol Channel and Severn Estuary 449
450
451
Page 22
22
452
t (hour)
Wat
erle
vel(
m)
0 24 48 72 96 120 144 168 192 216 240 264 288 312 336-5
0
5
453
Figure 3. Water elevations at seaward boundary in model verification 454
455
456
457
458
Figure 4. Locations of the verification sites 459
460
461
462
463
Page 23
23
t (hour)
Wat
erd
epth
(m)
80 85 90 95 10010
15
20
25
t (hour)
Cu
rren
tsp
eed
(m/s
)
80 85 90 95 1000
0.5
1
1.5
t (hour)
Cu
rren
tdir
ectio
n
80 85 90 95 100
-120
0
120
464
(a) South Wales site on 24th July 2001 465
t (hour)
Wat
erd
epth
(m)
130 135 140 145 15010
15
20
25
t (hour)
Cu
rren
tsp
eed
(m/s
)
130 135 140 145 1500
0.5
1
1.5
t (hour)
Cu
rren
tdir
ectio
n
130 135 140 145 150
-120
0
120
466
(b) South Wales site on 26th July 2001 467
t (hour)
Wat
erd
epth
(m)
225 230 235 240 24510
15
20
25
t (hour)
Cu
rren
tsp
eed
(m/s
)
225 230 235 240 2450
0.5
1
1.5
t (hour)
Cu
rren
tdir
ectio
n
225 230 235 240 245
-120
0
120
468
(c) Minhead site on 30th July 2001 469
t (hour)
Wat
erd
epth
(m)
275 280 285 290 29510
15
20
25
t (hour)
Cu
rren
tsp
eed
(m/s
)
275 280 285 290 2950
0.5
1
1.5
t (hour)
Cur
rent
dir
ectio
n
275 280 285 290 295
-120
0
120
470
(d) Minhead site on 1st August 2001 471
Figure 5. Model verification examples, where lines and symbols are predicted and 472
measured values respectively 473
474
Page 24
24
475
476
(a) Overall view with one every ten vectors drawn 477
478
479
(b) First close-up with one every five vectors drawn 480
481
Page 25
25
482
(c) Medium close-up with one every four vectors drawn 483
484
485
(d) Large close-up with all vectors drawn 486
Figure 6. Predicted tidal currents in the ebb tide at t = 227.5 hours 487
488
489
Page 26
26
490
491
Figure 7. Locations of the monitoring points 492
493
494
Page 27
27
495
t (hour)
Wat
erle
vel(
m)
36 42 48 54 60-3
-1.5
0
1.5
3
T = 1 hour
T = 4 hours
T = 8 hours
T = 16 hours
496
(a) Period = 1, 4, 8 or 16 hours 497
498
t (hour)
Wat
erle
vel(
m)
36 42 48 54 60-3
-1.5
0
1.5
3
T = 2 hours
T = 6 hours
T = 12 hours
T = 24 hours
499
(b) Period = 2, 6, 12 or 24 hours 500
Figure 8. Water elevation oscillations at Site P12 due to tides of different periods 501
502
503
Page 28
28
504
1
1
1
11
1 1 1 1 1 11 1 1 1
2
2
2
22 2 2 2
22 2
2 2 2 2
3
3
3
33 3 3 3
33
3
3 3 3 3
4
4
4
44
44 4
44
4
44 4 4
5
5 5
55
55 5
5
55
55 5 5
6
6
66
6
66
6
6
6
6
6
66
6
7
7
7
7
7
77
7
7
7
7
7
77
7
8
8
88
8
8 8
8
8
8
8
8
88
8
9
9
99
9
9 9
9
9
9
9
9
99
9
X
X
XX
X
X X
X
X
X
X
X
XX
X
A
A
A
A
A
AA
A
A
A
A
A
AA
A
B
B
B
B
B
BB
B
B
B
B
B
BB
B
C
C
C
C
C
C
CC C
CC
C
CC
C
Period (hours)
Am
plif
ica
tion
Fa
cto
r
0 4 8 12 16 20 24 280
1
2
3P1P2P3P4P5P6P7P8P9P10P11P12P13
1
2
3
4
5
6
7
8
9
X
A
B
C
505
Figure 9. Relationship between amplification factor and tidal period 506
507
508
Page 29
29
509
(a) Period = 1 hour 510
511
(b) Period = 2 hours 512
513
(c) Period = 4 hours 514
515
Page 30
30
516
(d) Period = 8 hours 517
518
(e) Period = 12 hours 519
520
(f) Period = 28 hours 521
Figure 10. Water surface positions at mean flood tide at seaward boundary 522
523
524
525
Page 31
31
Table 1. Resonance periods and amplification factors at monitoring points 526
Label Locations Peak amplification factors
and resonance periods *
P1 Burry Port 2.03 (2), 1.12 (8)
P2 Near open sea 1.44 (4), 1.23 (8)
P3 Ilfracombe 1.59 (4), 1.36 (7)
P4 Mumbles 1.96 (2), 1.41 (8)
P5 South Wales 2.60 (2), 1.58 (8)
P6 Minehead 1.73 (4), 1.98 (8)
P7 Cardiff 2.33 (8)
P8 Burnham-on-Sea 2.18 (4), 2.36 (8)
P9 Weston-Super-Mare 2.40 (8)
P10 Newport 2.57 (8)
P11 Avonmouth 2.72 (8)
P12 Beachley (M48 Bridge) 2.82 (8)
P13 Sharpness Dock 2.37 (9)
527
* There are two resonance peaks at some locations. For each peak, the first number 528
indicates the value of the amplification factor and the second number in brackets 529
indicates the corresponding tidal period. 530
531
Page 32
32
532
Table 2. Categorisation of the monitoring points according to the resonance period 533
Resonance peak period (hours) Monitoring sites
2 P1, P4, P5,
4 P2, P3, P6, P8
7 – 9 All
534