rainfall organization control on the flood response of...
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Accepted Manuscript
Rainfall Organization Control on the Flood Response of mild-slope Basins
Yiwen Mei, Emmanouil N. Anagnostou, Dimitrios Stampoulis, Efthymios I.Nikolopoulos, Marco Borga, Humberto J. Vegara
PII: S0022-1694(13)00910-4DOI: http://dx.doi.org/10.1016/j.jhydrol.2013.12.013Reference: HYDROL 19275
To appear in: Journal of Hydrology
Received Date: 21 May 2013Revised Date: 26 November 2013Accepted Date: 7 December 2013
Please cite this article as: Mei, Y., Anagnostou, E.N., Stampoulis, D., Nikolopoulos, E.I., Borga, M., Vegara, H.J.,Rainfall Organization Control on the Flood Response of mild-slope Basins, Journal of Hydrology (2013), doi: http://dx.doi.org/10.1016/j.jhydrol.2013.12.013
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Rainfall Organization Control on the Flood Response of mild-slope
Basins
Yiwen Mei, Emmanouil N. Anagnostou, Dimitrios Stampoulis
Civil and Environmental Engineering
University of Connecticut, Storrs, CT, USA
Efthymios I. Nikolopoulos and Marco Borga
Department of Land, Environment, Agriculture and Forestry,
University of Padova, Legnaro, PD, Italy
Humberto J. Vegara
School of Civil Engineering and Environmental Sciences
University of Oklahoma, Norman, OK, USA
Submitted to: Journal of Hydrology
Submission date: April 2013
Revised Manuscript Submitted: October 2013
Corresponding Author: Emmanouil N. Anagnostou, CEE, University of Connecticut, Storrs, CT
06269, (860) 486-6806, Email: [email protected]
i
Abstract
This study uses a long-term (8 years) dataset of radar-rainfall and runoff observations for the Tar River
Basin in North Carolina, to explore the rainfall space-time organization control on the flood response of
mild-slope (max slope < 32 degrees) basins. We employ the concepts of ―spatial moments of catchment
rainfall‖ and ―catchment scale storm velocity‖ to quantify the effect of spatial rainfall variability and
basin geomorphology on flood response. A calibrated distributed hydrologic model is employed to assess
the relevance of these statistics in describing the degree of spatial rainfall organization, which is important
for runoff modeling. Furthermore, the Tar River Basin is divided into four nested sub-basins ranging from
1106 km2 to 5654 km
2, in order to investigate the scale dependence of results. The rainfall spatiotemporal
distribution represented in the analytical framework is shown to describe well the differences in
hydrograph timing (less so in terms of magnitude of the simulated hydrographs) determined from forcing
the hydrologic model with lumped vs. distributed rainfall. Specifically, the first moment exhibits a linear
relationship with the difference in timing between lumped and distributed rainfall forcing. The analysis
shows that the catchment scale storm velocity is scale dependent in terms of variability and rainfall
dependent in terms of its value, assuming typically small values. Accordingly, the error in dispersion of
simulated hydrographs between lumped and distributed rainfall forcing is relatively insensitive to the
catchment scale storm velocity, which is attributed to the spatial variability of routing and hillslope
velocities that is not accounted by the conceptual framework used in this study.
Keywords: Spatiotemporal Variability of Rainfall; Rainfall Moment; Storm Velocity; Hydrologic Model
1
1 Introduction 1
The prediction of catchment flood response is one of the recurrent themes in hydrology (Nicótina, et 2
al., 2008; Smith, et al., 2004; Woods & Sivapalan, 1999). A question asked is that, given certain 3
catchment and precipitation characteristics, what are the dominant processes in flood response? In 4
practical terms, operational flood and flash flood guidance systems are based on continuous hydrological 5
models that provide catchment-scale soil moisture estimates representing the antecedent moisture 6
conditions at spatial scales closer to the need of flash flood forecasting (Carpenter, et al., 1999). Based on 7
these antecedent moisture conditions, it is possible to provide an estimate of rainfall depth for a given 8
duration that can lead to flooding without explicitly modeling the event dynamics (Georgakakos, 2005; 9
Reed, et al., 2004). At the ground of flood/flash flood guidance is the computation of the basin-average 10
rainfall for a given duration that is necessary to cause flooding. 11
The fundamental problem facing flood modeling associated with flash flood guidance (FFG) is that 12
small to medium size basins prone to flash floods are rarely gauged and, therefore, prediction of flash 13
flood response relies on basin-average rainfall information and the parameterized response of the larger 14
scale, parent basins. As several past studies have indicated the basin flood response is sensitive to the 15
spatial rainfall patterns (Dawdy & Bergmann, 1969; Naden, 1992; Viglione, et al., 2010a; Wilson, et al., 16
1979; Wood, et al., 1988; de Lima & Singh, 2002). Therefore, from the perspective of developing 17
effective flood forecasting systems, it is important to develop a consistent framework to quantify the 18
effects of space-time rainfall aggregations on the prediction accuracy of flood response for different basin 19
and storm characteristics (Borga, et al., 2007; Merz & Blöschl, 2003; Norbiato, et al., 2008; Parajka, et 20
al., 2010; Saulnier & Le Lay, 2009; Zoccatelli, et al., 2010). 21
An important feature frequently reported in hydrologic modeling studies is the catchment dampening 22
effect, which is often interpreted as the property of the catchment to filter out specific space-time 23
characteristics of the precipitation input in the flood response (Skøien & Blöschl, 2006; van De Giesen, et 24
al., 2000; van Loon & Keesman, 2000). Therefore, only a portion of rainfall space-time characteristics 25
2
(e.g. spatial concentration in specific catchment regions and storm motion) will emerge to control the 26
hydrograph shape (Skøien, et al., 2003). As shown in a number of works (Smith, et al., 2002; 2005; 27
Woods & Sivapalan, 1999), the river network geometry plays an essential role in the structure of the 28
catchment smoothing properties. Therefore a flow distance coordinate, i.e. the coordinate defined by the 29
distance along the runoff flow path to the basin outlet, has been introduced with the aim of providing 30
information on rainfall spatial organization relative to the basin network structure as represented by the 31
routing time (Borga, et al., 2007; Smith, et al., 2005; Zhang, et al., 2001). Similar works (Smith, et al., 32
2002; 2005) have developed dimensionless normalized indicators based on the flow distance coordinate 33
in terms of either routing time or length of flow path (e.g. normalized flow distance, normalized 34
dispersion) and used them for quantifying the geomorphologic driven spatial rainfall patterns. Zanon et al. 35
(2010) showed that the normalized time distances and normalized time dispersion of a severe storm event 36
at four small size cascade basins (less than 150km2) with complex terrain structure had a value very close 37
to one while similar results were also exhibited in Sangati et al. (2009). Sangati et al. (2009) additionally 38
showed that the normalized time distance and dispersion have a considerable increase for basin sizes 39
exceeding 500 km2. Beside the normalized time distance and dispersion, the concept of rainfall movement 40
has been developed to quantify theoretically and experimentally the combined effect between the rainfall 41
space-time properties and basin geomorphology. Viglione et al. (2010b) applied the analytical framework 42
developed in Viglione et al. (2010a) and concluded that due to the high spatial heterogeneity properties of 43
short-rain event, the roles of movement component of flood inducing complex terrain storms can be 44
important in runoff generation; and that for the more spatially uniform long-lasting rain events, the 45
movement component is weak in influencing the hydrograph. Seo et al. (2012) on the other hand has 46
shown that storm motion may have significant impact even for long-lasting precipitation events. 47
In a recent work, Zoccatelli et al. (2011) derived a term named ―catchment scale storm velocity‖, 48
which accounts for the combined effects of total storm motion and temporal storm variability over 49
catchment. The scale dependency of this concept was further examined by Nikolopoulos et al. (2013) who 50
3
showed strong nonlinearity and low value based on a single flash flood event. These studies on 51
―catchment scale storm velocity‖ were focused on a limited number of short-living flood events occurring 52
in small catchments. For this type of floods and basin sizes, differences between the assumptions in the 53
method and the event characteristics are deemed to be small; therefore, the method may be applied to 54
represent the effect of spatial rainfall aggregation on flood modeling. In this work, the method is applied 55
on a large number of moderate storm intensity, long-lasting flood events occurring over large (greater 56
than 1000km2) and mild-slope (max of slope less than 32° with mean at around 3°) catchments from the 57
Tar River Basin in North Carolina. Our aim is to test the representation of ―spatial moments of catchment 58
rainfall‖ and ―catchment scale storm velocity‖ reported in Zoccatelli et al. (2011) as potential metrics for 59
quantifying the effect of rainfall organization and storm motion on the hydrologic response and to analyze 60
the impact of some of its assumptions (e.g. uniform runoff routing velocity). In section 2 we present the 61
study area and data used in our analysis. Section 3 summarizes the analytical framework of Zoccatelli et 62
al. (2011), while section 4 presents the numerical experiments used to determine the two methods, and 63
evaluates the correlations of those statistics to the hydrologic modeling error metrics. Conclusions and 64
recommendations for further research are provided in section 5. 65
66
2 Study Area and Data 67
2.1 Tar River Basin 68
The target area of this study is the Tar River basin in North Carolina, USA. The Tar River originates 69
in Person County as a freshwater spring and flows 225km southeast to Washington, NC. The main stem 70
of the upper river flows through Louisburg, Rocky Mount, Tarboro and Greenville and provides drinking 71
water for these communities. Its major tributaries are Swift, Fishing and Tranters creeks and Cokey 72
Swamp. The area within this basin is relatively undeveloped. Agriculture accounts for 33.6% of the land 73
use while the rest includes mainly forests (29.6%), open water (19.7%), and wetlands (11.4%). Urban 74
lands and scrub growth accounts for 5.2% of the land usage. Fig.1 shows the location and elevation of the 75
4
Tar River basin. The basin is characterized by mild slopes (Table 1) and elevations ranging between 4m 76
a.s.l. (above sea level) close to the outlet on the southeast to about 225m a.s.l. near the headwaters on the 77
northwest. The study area was divided into four cascade basins namely B1, B2, B3, and B4 (shown in 78
Fig.1). Drainage areas for the four basins are approximately 1106, 2012, 2396, and 5654 km2, 79
respectively. Table 1 summarizes some basic statistics on local slope and flow length distribution, derived 80
from available elevation dataset (10 feets) for each basin. Note that slope values reported corresponds to 81
the steepest downhill descent for each point and flow length is equal to the distance, along the runoff flow 82
path, from a given point to basin outlet. 83
2.2 Rainfall Data 84
Rainfall information was based on the US National Weather Service (NWS) Multisensor Precipitation 85
Estimation (MPE) rainfall product available at 4 km/hourly spatiotemporal resolution. MPE data are 86
derived from a blend of automated and interactive procedures that combine information from satellite, the 87
WSR-88D radar network and rain gauges (Breidenbach & Bradberry, 2001; Fulton, 2002). Hourly MPE 88
data are available for the Southeast River Forecast Center (SERFC) region at HRAP (Hydrologic Rainfall 89
Analysis Project) resolution since January 2002. The nominal size of an HRAP grid cell in the area is 90
about 4 km (Greene & Hudlow, 1982; Reed & Maidment, 1999). A total of eight years of data (2002-91
2009) were analyzed for this work. Among the eight years, 2003 was the wettest, which had 1260 mm of 92
annual basin-average rainfall, while the driest year of the study period was in 2007 with 831 mm of 93
annual basin-average rainfall. Fig.2 shows the eight-year average annual rainfall within the study area. A 94
point to note is that the mean annual rainfall increases by 20% going from west (the headwaters of the 95
basin) to east (basin outlet). 96
2.3 Flood Events 97
The streamflow dataset used in this study consists of hourly streamguage measurements from US 98
Geological Survey (USGS) and span the same 8 years period as the precipitation data. Similarly to 99
precipitation, 2003 had the maximum annual flow for the overall basin as well as the three sub-basins. 100
5
The highest peak flow for B1 was 225m3/s and was observed during 2002. For the other three basins, the 101
highest peak flows occurred during 2006 and were 292m3/s, 402m
3/s and 694m
3/s. A procedure was 102
applied on the runoff time series to extract the flood events used in this study. One of the steps in this 103
procedure involved separation of baseflow from discharge time series that was performed following the 104
―Smooth Minima Technique‖ (Gustard, et al., 1992). Specifically, the technique first finds the minima of 105
every 144-hour non-overlapping periods by searching from the beginning to the end of the entire period 106
of record. Next, it searches the time series of the minima for values that are less than 11% of its two outer 107
values; such central values are then defined as turning points. Baseflow hydrograph is then constructed by 108
connecting all of the turning points with straight lines. Flood events were then selected from the time 109
series by identifying the peak flows between any two turning points. For a flood event to be considered 110
for further analysis, the ratio of the direct runoff to baseflow at the time of peak flow should be greater 111
than 4 (this value was empirically set to exclude peaks from moderate to low flood events). As a final 112
step, events were visually inspected to separate multimodal hydrographs into respective single peak 113
hydrographs. Fig.3 illustrates three of the selected flood events for B4 basin after applying the event 114
separation method on the streamflow data. 115
Table 2 summarizes the minimum and maximum range values as well as the mean values of the 116
event-based statistics of the selected flood events. Mean rainfall volume increases with basin scale (from 117
42 mm for B1 to 61 mm for B4), which points to the fact that as the basin scale increases, larger portion 118
of the relatively wet part of the east basin is accounted for. Both the mean cumulative direct flow and 119
peak flow rate increase with basin scale as expected (225 mm and 88 m3/s for B1 to 390 mm and 213 m
3/s 120
for B4). The event runoff coefficients (RC), defined as the ratio between direct flow and total 121
precipitation (Blume, et al., 2007; Merz, et al., 2006; Norbiato, et al., 2009), are also reported. The mean 122
RC is shown to decrease with basin area suggesting that runoff generation in west part of the basin is 123
higher than the east part. 124
125
6
3 Catchment Scale Rainfall Organization 126
3.1 Spatial Moments of Catchment Rainfall 127
We apply the concept of Spatial Moments of Catchment Rainfall reported in Zoccatelli et al. (2011) 128
to examine the space-time precipitation organization. This analytical framework was built upon the work 129
of Woods and Sivapalan (1999), Viglione et al. (2010a) and Smith et al. (2002; 2005). The spatial rainfall 130
moments provide a description for spatial integration of rainfall field p(x,y,t) (L·T-1
) within a basin at a 131
certain time t as a function of the flow length d(x,y) (L) defined as the distance along the flow path, from 132
position x,y to the outlet of the basin. The n-th spatial moment of catchment rainfall pn (Ln+1
·T-1
) is 133
defined by Zoccatelli et al. (2011) as: 134
(1)
where A denotes the catchment area. Note that the zero-th order spatial moment of catchment rainfall p0(t) 135
is the catchment-averaged rainfall rate at time t. Analogously, the gn, n-th moments of flow-length yields 136
a similar form as: 137
(2)
Thus, the catchment-averaged flow distance is the first order moment of flow-length (g1). 138
By taking the ratio between moments of catchment rainfall and flow-length, one can obtain a 139
dimensionless form for the spatial moments of catchment rainfall as the formulations below: 140
(3)
(4)
The first order moment δ1(t) reflects the location of catchment rainfall centroid (i.e., the catchment center 141
of mass) over the basin. Values of δ1(t) around one indicate rainfall is distributed uniformly over the 142
catchment or mostly concentrated over the catchment centroid. Values of δ1(t) less (greater) than one 143
7
indicate that rainfall is distributed close to the outlet (the periphery) of the basin. The second order 144
moment δ2(t) describes the dispersion of the rainfall field relative to its mean position with respect to the 145
spreading of the flow-length. Values of δ2(t) close to one reflect that rainfall distributes uniformly over 146
the catchment. Values of δ2(t) less (greater) than one indicate that rainfall is characterized by a unimodal 147
(multimodal) distribution along the flow-length. 148
The above equations can also be extended to reflect rainfall organization corresponding to the 149
cumulative rainfall over the time period Ts (e.g. storm period). These statistics are termed Pn and Δn 150
(Zoccatelli, et al., 2011) and are defined as follow: 151
(5)
(6)
(7)
Therefore, P0 stands for the average rainfall intensity over the given time period and product between P0 152
and the time period Ts is the cumulative rainfall volume for that period. 153
3.2 Catchment Scale Storm Velocity 154
Since the first order moment of rainfall reflects the location of rainfall mass center, it is then 155
interesting to note that its first order temporal derivative of evolution over time reveals the effect of storm 156
motion. For a simple case of a storm element characterized by constant rainfall intensity moving along the 157
catchment, the definition of the catchment scale storm velocity V(L·T-1
) is as follows: 158
(8)
Storm velocity defined in this way reflects the kinematic movement of rainfall barycenter with respect to 159
basin geomorphology (i.e. movement of rainfall mass center across the flow-length coordinate). 160
8
For a more realistic case of storm motion with changes in mean areal precipitation, Zoccatelli et al. 161
(2011) provided the following definition: 162
(9)
(10)
where w(t) is termed as the rainfall weight. Eq.(9) contains two slope terms; the first slope term is 163
estimated based on the time regression between rainfall-weighted first scaled moments and time, while 164
the second one is based on the regression between rainfall weights and time. The difference between these 165
two terms describes the storm velocity Vs, which reflects the combined effect of storm kinematic motion 166
and dynamics of the catchment mean areal rainfall rate. For temporally variable but spatially uniform 167
rainfall (δ1 = Δ1 = 1) the two slope terms will be equal in value and opposite in sign, which implies a null 168
value for the catchment scale storm velocity. In this case, the storm is effectively stationary. On the other 169
hand, if rainfall is variable in space, but uniform in time (w = 1), Vs takes the same value as V. Note that 170
the sign of the velocity is positive (negative) for the case of upstream (downstream) storm motion. 171
Solving for Eq.(9) requires a numerical evaluation of the linear regression over a specified space and 172
time window. The spatial window is defined by the catchment size, whereas the temporal window is 173
chosen in this study to have two distinct durations: a) a time length equal to the entire storm event 174
duration, and b) a shorter-length moving time window (arbitrarily set to be 6 hours). Vs obtained from 175
time window (a) reflects the overall velocity of the entire event representing the concept of ―catchment 176
scale storm velocity‖, while Vs(t) computed based on time window (b) represents a time-dependent storm 177
velocity. 178
3.3 Events Analysis 179
Rainfall variability is evaluated here by means of the ―Spatial Moments of Catchment Rainfall‖, 180
described in the previous section. A long duration flood event associated with more than 35 hours of 181
rainfall (January 13th to 14
nd, 2005) is selected to illustrate the conceptualization of rainfall spatial 182
9
moments (the corresponding flood event is shown in Fig.9). Rainfall statistics and spatial moments are 183
presented for the first 35 hours of the rain event, which is the period contributing the majority of the rain 184
accumulation. This event induced flooding in all four sub-basins of the Tar River basin enabling the 185
illustration of the scale dependency of the statistics. The time series of the first and second scaled 186
moments (δ1 and δ2) of the catchment rainfall are reported in Fig.4, along with the basin-averaged rainfall 187
rate (p0). 188
The temporal patterns of the basin-averaged rainfall rate (Fig.4 Panel a) of these cases are quite 189
similar since they are from the same event. All of them begin with very low rain rate followed by a 190
smooth peak after 22:00 of January 13th. Subsequently, a sharp peak with the highest rainfall rate 191
(11.7mm/h for B1, 7.6mm/h for B2, 7.2mm/h for B3 and 7.1mm/h for B4) occurred between 11:00 and 192
17:00 on January 14th. A pause during 17:00 and 22:00 on January 13
th is also seen. The time series of 193
both first and second scaled spatial moment (Fig.4 Panel b and c) exhibit a relatively large variability with 194
δ1 varying between 0.19 and 1.91 in B4 basin. Based on the trend of δ1 it can be seen that the storm 195
centroid was located towards the headwater of the basin (except for B1 sub-basin) within most of the time 196
(from 22:00 of 13th to 14:00 of 14
th). The overall movement of storm center is from the periphery towards 197
the outlet at the phase of the 2nd
rainfall peak (from January 14th 12:00 to 17:00, the last part of the second 198
segment in Fig.4 Panel b and c). This down basin movement is captured by a sequence of snapshots of 199
hourly rainfall maps rendered in Fig.5 between 12:00 and 17:00 of January 14th. The highest value of δ2 200
for B1 in that period is 2.63. The value of δ2 appears to be greater than 1 for several hours in B1, while 201
those in the other basins rarely exceeded 1 (except for δ2 in the 2nd
hour) during most of the hours (i.e. the 202
storm only has one core during almost the entire event in these basins), specifically at the late period of 203
the storm shown in Fig.5. The temporal evolution of δ1 and δ2 for this storm are similar to each other 204
especially for the B2 and B3 basins due to the high shape and geomorphologic (see Table 1) similarity of 205
the two basins. More importantly, values of δ2 generally reflect the trend of δ1, as expected, with small 206
10
values of dispersion when δ1 is either larger or smaller than one and values of dispersion close to one 207
when δ1 is also close to unity. 208
The main direction of the storm centroid during the main part of this event (i.e. after 11:00 UTC) is 209
downstream, which is interpreted by the negative Vs(t) values reported in Fig.6. Results from this figure 210
show that for all basins, magnitude of catchment scale storm velocity for the main event was relatively 211
low (within 0.5 m/s). In addition, although Vs has been accounted for the combined-effect of storm 212
movement and basin-average rainfall rate of change, it still reveals the time evolution of δ1. For example, 213
the time that Vs(t) reaches the maximum value of 1.51m/s for B2, 2.37m/s for B3 and 2.76m/s for B4 at 214
15:00 of January 13th is overlapping with the period that δ1(t) increases rapidly (i.e. between 13:00 and 215
16:00 of January 13th). The overall dependency of Vs(t) to the change rate in δ1(t) is not clear because the 216
regression is performed over δ1(t) weighted by w(t). Hence, during periods with a minor rate of change of 217
w(t), Vs(t) can explain the change of δ1(t) and Eq.(9) becomes 218
(11)
This equation contains only one regression performed over t and δ1(t). 219
It was stated in Eq.(9) that the Vs term can partly reflect the dynamics of rainfall rate. To verify this 220
aspect, Fig.7 is produced by juxtaposing the time series of basin-averaged rainfall rate and the catchment 221
scale storm velocity. Upslope deceleration characterized as positive decreasing values of Vs(t) can be 222
revealed between 22:00 of 13th and 4:00 of 14
th for all basins (start 2 hours earlier for B1). Coincidentally, 223
these time ranges are also the time periods for which rainfall grows from 0 to the first peak rain rate. 224
Conversely, upstream acceleration of the rainfall mass center appears between 7:00 and 9:00 of the 14th 225
with a decreasing of rainfall rate. A clearer example period occurs around the second rainfall peak. These 226
two example periods lead to the observation that the extreme values of Vs(t) are likely to occur at the time 227
that rainfall rate reaches its maxima (peak value) or minima (gap between two rainfall peaks). This 228
observation highlights the dependence between rainfall intensity to the storm velocity, which was also 229
demonstrated in previous studies (Tarolli, et al., 2013). Possible cause of this observational result is that 230
11
the second linear regression term offsets the first term due to the high values that it can take when rainfall 231
rate is changing rapidly. This further affects the magnitude of Vs(t). Consequently, it seems that Vs(t) can 232
represent the change of δ1(t) when the change of basin areal rainfall rain is null or negligibly small. On 233
the other hand Vs(t) would reflect the temporal variability of p0(t) rather than the barycenter movement 234
when p0(t) is significantly fluctuated over time. 235
From Fig.6, it is shown that the range of Vs(t) is increasing with scale, which implies that the 236
variability of Vs(t) could be scale dependent. For better understanding of this aspect we present the mean 237
and variability of the hourly Vs determined based on all storm events in our database, and render box plots 238
(Fig.8) to demonstrate the change in distributions of mean and STD of Vs(t) with respect to basins size. 239
The medians (in terms of absolute values) and length of value ranges of the mean of Vs(t) are increasing 240
with scale in panel a) of Fig.8 which is consistent with other works on this topic (Nikolopoulos, et al., 241
2013; Tarolli, et al., 2013). This implies that mean of event Vs(t) from larger basins are in general larger 242
and have higher degree of variability. Fig.8 panel b) displays another aspect of scale dependency by 243
means of standard deviation of event Vs(t). A positive shift (denoted by the shift of medians) from the 244
smallest to the largest basin can be revealed on the plot in panel b) of Fig.8, which corresponds to our 245
observation regarding the value range of Vs(t) in Fig.6. Hence, values of the event-based hourly Vs from 246
larger basin events are more extreme. In addition, it is interesting to note that the value range for standard 247
deviation of Vs(t) is expanding from the smallest to the largest basin pointing to the fact that the inter-248
event variability of Vs(t) is also scale dependent. 249
250
4 Framework Examination with hydrologic modeling 251
4.1 Hydrologic Model 252
In this section we carried out a series of hydrologic simulations, for all events examined, using as 253
input a) lumped and b) distributed rainfall, in order to quantify the effect of neglecting the rainfall spatial 254
variability on the hydrologic model application. The hourly discharge rate for the selected events from the 255
12
four study basins is simulated with the Hydrology Laboratory Research Modeling System (HL-RMS) 256
developed by National Weather Service (Koren, et al., 2004). HL-RMS is a flexible hydrologic modeling 257
system consisting of a well-tested conceptual water balance model currently adopted as the Sacramento 258
Soil Moisture Accounting Model (SAC-SMA) applied on a regular spatial grid and kinematic hillslope 259
and channel routing models. 260
The SAC-SMA is a well-developed and widely used conceptual rainfall-runoff watershed model 261
(refer to Koren et al. (2004) for model structure and other details) with 17 conceptual parameters (16 of 262
which cannot be measured directly). Koren et al. (2000) derived 11 major SAC-SMA parameters based 263
on a set of equations and the State Soil Geographic soil data (STATSGO). The flow routing component in 264
HL-RMS is divided into hillslope routing (overland flow) and channel routing. Values for the parameters 265
controlling overland flow were derived from high-resolution digital elevation model (DEM), land use 266
data, and results reported from initial tests on the model (NWS, et al., 2008). The channel routing 267
parameters were determined based on the measurements of Q and A data at the outlets of B1, B2, B3 and 268
B4 by following the rating curve method used by Koren et al. (2004). 269
Initial estimates of the remaining six model parameters were established based on previous 270
experience on different basins (Pokhrel, et al., 2008; Yilmaz, et al., 2008), and subsequently calibrated 271
using the Differential Evolution Adaptive Metropolis, DREAM (Vrugt, et al., 2009). DREAM employs 272
Markov Chain Monte Carlo sampling, which uses a formal likelihood function to estimate the posterior 273
probability density function of parameters in complex, high-dimensional sampling problems and separates 274
behavioral from non-behavioral solutions using a cutoff threshold that is based on the sampled probability 275
mass (Vrugt, et al., 2008). Hourly streamflow observations from 2004 to 2006 were used as the reference 276
in the calibration process to compute the sum of squared residuals (between observed and simulated 277
streamflow) that was chosen as the optimization criterion. The model validation was based on two 278
separate periods: 2002-2003 and 2007-2009. Fig.9 displays the simulation hydrographs for the selected 279
event discussed in previous section. Apart from the underestimation of peak flow, consistently for all 280
13
basins, the model captures well the time to peak and the general shape of observed hydrographs. 281
Quantitative statistics of the model performance are discussed next. 282
4.2 Evaluation of HL-RMS performance 283
In this section, we evaluate the performance of the calibrated HL-RMS model forced with the 284
distributed MPE radar-rainfall. Four comparative metrics based on simulated and observed runoff data are 285
calculated on event basis and include: the absolute relative error of event runoff volume (εV), absolute 286
relative error of event peak flow rate (εp), normalized root mean square error (εNRMS) and correlation 287
coefficient (ρ), which are determined as following: 288
(12)
(13)
(14)
(15)
where Vo (Qpo) and Vs (Qps) are the observed and simulated event runoff volume (event peak flow rate) 289
and Qo , Qs are the observed and simulated hourly runoff rate for every event; M is the total number of 290
hours for an event. 291
Table 3 lists the mean value and standard deviations of values of the metrics defined above. The mean 292
value of εV and εp for all the basins is around 30%; more than 85% of the events exhibit εV and εp values 293
less than 60%. These error metrics indicate reasonable performance results from the HL-RMS model 294
simulations. The flow volume simulations provided better error statistics than the peak flow rate 295
simulations. Results reported on Table 3 do not reveal any dependency of the error statistics on basin 296
scale, except for the εNRMS metric, which is shown to be inversely proportional to basin scale. Correlation 297
14
between simulated and observed streamflow is high for the majority of the events, with more than 80% of 298
B2 and B3 (and ~80% for B1) cases associated with correlation values above 0.8, while for the entire 299
basin (B4 basin) only 50% of the events gave correlations above 0.8. 300
4.3 Role of the Analytical Framework in Hydrologic Modeling 301
Aiming at understanding the interaction between the catchment morphological properties and rainfall 302
organization, Zoccatelli et al. (2011) (referred as Z2011 hereafter) introduce the concept of spatial 303
moments of catchment rainfall based on the framework proposed in Viglione et al. (2010a). Z2011 304
assumed than rainfall is not stationary and 2) calculated the hillslopes and channel routing time in terms 305
of a joint runoff travel time by considering a spatial constant runoff routing velocity (v). The Z2011 306
method is linked with two quantities of the hydrograph: a) the mean runoff time (i.e., the time of the 307
center of mass of the runoff hydrograph at a catchment outlet), and b) the variance of the timing of runoff 308
(i.e., the temporal dispersion of the runoff hydrograph). The expected value of catchment runoff time is a 309
surrogate for the time to peak; the variance of runoff time is indicative of the magnitude of the peakedness 310
(i.e. shape of the hydrograph). For a given event duration and volume of runoff, a sharply peaked 311
hydrograph will have a relatively low variance compared to a more gradually varying hydrograph 312
(Woods, 1997). 313
According to Z2011, the catchment flood response is conceptualized into two subsequent steps: 1) 314
rain falls on the catchment and is converted to an amount of runoff by the surface; 2) runoff transport 315
from that point to the catchment outlet. Hence, catchment runoff time Tq is treated as the summation of 316
the holding time for the two stages: 317
(16)
where Tr and Tc are the holding time for the first and the second stages respectively. Term Tr is assumed 318
to be equal to the instantaneous time t which is uniformly distributed as in Viglione et al. (2010a) 319
(V2010a hereafter). Therefore, the expectation and variance of catchment runoff time Tq are expressed as: 320
15
(17)
(18)
For E(Tr) and var(Tr), we refer to V2010a. E(Tc), var(Tc) and cov(Tr,Tc) are given in Z2011 as: 321
(19)
(20)
(21)
where v is the runoff routing velocity in m/s. Based on the components of E(Tq) and var(Tq) we note that 322
timing of hydrograph is not controlled by storm movement while both the rainfall spatial dispersion and 323
storm motion contributes to the hydrograph shape and to further extend the peak runoff. 324
Two sensitivity tests are conducted in the next two sub-sections to verify the controls on hydrograph 325
timing and magnitude by neglecting the rainfall spatial variability in modeling the hydrologic response of 326
basins. Two event-based difference statistics are derived for relating to Δ1, Δ2, and Vs: a) the difference in 327
timing of the mean values (dE) and b) the difference in dispersion around the mean values (dvar) between 328
distributed and basin-averaged rainfall forced hydrologic modeling. Before describing the statistics two 329
concepts are introduced first. The first concept is the hydrograph centroid (V2010a). The term ―centroid‖ 330
here refers to the expected value of time with respect to the hourly flow rate, i.e. statistically, the first 331
order origin moment of variable t weighted by hourly flow rate: 332
(22)
where Tf is the period of runoff event. Another concept is the dispersion of hydrograph around the 333
centroid; it is determined as the variance of time related to the flow rate. Thus, it is the second order 334
center moment of variable t weighted by hourly flow rate: 335
16
(23)
4.4 Control on Timing of Hydrograph 336
As previously mentioned, Δ1 reflects the spatial organization of catchment rainfall mass center with 337
respect to the flow length coordinate. For the cases with Δ1 larger than one (i.e. rainfall concentrated 338
towards basin’s periphery), a detention of the hydrograph centroid relative to the lumped (spatially 339
uniform) rainfall is expected. For events with Δ1 smaller than one (i.e. rainfall concentrated over basin’s 340
outlet), an advance in hydrograph timing is anticipated compared to hydrographs from the lumped rain. 341
Hence, the difference in timing of the mean value, or timing error, which is the time difference between 342
the centroid of the two types of hydrographs attained from the distributed and lumped rainfall forcing is 343
applied here to show its relation to Δ1: 344
(24)
Where Tq,d and Tq,l correspond to runoff time according to distributed and lumped rainfall forcing, 345
respectively. Applying the spatial moments of catchment rainfall and the associated assumptions we 346
derived dE as function of Δ1 (see Appendix for derivations): 347
(25)
A positive/negative value of dE implies a positive/negative shift in time of the distributed hydrograph with 348
respect to the one produced by using uniform precipitation. Namely, a positive correlation between Δ1 and 349
dE is anticipated. Additionally, the value of the slope and intercept are expected to be the same in number, 350
but different in sign. 351
The relationship between Δ1 and dE derived from simulated hydrographs according to Eq.(25) is 352
reported in Fig.10, depicting a linear trend especially for B2 and B3 basins. This suggests that Δ1 is able 353
to describe the control of rainfall spatial organization on the timing error of flood response for the basins 354
examined. Note from Fig.10 that for all basins, a value of Δ1 around 1 corresponds to a turning point 355
17
below (above) which the timing error becomes negative (positive) as indicated by the analytical 356
relationship of Eq.(25). Furthermore, a line was fitted (based on least-squares) to demonstrate the degree 357
of correlation between dE and Δ1 and investigate also the agreement between fitted coefficients (slope and 358
intercept) as indicated by Eq.(25). Results are summarized in Table 4. It is noted that the absolute values 359
of slope and intercept parameters are increasing with basin scale, which implies an increase in mean flow-360
length g1 values with basin areas referred as the Hack’s Law (Rigon, et al., 1996), considering that runoff 361
routing velocity v is similar in magnitude. The r2 values are greater than 0.8 for B2 and B3 indicating a 362
clear linear trend while drops to ~0.6-0.65 for B1 and B4. From a statistical perspective, presence of few 363
outliers (shown in Fig.10) may be the possible cause for the significant difference in correlation between 364
B2, B3 and B1, B4. Examination of the regression coefficients (Table 4) showed that slope and intercept 365
have almost equal and opposite in sign values, which further corroborates the validity of Eq.(25). 366
According to these results we may conclude that overall the difference in timing between distributed and 367
lumped rainfall hydrographs is well described by Eq.(25). 368
4.5 Control on the Shape of Hydrograph 369
Analogously, we tested the sensitivity of statistic Δ2 of every event to the difference in hydrograph 370
dispersion from distributed and basin-average rainfall forcing. It is noted that with the rainfall excess 371
volume remaining unchanged the effect of decreasing the variance of runoff time is to increase the flood 372
peak (Gaál, et al., 2012). However, since Eq.(18) involves the covariance between Tr and Tc, the 373
catchment storm velocity should have an effect in shaping the hydrograph. Consequently, we may write 374
dvar as: 375
(26)
Apply the spatial moments of catchment rainfall as well as the catchment scale storm velocity to develop 376
dvar (see Appendix): 377
(27)
18
Eq.(27) indicates that the event-based dvar is manipulated by both Δ2 and the product of Vs and square of 378
event duration |Ts|2. A positive (negative) value of dvar would imply a decrease (increase) of temporal 379
dispersion of the hydrograph generated by lumped rainfall with respect to the one produced by the 380
spatially distributed precipitation. 381
Events characterized by a near stationary storm (Vs very close to 0), dvar is the marginal distribution 382
of Δ2 based on Eq.(27): 383
(28)
Observations from a number of case studies have shown that flash floods are frequently characterized by 384
near stationary storm movement (Smith, et al., 2000; Sturdevant-Rees, et al., 2001). From this sense, a 385
relatively strong linearity between dvar and Δ2 may be seen for the flash flood generation rainfall events. 386
For events with extremely high rainfall spatial concentration (Δ2 fairly close to zero) for every time step 387
(rarely occur), dvar is the marginal distribution of Vs times |Ts|2: 388
(29)
In this case, the degree of dispersion is a function of Vs|Ts|2. Furthermore, if Vs is evaluated based on a 389
fixed length time window, dvar is proportional to Vs (|Ts| is constant). 390
Table 4 lists the regression coefficients between dvar, Δ2 and VsTs2. It is seen that the regression 391
intercept and the first slope coefficient are close to each other (with the exception of the B1 basin) while 392
the second slope coefficient is close to zero. Since Eq.(27) is unable to capture the tendency of the bulk 393
Δ2, Vs|Ts|2 and dvar in an efficient way (refer to the r
2 values in Table 4), we present a box plot (Fig.11) of 394
residuals between the model-calibrated dvar with respect to dvar attained from its regression function. As it 395
demonstrated in Fig.11, the residuals are distributed within a considerable range of values ([-448 402] for 396
B1, [-498 606] for B2, [-646 395] for B3 and [-1563 2079] for B4) with the medians having a non-397
negligible displacement from zero (especially for the B4 case). This implies a considerable large degree 398
of disagreement between the model-calculated dvar and the dvar derived from analytical framework. 399
19
Possible reason lies in the differences on assumption of routing kinematics. The Z2011 framework 400
lumped the hillslope routing and channel routing as runoff routing with constant routing velocity 401
spatiotemporally while deriving the relative parameters. These assumptions are acceptable for small scale 402
basins and flood events with bank-full condition (e.g. flash floods) (Rodríguez-Iturbe & Valdés, 1979; 403
Saco & Kumar, 2002). On the other hand, the HL-RMS differentiates hillslope from channel routing and 404
assigns spatiotemporal variable as the channel routing velocity. Namely, the analytical framework in 405
Z2011 and the hydrologic model in this study share different assumptions on the routing kinematics. 406
From the model, the standard deviations of channel routing velocity range between 0.03 and 0.06 m/s, 407
which indicates that the assumption of constant routing velocity does not hold for the hydrologic model. 408
Consequently, differences in routing schemes are the main cause of low efficiency in the regression of 409
Eq.(27). Moreover, due to the square operator of v in Eq.(27) the disagreement between the framework 410
and hydrologic model may be amplified. Nevertheless, as shown above the timing error of the hydrograph 411
is not as susceptible as the shape error to the manners of routing kinematics. 412
413
5 Conclusions 414
In this study we applied the concept of ―spatial moments of catchment rainfall‖ (i.e. first and second 415
order rainfall moment and catchment scale storm velocity presented in Z2011) to investigate the role of 416
rainfall spatial organization on flood response of mild-slope basins in the south Atlantic region of US. We 417
have concluded that values of the time-integrate second scale moment generally reflect the trend of the 418
time-integrate first scale moment with values of δ2 close to zero when δ1 is far from one, and values of δ2 419
around one when δ1 is close to unity. Neither of the Vs values determined based on the entire storm 420
duration or computed with a fixed-length (6 hour time) moving time-window were significantly different 421
than zero. With considerably large space-time rainfall variability, Vs(t) was found to be rainfall intensity 422
dependent, and its mean and variability was basin-scale dependent. 423
20
Another essential aspect of this study was to test the framework sensitivity with a distributed 424
hydrologic model. We used two error metrics determined based on model simulations forced with 425
distributed and basin-averaged rainfall to evaluate the framework statistics in representing the errors in 426
flood response. Results from both empirical equations relating modeling error metrics to the framework 427
statistics showed reasonable fitting. It was concluded that catchment response is relatively sensitive to the 428
spatial heterogeneity of rainfall quantified on the basis of Δ1, Δ2, and Vs especially for the dependency 429
between timing difference dE and Δ1. Specifically, strong linear dependency was exhibited between dE and 430
Δ1 even though they were carried out under routing kinematics with different properties. However, the 431
correlation was weak in terms of difference in peakedness of the hydrograph, due to again the differing 432
assumptions on routing between the conceptual framework and the distributed hydrologic model, i.e. 433
separated hillslope and channel vs. lumped routing processes as well as constant vs. spatiotemporal 434
variability v for the framework and model, respectively. It is concluded that different processes in routing 435
kinematics disrupt the shape of hydrograph more profoundly than the timing of it. 436
Overall, this study has demonstrated that the application of the concept of spatial moments of 437
catchment rainfall in the case of mild-slope terrain basins and moderate flood regimes can be used to 438
understand the effect of rainfall space-time organization on the timing of hydrologic response, but does 439
not provide a strong dependence on the variance of runoff time series. Further research should consider 440
performing hydrologic modeling on smaller scale basins with more uniform channel routing velocities 441
and where the hillslope routing process is not significant, and therefore, it would be reasonable to verify 442
the role of Δ2 and Vs on the dispersion of hydrograph. In addition, future studies could focus on complex-443
terrain flash-flood inducing storm events that are characterized with stationary storm velocity to evaluate 444
the rigorousness of the marginal relationship of dvar to Δ2. 445
446
Acknowledgment: This work was supported by a NASA Precipitation Measurement Mission award 447
(NNX07AE31G). 448
21
Appendix 449
Difference between centroids of hydrographs attained from distributed and lumped rain forcing in this 450
paper is defined as: 451
Since Tr is a temporal variable which is assumed uniformly distributed over Ts, E(Tr) from both models 452
are the same (refer to V2010a). Also note that Δ1 is equal to one for lumped rain. Therefore: 453
Difference in hydrograph peakedness related to the centroid is determined as: 454
Similar to the expectation, variance of Tr for both rainfall forcing is the same (see V2010a for details). Δ2 455
is one and Vs, or cov(Tr,l,Tc,l), is zero for lumped rain. So: 456
(A.1)
By applying the assumption that the instantaneous time t is uniformly distributed over Ts (V2010a), 457
Eq.(A.1) becomes Eq.(27): 458
Since 459
460
22
References 461
Blume, T., Zehe, E., & Bronstert, A. (2007). Rainfall—runoff response, event-based runoff coefficients 462
and hydrograph separation. Hydrol. Sci. J., 52(5), 843-862. doi:10.1623/hysj.52.5.843 463
Borga, M., Boscolo, P., Zanon, F., & Sangati, M. (2007). Hydrometeorological Analysis of the 29 August 464
2003 Flash Flood in the Eastern Italian Alps. J. Hydrometeor., 8(5), 1049-1067. 465
doi:10.1175/JHM593.1 466
Breidenbach, J. P., & Bradberry, J. S. (2001). Multisensor precipitation estimates produced by national 467
weather service river forecast centers for hydrologic applications. In K. J. Hatcher (Ed.), Proc. of 468
the 2001 Georgia Water Resources Conf. Athens, GA. 469
Carpenter, T. M., Sperfslage, J. A., Georgakakos, K. P., Sweeney, T., & Fread, D. L. (1999). National 470
threshold runoff estimation utilizing GIS in support of operational flash flood warning systems. J. 471
Hydrol., 224(1-2), 21-44. doi:10.1016/S0022-1694(99)00115-8 472
Dawdy, D. R., & Bergmann, J. M. (1969). Effect of rainfall variability on streamflow simulation. Water 473
Resour. Res., 5(5), 958-966. doi:10.1029/WR005i005p00958 474
de Lima, J. L., & Singh, V. P. (2002). The influence of the pattern of moving rainstorms on overland 475
flow. Adv. Water Resour., 25(7), 817-828. doi:10.1016/S0309-1708(02)00067-2 476
Fulton, R. A. (2002). Activities to improve WSR-88D radar rainfall estimation in the National Weather 477
Service. Proc. Second Federal Interagency Hydrologic Modeling Conf. Las Vegas, NV. 478
Retrieved from 479
http://www.nws.noaa.gov/oh/hrl/presentations/fihm02/pdfs/qpe_hydromodelconf_web.pdf 480
Gaál, L., Szolgay, J., Kohnová, S., Parajka, J., Merz, R., Viglione, A., & Blöschl, G. (2012). Flood 481
timescales: Understanding the interplay of climate and catchment processes through comparative 482
hydrology. Water Resour. Res., 48(4), W04511. doi:10.1029/2011WR011509 483
Georgakakos, K. (2005). Modern operational flash flood warning systems based upon flash flood 484
guidance- performance evaluation. International conference on innovation advances and 485
implementation of flood forecasting technology (pp. 1-10). Tromsø: HR Willingford. 486
Greene, D. R., & Hudlow, M. D. (1982). Hydrometeorological grid mapping procedures. Proc. 487
International Symposium on Hydrometeorology Conf. Denver, CO. 488
Gustard, A., Bullock, A., & Dixon, J. M. (1992). Low flow estimation in the United Kingdom. Institute of 489
Hydrology. Wallingford, UK: Institute of Hydrology. 490
Koren, V. I., Smith, M. B., Wang, D., & Zhang, Z. (2000). Use of Soil Property Data in the Derivation of 491
Conceptual Rainfall-Runoff Model Parameters. Paper read at 15th Conference on Hydrology, 492
AMS. Long Beach, CA. 493
Koren, V., Reed, M., Zhang, Z., & Seo, D.-J. (2004). Hydrology laboratory research modeling system 494
(HL-RMS) of the US national weather service. J. Hydrol., 291(3-4), 297-318. 495
doi:10.1016/j.jhydrol.2003.12.039 496
23
Merz, R., & Blöschl, G. (2003). A process typology of regional floods. Water Resour. Res., 39(12), 1340. 497
doi:10.1029/2002WR001952 498
Merz, R., Blöschl, G., & Parajka, J. (2006). Spatio-temporal variability of event runoff coefficients. J. 499
Hydrol., 331(3-4), 591-604. doi:10.1016/j.jhydrol.2006.06.008 500
Naden, P. S. (1992). Spatial variability in flood estimation for large catchments: the exploitation of 501
channel network structure. Hydrolog. Sci. J., 37(1), 53-71. doi:10.1080/02626669209492561 502
Nicótina, L., Alessi Celegon, E., Rinaldo, A., & Marani, M. (2008). On the impact of rainfall patterns on 503
the hydrologic response. Water Resour. Res., 44(12), W12401, 14. doi:10.1029/2007WR006654 504
Nikolopoulos, E., Borga, M., Zoccatelli, D., & Anagnostou, E. (2013). Catchment scale storm velocity: 505
Quantification, scale dependence and effect on flood response. Hydrol. Sci. J. (Accepted). 506
Norbiato, D., Borga, M., Degli Esposti, S., Gaume, E., & Anquetin, S. (2008). Flash flood warning based 507
on rainfall depth-duration thresholds and soil moisture conditions: An assessment for gauged and 508
ungauged basins. J. Hydrol., 362(3-4), 274-290. doi:10.1016/j.jhydrol.2008.08.023 509
Norbiato, D., Borga, M., Merz, R., Blöschl, G., & Carton, A. (2009). Controls on event runoff 510
coefficients in the eastern Italian Alps. J. Hydrol., 375(3-4), 312-325. 511
doi:10.1016/j.jhydrol.2009.06.044 512
NWS, OHD, HL, & HSMB. (2008). Hydrology Laboratory - Research Distributed Hydrologic Model 513
(HL-RDHM) User's Manual V 2.4.2. 514
Parajka, J., Kohnová, S., Bálint, G., Barbuc, M., Borga, M., Claps, P., . . . Blöschl, G. (2010). Seasonal 515
characteristics of flood regimes across the Alpine–Carpathian range. J. Hydrol., 394(1-2), 78-89. 516
doi:10.1016/j.jhydrol.2010.05.015 517
Pokhrel, P., Gupta, H. V., & Wagener, T. (2008). A spatial regularization approach to parameter 518
estimation for a distributed watershed model. Water Resour. Res., 44(12), w12419. 519
doi:10.1029/2007WR006615 520
Reed, S., & Maidment, D. (1999). Coordinate Transformations for Using NEXRAD Data in GIS-Based 521
Hydrologic Modeling. J. Hydrol. Eng., 4(2), 174-182. doi:10.1061/(ASCE)1084-522
0699(1999)4:2(174) 523
Reed, S., Schaake, J., Koren, V., Seo, D., & Smith, M. (2004). A Statistical-distributed Modeling 524
Approach for Flash Flood Prediction. 18th Conference on Hydrology. Boulder(CO): AMS. 525
Rigon, R., Rodriguez-Iturbe, I., Maritan, A., Giacometti, A., Tarboton, D. G., & Rinaldo, A. (1996). On 526
Hack's Law. Water Resour. Res., 32(11), 3367-3374. doi:10.1029/96WR02397 527
Rodríguez-Iturbe, I., & Valdés, J. B. (1979). The geomorphologic structure of hydrologic response. Water 528
Resour. Res., 15(6), 1409-1420. doi:10.1029/WR015i006p01409 529
Saco, P. M., & Kumar, P. (2002). Kinematic dispersion in stream networks 1. Coupling hydraulic and 530
network geometry. Water Resour. Res., 38(11), 1244. doi:10.1029/2001WR000695 531
24
Sangati, M., Borga, M., Rabuffetti, D., & Bechini, R. (2009). Influence of rainfall and soil properties 532
spatial aggregation on extreme flash flood response modelling: An evaluation based on the Sesia 533
river basin, North Western Italy. Adv. Water Resour., 32(7), 1090-1106. 534
doi:10.1016/j.advwatres.2008.12.007 535
Saulnier, G. M., & Le Lay, M. (2009). Sensitivity of flash-flood simulations on the volume, the intensity, 536
and the localization of rainfall in the Cévennes-Vivarais region (France). Water Resour. Res., 537
45(10), W10425. doi:10.1029/2008WR006906 538
Seo, Y., Schmidt, R., & Sivapalan, M. (2012). Effect of storm movement on flood peaks: Analysis 539
framework based on characteristic timescales. Water Resour. Res., 48(5), W05532. 540
doi:doi:10.1029/2011WR011761 541
Skøien, J. O., & Blöschl, G. (2006). Catchments as space-time filters – a joint spatio-temporal 542
geostatistical analysis of runoff and precipitation. Hydrol. Earth Syst. Sci. Discuss., 3, 941-985. 543
doi:10.5194/hessd-3-941-2006 544
Skøien, J. O., Blöschl, G., & Western, A. W. (2003). Characteristic space scales and timescales in 545
hydrology. Water Resour. Res., 39(10), 1304,19. doi:10.1029/2002WR001736 546
Smith, J. A., Baeck, M. L., Meierdiercks, K. L., Nelson, P. A., Miller, A. J., & Holland, E. J. (2005). 547
Field studies of the storm event hydrologic response in an urbanizing watershed. Water Resour. 548
Res., 41(10), W10413, 15. doi:10.1029/2004WR003712 549
Smith, J. A., Baeck, M. L., Morrison, J. E., & Sturdevant-Rees, F. (2000). Catastrophic Rainfall and 550
Flooding in Texas. J. Hydrometeor, 1(1), 5-25. doi:10.1175/1525-551
7541(2000)001<0005:CRAFIT>2.0.CO;2 552
Smith, J. A., Baeck, M. L., Morrison, J. E., Turner-Gillespie, D. F., & Bates, P. D. (2002). The Regional 553
Hydrology of Extreme Floods in an Urbanizing Drainage Basin. J. Hydrometeor., 3(3), 267-282. 554
doi:10.1175/1525-7541(2002)003<0267:TRHOEF>2.0.CO;2 555
Smith, M. B., Seo, D.-J., Koren, V. I., Reed, S. M., Zhang, Z., Duan, Q., . . . Cong, S. (2004). The 556
distributed model intercomparison project (DMIP): motivation and experiment design. J. Hydrol., 557
298(1-4), 4-26. doi:10.1016/j.jhydrol.2004.03.040 558
Sturdevant-Rees, P., Smith, J. A., Morrison, J., & Baeck, M. L. (2001). Tropical storms and the flood 559
hydrology of the central Appalachians. Water Resour. Res., 37(8), 2143-2168. 560
doi:10.1029/2000WR900310 561
Tarolli, M., Borga, M., Zoccatelli, D., Bernhofer, C., Jatho, N., & al Janabi, F. (2013). Rainfall space-time 562
organisation and orographic control on flash flood response: the August 13, 2002, Weisseritz 563
event. J. Hydrol. Eng., 18(2), 183-193. doi:10.1061/(ASCE)HE.1943-5584.0000569 564
van De Giesen, N. C., Stomph, T. J., & de Ridder, N. (2000). Scale effects of Hortonian overland flow 565
and rainfall–runoff dynamics in a West African catena landscape. Hydrol. Process., 14(1), 165-566
175. doi:10.1002/(SICI)1099-1085(200001)14:1<165::AID-HYP920>3.0.CO;2-1 567
25
van Loon, E. E., & Keesman, K. J. (2000). Identifying scale-dependent models: The case of overland flow 568
at the hillslope scale. Water Resour. Res., 36(1), 243-254. doi:10.1029/1999WR900266 569
Viglione, A., Chirico, G. B., Komma, J., Woods, R., Borga, M., & Blöschl, G. (2010b). Quantifying 570
space-time dynamics of flood event types. J. Hydrol., 394(1-2), 213-229. 571
doi:10.1016/j.jhydrol.2010.05.041 572
Viglione, A., Chirico, G. B., Woods, R., & Blöschl, G. (2010a). Generalised synthesis of space–time 573
variability in flood response: An analytical framework. J. Hydrol., 394(1-2), 198-212. 574
doi:10.1016/j.jhydrol.2010.05.047 575
Vrugt, J. A., ter Braak, C. J., Gupta, H. V., & Robinson, B. A. (2008). Equifinality of formal (DREAM) 576
and informal (GLUE) Bayesian approaches in hydrologic modeling? Stoch. Environ. Res. Risk 577
Assess., 23(7), 1011-1026. doi:10.1007/s00477-008-0274-y 578
Vrugt, J. A., ter Braark, C. J.-F., Diks, C. G.-H., Robinson, B. A., Hyman, J. M., & Higdon, D. (2009). 579
Accelerating Markov Chain Monte Carlo Simulation by Differential Evolution with Self-580
Adaptive Randomized Subspace Sampling. Int. J. Nonlin. Sci. Num., 10(3), 273-290. 581
doi:10.1515/IJNSNS.2009.10.3.273 582
Wilson, C. B., Valdes, J. B., & Rodriguez-Iturbe, I. (1979). On the influence of the spatial distribution of 583
rainfall on storm runoff. Water Resour. Res., 15(2), 321-328. doi:10.1029/WR015i002p00321 584
Wood, E. F., Sivapalan, M., Beven, K., & Band, L. (1988). Effects of spatial variability and scale with 585
implications to hydrologic modeling. J. Hydrol., 102(1-4), 29-47. doi:10.1016/0022-586
1694(88)90090-X 587
Woods, R. A. (1997). A search for fundamental scales in runoff generation : combined field and 588
modelling approach. PhD. Thesis. University of Western Australia., Dept. of Environmental 589
Engineering. 590
Woods, R. A., & Sivapalan, M. (1999). A synthesis of space-time variability in storm response: Rainfall, 591
runoff generation, and routing. Water Resour. Res., 35(8), 2469-2485. 592
doi:10.1029/1999WR900014 593
Yilmaz, K. K., Gupta, H. V., & Wagener, T. (2008). A process-based diagnostic approach to model 594
evaluation: Application to the NWS distributed hydrologic model. Water Resour. Res., 44(11), 595
W09417. doi:10.1029/2007WR006716 596
Zanon, F., Borga, M., Zoccatelli, D., Marchi, L., Gaume, E., Bonnifait, L., & Delrieu, G. (2010). 597
Hydrological analysis of a flash flood across a climatic and geologic gradient: The September 18, 598
2007 event in Western Slovenia. J. Hydrol., 394(1-2), 182-197. 599
doi:10.1016/j.jhydrol.2010.08.020 600
Zhang, Y., Smith, J. A., & Baeck, M. L. (2001). The hydrology and hydrometeorology of extreme floods 601
in the Great Plains of Eastern Nebraska. Adv. Water Resour., 24(9-10), 1037-1049. 602
doi:10.1016/S0309-1708(01)00037-9 603
26
Zoccatelli, D., Borga, M., Viglione, A., Chirico, G. B., & Blöschl, G. (2011). Spatial moments of 604
catchment rainfall: rainfall spatial organisation, basin morphology, and flood response. Hydrol. 605
Earth Syst. Sci., 8(3), 5811-5847. doi:10.5194/hessd-8-5811-2011 606
Zoccatelli, D., Borga, M., Zannon, F., Antonescu, B., & Stancalie, G. (2010). Which rainfall spatial 607
information for flash flood response modelling? A numerical investigation based on data from the 608
Carpathian range, Romania. J. Hydrol., 394(1-2), 148-161. doi:10.1016/j.jhydrol.2010.07.019 609
610
611
27
List of Tables 612
Table 1. Summary of flow-length and slope statistics ................................................................................ 29 613
Table 2. Summary of flood event statistics for the four basins ................................................................... 30 614
Table 3. HL-RMS runoff simulation error statistics ................................................................................... 31 615
Table 4. Parameters for Eq.(25) and (27) .................................................................................................... 32 616
617
28
List of Figures 618
Fig.1. Location and elevation map of the Tar-River basin ......................................................................... 33 619
Fig.2. Spatial distribution of mean annual precipitation (computed over the period 2002 to 2009) .......... 34 620
Fig.3. Illustration of sample flood events derived from the time-series of runoff data (December 2004 to 621
January 2005) .............................................................................................................................................. 35 622
Fig.4. Illustration of rainfall analysis for January 13th to 14
th, 2005: a) basin-averaged rainfall rate; b) 1
st 623
order moment of rainfall and c) 2nd
order moment of rainfall..................................................................... 36 624
Fig.5. Hourly snapshots of rainfall spatial organization from 11:00 to 16:00 on January 14th 2005 (rain 625
intensity in mm/h) ....................................................................................................................................... 37 626
Fig.6. Illustration of the temporal evolution of catchment scale storm velocity Vs(t) for January 13th to 627
14th, 2005..................................................................................................................................................... 38 628
Fig.7. Illustration of basin-averaged rainfall and storm velocity time series for January 13th to 14
th, 200539 629
Fig.8. Boxplot of Vs(t) variance for the four basins and for all storms examined. ...................................... 40 630
Fig.9. Illustration of HL-RMS runoff simulation versus observed runoff for a sample flood event at the 631
four basins ................................................................................................................................................... 41 632
Fig.10. Time-integrated first order moment of rainfall versus timing error for the four basins ................. 42 633
Fig.11. Box plot of residuals between model-calibrated dvar to predicted dvar for the four basins .............. 43 634
635
29
Table 1. Summary of flow-length and slope statistics 636
Basin ID B1 B2 B3 B4
Basin Area (km2) 1106 2012 2396 5654
Flow-length
Statistics
(km)
mean 56 110 111 142
std 26 49 56 66
max 108 199 214 287
Slope
Statistics
(°)
mean 3.2 2.9 2.7 2.3
std 2.2 2.1 2.0 1.9
max 32 32 32 32
637
30
Table 2. Summary of flood event statistics for the four basins 638
Basin ID B1 B2 B3 B4
Num. of event 44 42 40 38
Rainfall
Volume
(mm)
range [12.8, 124.5] [13.4, 123.8] [16.5, 128.7] [18.8, 221.7]
mean 42.1 49.6 54.5 61.0
|Ts|
(h)
range [12, 124] [11, 219] [12, 219] [28, 377]
mean 41 71 81 132
Direct flow
(mm)
range [3.7, 65.9] [4.4, 66.6] [3.9, 58.1] [3.8, 87.0]
mean 16.2 14.7 17.1 18.8
Tq
(h)
range [81, 558] [123, 551] [140, 573] [202, 1030]
mean 225 270 280 390
Peak flow
rate (m3/s)
range [32.6, 225.4] [50.1, 291.7] [53.0, 402.1] [103.9, 693.8]
mean 88.3 102.0 123.7 213.1
Baseflow
(mm)
range [0.1, 14.3] [0.5, 10.5] [0.6, 12. 9] [1.4, 23.8]
mean 3.9 4.8 4.4 9.5
RC
(%)
range [10.0, 80.5] [9.3, 71.4] [7.8, 79.9] [9.0, 73.1]
mean 39.8 30.7 31.5 29.9
639
31
Table 3. HL-RMS runoff simulation error statistics 640
B1 B2 B3 B4
εp
(%)
mean 27.13 31.86 31.64 28.16
STD 6.59 22.61 20.43 15.89
εV
(%)
mean 25.96 28.56 27.55 28.01
STD 5.01 13.12 13.74 9.83
εRMS mean 0.67 0.62 0.56 0.48
STD 0.28 0.44 0.31 0.25
ρ mean 0.82 0.81 0.86 0.75
STD 0.09 0.1 0.05 0.06
641
32
Table 4. Parameters for Eq.(25) and (27) 642
Basin ID B1 B2 B3 B4
Straight
Line
Intercept -31 -57 -61 -99
Slope 31 57 61 97
r2 0.58 0.84 0.82 0.65
Straight
Surface
Intercept -164 -640 -316 -1971
Slope1 202 638 326 1865
Slope2 0.09 0.02 0.03 0.02
r2 0.16 0.16 0.19 0.16
643
33
644
645
Fig.1. Location and elevation map of the Tar-River basin 646
34
647
Fig.2. Spatial distribution of mean annual precipitation (computed over the period 2002 to 2009) 648
35
649
Fig.3. Illustration of sample flood events derived from the time-series of runoff data 650
(December 2004 to January 2005) 651
36
652
Fig.4. Illustration of rainfall analysis for January 13th to 14
th, 2005: a) basin-averaged rainfall rate; b) 1
st 653
order moment of rainfall and c) 2nd
order moment of rainfall 654
37
11:00 12:00
13:00 14:00
15:00 16:00
Fig.5. Hourly snapshots of rainfall spatial organization from 11:00 to 16:00 on January 14th 2005 (rain 655
intensity in mm/h) 656
38
657
Fig.6. Illustration of the temporal evolution of catchment scale storm velocity Vs(t) for January 13th to 658
14th, 2005 659
39
660
Fig.7. Illustration of basin-averaged rainfall and storm velocity time series for January 13th to 14
th, 2005 661
40
662 Fig.8. Boxplot of Vs(t) variance for the four basins and for all storms examined. 663
41
664
Fig.9. Illustration of HL-RMS runoff simulation versus observed runoff for a sample flood event at the 665
four basins 666
42
667
Fig.10. Time-integrated first order moment of rainfall versus timing error for the four basins 668
43
669
Fig.11. Box plot of residuals between model-calibrated dvar to predicted dvar for the four basins 670
44
Highlights 688
Spatio‐temporal rainfall variability effects on flood modeling 689
Rainfall moments and storm velocity conceptual frameworks 690
Experimental framework to assess the conceptual frameworks’ predictability 691
692