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Flood Hydraulics project for the course Flood
Risk Evaluation
Prof. Alessio Radice
Group Members
v  Seyed Mohammad Sadegh (Arshia) Mousavi (836154)
v  Abdolreza Khalili (832669)
v  Omid Habibzadeh Bigdarvish (836722)
General Presentation
The Serio (Lombard: Sère[1][2]) is an
Italian river that flows entirely within
Lombardy, crossing the provinces of
Bergamo and Cremona. It is 124
kilometres (77 mi) long and flows into the
Adda at Bocca di Serio south of Crema.
Its valley is known as the Val Seriana.
3
General Presentation
General information
•  Length: 125 km
•  Area of basin: 1250 km2
•  Average discharge: around 25 m3/s
•  Water used for hydropower (famous falls
are activated some times every year) and
irrigation
Our models examines the last 15 km of the
river, from Crema to the confluence with the
Adda.
Data provided:
•  Cross sections (map and survey data)
•  Flood hydrograph
•  Geometry data incorporated into a project
of Hec‐Ras
•  Pictures of the reach
4
1-D Modeling – Introduction
5
Objective: 1‐D modeling of river flow in ordinary and peak conditions.
Steps:
²  Cross section data: choosing extent of main channel and roughness values for main channel
and floodplains
²  Completing geometry data: adding the bridge at section 6.1
²  Choosing discharge data and boundary conditions
²  Choosing levees
²  Running models:
v  Steady model with ordinary flow: Sensitivity analysis (roughness and BCs) and discussion
v  Steady model with peak flow: Sensitivity analysis (geometry, levees, roughness, BCs) and
discussion
v  Unsteady model for 200-year hydrograph: Sensitivity analysis (outflow + storage, single or
multiple) and discussion
1-D Modeling - Theoretical
6
Theoretical Background
HEC-RAS as an 1-D modeling software is based on the Saint Venant Equations. These equations are
obtained based on the following assumptions, generally satisfied in hydraulic processes:
o  flow is one-dimensional.
o  All the quantities can be described as continuous and derivable functions of longitudinal position
(s) and time (t).
o  Fluid is uncompressible.
o  Flow is gradually varied, and the pressure is distributed hydrostatically.
o  Bed slope is small enough to consider cross sections as vertical.
o  Channel is prismatic in shape.
o  Flow is fully turbulent.
Saint Venant Equations:
1-D Modeling - Theoretical
7
For special cases, these equations can be simplified as follows:
§  Steady flow with no temporal variation:
§  Steady flow with no spatial and temporal variability (Uniform flow):
In case of steady flow, modeling is simple: a constant discharge should be assign to the entire
reach, and a boundary condition for water level which would be at upstream for supercritical
flows or at downstream for subcritical flows.
1-D Modeling - Theoretical
8
Energy Head Loss
The change in the energy head
between adjacent sections equals the
head loss. The head loss occurring
between two cross-sections is
consisting of the sum of the
frictional losses and expansion or
contraction losses.
The energy head is given by:
1-D Modeling - Theoretical
9
In case of unsteady flow, an initial condition is necessary together with an upstream
boundary condition (usually a discharge hydrograph) and a second boundary condition
which must be upstream for supercritical flows or downstream for subcritical flow.
Characteristic Depths
Critical Depth dc:
The depth for which the specific energy is minimum is called the critical depth.
When dc>d the flow is called supercritical (velocity larger than that for critical flow).
When dc<d the flow is subcritical.
1-D Modeling - Theoretical
10
Normal Depth d0:
If no quantity varies with the longitudinal direction, the flow is called uniform, and the
momentum equation representing the process is S0=Sf. The depth for which this happens is
called the normal depth.
For a given discharge, Sf is a decreasing function of water depth, therefore:
d>d0 ⇒S0 >Sf
d<d0 ⇒S0 <Sf
1-D Modeling - Theoretical
11
Steady model for the ordinary flow
Length: 125 km
Average discharge: 25 m3/s
S0= 0.15%
1-D Modeling Description
12
1-D Modeling Description
13
Main channel bank stations
The left and the right bank values are inserted in the HEC-RAS software considering the
width of the channel in the map and trying to find the nodes having roughly the same
distance.
1-D Modeling Description
14
Manning Roughness Coefficient:
There is no exact method for selecting n values. At the present stage of knowledge to select a
value of n actually means to estimate the resistance to flow in a given channel which is really
a matter of intangibles.
So for this issue, different individuals will obtain different results, such as:
1.  experience; comparison with similar systems
2.  calibration over past (and known) events
3.  sensitivity analysis
For the Calibration of the main channel, left and right banks of the channel we considered the
USGS data for the rivers.
1-D Modeling Description
15
Manning Coefficient:
²  The values of roughness for main channel, left and right banks are selected based on the map of
the area and provided pictures of the sections. These values are obtained from the “Verified
Roughness Characteristics of Natural Channels” provided by USGS website.
²  The Manning coefficient of main channel has been selected n=0.038 whereas for the sensitivity
analysis considered n=0.028 and n=0.041.
²  In addition, different manning values have been observed for the three cases with respect to the
Hec-Ras software’s table.
1-D Modeling Description
Serio River
Clark Fork River
USGS
N=0.028
16
Manning Coefficient (n) in Flood Plains:
Left and Right Coefficients bank corresponding to n=0.028
1-D Modeling Description
Left%Bank 0.035 Light%Brush%&%tress%in%winter
Right%Bank 0.035 Light%Brush%&%tress%in%winter
Left%Bank 0.035 Light%Brush%&%tress%in%winter
Right%Bank 0.025 Short%Grass
Left%Bank 0.035 Light%Brush%&%tress%in%winter
Right%Bank 0.025 Short%Grass
Left%Bank 0.025 Short%Grass
Right%Bank 0.08 Heavy%stand%of%timber,%Few%down%trees
Left%Bank 0.035 Light%Brush%&%tress%in%winter
Right%Bank 0.08 Heavy%stand%of%timber,%Few%down%trees
Left%Bank 0.035 Light%Brush%&%tress%in%winter
Right%Bank 0.035 Light%Brush%&%tress%in%winter
Left%Bank 0.025 Short%Grass
Right%Bank 0.025 Short%Grass
Left%Bank 0.028
Right%Bank 0.028
Left%Bank 0.028
Right%Bank 0.028
Left%Bank 0.025 Short%Grass
Right%Bank 0.035 Light%Brush%&%tress%in%winter
Left%Bank 0.035 Light%Brush%&%tress%in%winter
Right%Bank 0.025 Short%Grass
Left%Bank 0.035 Light%Brush%&%tress%in%winter
Right%Bank 0.035 Light%Brush%&%tress%in%winter
Left%Bank 0.035 Light%Brush%&%tress%in%winter
Right%Bank 0.035 Light%Brush%&%tress%in%winter
6.15
7
Bridge%Sections%(Main%Channel%value)
8
8.1
8.2
5
6
6.05
2.1
3
4
1
2
Sections Left / Right Bank Value Description
Left%Bank 0.025 Short%Grass
Right%Bank 0.035 Light%Brush%&%tress%in%winter
Left%Bank 0.035 Light%Brush%&%tress%in%winter
Right%Bank 0.035 Light%Brush%&%tress%in%winter
Left%Bank 0.025 Short%Grass
Right%Bank 0.035 Light%Brush%&%tress%in%winter
Left%Bank 0.045 Medium%to%dense%brush
Right%Bank 0.025 Short%Grass
Left%Bank 0.045 Medium%to%dense%brush
Right%Bank 0.035 Light%Brush%&%tress%in%winter
Left%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts
Right%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts
Left%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts
Right%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts
Left%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts
Right%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts
Left%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts
Right%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts
Left%Bank 0.035 Light%Brush%&%tress%in%winter
Right%Bank 0.035 Light%Brush%&%tress%in%winter
Left%Bank 0.045 Medium%to%dense%brush
Right%Bank 0.035 Light%Brush%&%tress%in%winter
Left%Bank 0.035 Light%Brush%&%tress%in%winter
Right%Bank 0.035 Light%Brush%&%tress%in%winter
Left%Bank 0.035 Light%Brush%&%tress%in%winter
Right%Bank 0.035 Light%Brush%&%tress%in%winter
Left%Bank 0.035 Light%Brush%&%tress%in%winter
Right%Bank 0.035 Light%Brush%&%tress%in%winter
15.1
20
16
17
18
19
13
14
15
11
12
12.1
Value Description
9
10
Sections Left / Right Bank
17
Manning Coefficient (n) in Flood Plains:
Left and Right Coefficients bank corresponding to n=0.038
1-D Modeling Description
Left%Bank 0.05 Light%Brush%&%tress%in%winter
Right%Bank 0.05 Light%Brush%&%tress%in%winter
Left%Bank 0.05 Light%Brush%&%tress%in%winter
Right%Bank 0.03 Short%Grass
Left%Bank 0.05 Light%Brush%&%tress%in%winter
Right%Bank 0.03 Short%Grass
Left%Bank 0.03 Short%Grass
Right%Bank 0.1 Heavy%stand%of%timber,%Few%down%trees
Left%Bank 0.05 Light%Brush%&%tress%in%winter
Right%Bank 0.1 Heavy%stand%of%timber,%Few%down%trees
Left%Bank 0.05 Light%Brush%&%tress%in%winter
Right%Bank 0.05 Light%Brush%&%tress%in%winter
Left%Bank 0.03 Short%Grass
Right%Bank 0.03 Short%Grass
Left%Bank 0.038
Right%Bank 0.038
Left%Bank 0.038
Right%Bank 0.038
Left%Bank 0.03 Short%Grass
Right%Bank 0.05 Light%Brush%&%tress%in%winter
Left%Bank 0.05 Light%Brush%&%tress%in%winter
Right%Bank 0.03 Short%Grass
Left%Bank 0.05 Light%Brush%&%tress%in%winter
Right%Bank 0.05 Light%Brush%&%tress%in%winter
Left%Bank 0.05 Light%Brush%&%tress%in%winter
Right%Bank 0.05 Light%Brush%&%tress%in%winter
Bridge%Sections%(Main%Channel%value)
Sections Left / Right Bank Value Description
1
2
2.1
3
4
5
8.2
8.1
6
6.05
6.15
7
8
Left%Bank 0.03 Short%Grass
Right%Bank 0.05 Light%Brush%&%tress%in%winter
Left%Bank 0.05 Light%Brush%&%tress%in%winter
Right%Bank 0.03 Light%Brush%&%tress%in%winter
Left%Bank 0.05 Short%Grass
Right%Bank 0.03 Light%Brush%&%tress%in%winter
Left%Bank 0.03 Medium%to%dense%brush
Right%Bank 0.1 Short%Grass
Left%Bank 0.05 Medium%to%dense%brush
Right%Bank 0.1 Light%Brush%&%tress%in%winter
Left%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts
Right%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts
Left%Bank 0.03 Cleared%land%with%tree%stumps%but%heavy%sprouts
Right%Bank 0.03 Cleared%land%with%tree%stumps%but%heavy%sprouts
Left%Bank 0.038 Cleared%land%with%tree%stumps%but%heavy%sprouts
Right%Bank 0.038 Cleared%land%with%tree%stumps%but%heavy%sprouts
Left%Bank 0.038 Cleared%land%with%tree%stumps%but%heavy%sprouts
Right%Bank 0.038 Cleared%land%with%tree%stumps%but%heavy%sprouts
Left%Bank 0.038 Light%Brush%&%tress%in%winter
Right%Bank 0.038 Light%Brush%&%tress%in%winter
Left%Bank 0.03 Medium%to%dense%brush
Right%Bank 0.05 Light%Brush%&%tress%in%winter
Left%Bank 0.05 Light%Brush%&%tress%in%winter
Right%Bank 0.03 Light%Brush%&%tress%in%winter
Left%Bank 0.05 Light%Brush%&%tress%in%winter
Right%Bank 0.05 Light%Brush%&%tress%in%winter
Left%Bank 0.05 Light%Brush%&%tress%in%winter
Right%Bank 0.05 Light%Brush%&%tress%in%winter
14
15
15.1
16
Left / Right Bank Value Description
9
10
13
Sections
11
12
12.1
17
18
19
20
18
Manning Coefficient (n) in Flood Plains:
Left and Right Coefficients bank corresponding to n=0.041
1-D Modeling Description
Left%Bank 0.06 Light%Brush%&%tress%in%winter
Right%Bank 0.06 Light%Brush%&%tress%in%winter
Left%Bank 0.06 Light%Brush%&%tress%in%winter
Right%Bank 0.035 Short%Grass
Left%Bank 0.06 Light%Brush%&%tress%in%winter
Right%Bank 0.035 Short%Grass
Left%Bank 0.035 Short%Grass
Right%Bank 0.12 Heavy%stand%of%timber,%Few%down%trees
Left%Bank 0.06 Light%Brush%&%tress%in%winter
Right%Bank 0.12 Heavy%stand%of%timber,%Few%down%trees
Left%Bank 0.06 Light%Brush%&%tress%in%winter
Right%Bank 0.06 Light%Brush%&%tress%in%winter
Left%Bank 0.035 Short%Grass
Right%Bank 0.035 Short%Grass
Left%Bank 0.041
Right%Bank 0.041
Left%Bank 0.041
Right%Bank 0.041
Left%Bank 0.035 Short%Grass
Right%Bank 0.06 Light%Brush%&%tress%in%winter
Left%Bank 0.06 Light%Brush%&%tress%in%winter
Right%Bank 0.035 Short%Grass
Left%Bank 0.06 Light%Brush%&%tress%in%winter
Right%Bank 0.06 Light%Brush%&%tress%in%winter
Left%Bank 0.035 Light%Brush%&%tress%in%winter
Right%Bank 0.06 Light%Brush%&%tress%in%winter
6.15
7
Bridge%Sections%(Main%Channel%value)
8
8.1
8.2
5
6
6.05
2.1
3
4
1
2
Sections Left / Right Bank Value Description
Left%Bank 0.035 Short%Grass
Right%Bank 0.06 Light%Brush%&%tress%in%winter
Left%Bank 0.06 Light%Brush%&%tress%in%winter
Right%Bank 0.06 Light%Brush%&%tress%in%winter
Left%Bank 0.035 Short%Grass
Right%Bank 0.06 Light%Brush%&%tress%in%winter
Left%Bank 0.11 Medium%to%dense%brush
Right%Bank 0.035 Short%Grass
Left%Bank 0.11 Medium%to%dense%brush
Right%Bank 0.06 Light%Brush%&%tress%in%winter
Left%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts
Right%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts
Left%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts
Right%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts
Left%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts
Right%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts
Left%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts
Right%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts
Left%Bank 0.06 Light%Brush%&%tress%in%winter
Right%Bank 0.06 Light%Brush%&%tress%in%winter
Left%Bank 0.11 Medium%to%dense%brush
Right%Bank 0.06 Light%Brush%&%tress%in%winter
Left%Bank 0.06 Light%Brush%&%tress%in%winter
Right%Bank 0.06 Light%Brush%&%tress%in%winter
Left%Bank 0.06 Light%Brush%&%tress%in%winter
Right%Bank 0.06 Light%Brush%&%tress%in%winter
Left%Bank 0.06 Light%Brush%&%tress%in%winter
Right%Bank 0.06 Light%Brush%&%tress%in%winter
15.1
20
16
17
18
19
13
14
15
11
12
12.1
Value Description
9
10
Sections Left / Right Bank
19
1-D Modeling Description
Serio River
Manning Coefficient (n) in Flood Plains:
Left and Right Coefficients bank corresponding to n=0.028
20
1-D Modeling Description
Manning Coefficient (n) in Flood Plains:
Left and Right Coefficients bank corresponding to n=0.038
Serio RiverMoyie River
21
1-D Modeling Description
Manning Coefficient (n) in Flood Plains:
Left and Right Coefficients bank corresponding to n=0.041
Middle Fork River
Serio River
22
Floodplain
Section 1
1-D Modeling Description
23
Bridge:
v  At the section 6.1, a bridge is added to the channel.
v  We accomplished this by adding one section to the upstream, one section to downstream and one
section at the location of the structure.
v  The total width of the bridge is 10m.
v  The distance between these three sections (6.05-6.1-6.15) is10m from the middle section of the
bridge.
1-D Modeling Steady – Ordinary Flow
24
1-D Modeling Steady – Ordinary Flow
Bridge
Create a section before (6.15)
Create a section after (6.05)
Delete section 6.1
Insert the bridge (6.1)
25
Ordinary Flow
Bridge Section (Sec. 6.1)
26
Limitations Considerations of 1D Modeling
v  Since HEC-RAS is a 1D modeling software, it cannot consider whether water can move
across the main channel to the flood plains or not. Therefore, if the bed elevation at
floodplain is lower than water surface, HEC-RAS will consider water flows into the
flood plains. And in this case levee should be added to the section. For this issue, we
have considered both view 3D multiple cross section plot and view cross sections.
v  In ordinary flow (Q=25 m^3/sec), there are two necessity to add levees in Sections 2
and 8_1, after adding these levees water does not exist in the flood plains.
v  The presence of levees is specially required for the steady peak flow and the unsteady
simulation based on 200 years hydrograph.
1-D Modeling Description
27
1-D Modeling Description
Adding Levee in Section 2
3D View
Cross Section View
28
Levee
Cross Section View
3D View
1-D Modeling Description
Section 2
(After adding Levee)
29
1-D Modeling Description
Adding Levee in Section 8.1
As can be seen, in the section 8.1, a levee is added to the right of the main channel.
Since HEC-RAS is a 1-D modeling software, it cannot consider whether water can
move across the main channel to the banks or not. Thus, if the water surface is
higher than the bed elevation at the floodplain water, HEC-RAS will consider
water flows into the banks. To avoid this issue, in the section 8.1 in our model, a
levee has to be added.
30
1-D Modeling Description
Section 8.1
(After adding Levee)
Section 8.1
(Before adding Levee)
31
1-D Modeling Description – Ordinary Flow
Overall 3D View after adding levee (All Sections )
32
Boundary Conditions
Ø  The discharge for the ordinary flow is 25 m3/s.
Ø  The boundary conditions for the river depend on the nature of the flow. In the case of
subcritical flow, we have to input just downstream condition and for supercritical flows,
just upstream condition is needed.
Ø  By running the model with some assumed boundary conditions (critical flow at upstream
and normal flow at downstream), it was noted that the Froude Number along the channel
is lower than 1. Therefore, the flow is subcritical and just downstream boundary
condition has to be set. To do so, a sensitivity analysis of the boundary condition need to
be done.
Ø  For the Reference scenario we have chosen the normal depth for the downstream and
Critical depth for the upstream.
1-D Modeling Description
33
1-D Modeling Description
Longitudinal Profile
34
Ordinary Flow
3D View (without Flood)
35
Ordinary Flow
Bridge Section (Sec. 6.1)
36
Ordinary Flow
Bridge Section (Sec. 6.1)
The contraction in the bridge section causes the flow depth to change. Since the flow is
subcritical, water elevation decreases after the bridge and gets close to the critical depth.
37
Ordinary Flow
Sensitivity Analysis for Boundary Condition
To check the sensitivity of the results with respect to the boundary conditions, 5
sets of boundary conditions are considered and their results are compared:
1. Upstream Normal flow and Downstream Normal flow (S=0.0015)
2. Upstream Normal flow and Downstream Critical flow
3. Upstream Critical flow and Downstream Normal flow (S=0.0015) (Reference Scenario)
4. Upstream Critical flow and Downstream Critical flow
5. Upstream Normal flow and Downstream fixed Water Surface Elevation: 47.51
(45.71 Bed Elevation + 1.8 m Water Depth)
38
1-D Modeling Description
Water Surface for different boundary conditions
39
Ordinary Flow
Results: Velocity Conditions
Noticeable rise in water velocity in cases 2 and 4 (water level tends to critical depth)
Velocity for different boundary conditions
40
Ordinary Flow
Sensitivity Analysis for Boundary Condition
Results
1.  In whole profile (except bridge section) different boundary condition in upstream
makes no change in water profile. Because water level is over critical depth in whole
reach (subcritical flow) and just in case of a supercritical flow upstream boundary
condition affect our water profile.
2.  At this project (subcritical flow) the downstream boundary condition affect the water
profile. Water level variation is occurred in the last 4 stations (downstream).
41
Ordinary Flow
Roughness Sensitivity Analysis
In applying the Manning number the greatest difficulty lies in the determination of the
roughness coefficient n; there is no exact method of selecting the n value. In the present
study, comparison with similar system of the other rivers has been carried out based on the
database: “Verified Roughness Characteristics of Natural Channels” provided by USGS
website.
︎In ordinary flow water exists only in main channel therefore the simulation is only dependent
on the manning coefficient of main channel and not left and right banks. Therefore for flood
plains same manning coefficient has been chosen.
︎To study the roughness sensitivity, the manning coefficients are once increased from n=0.038
(reference coefficient) to n=0.041 and once decreased from n=0.038 to 0.028
The roughness sensitivity is evaluated regarding two aspects:
In this analysis two aspects have been considered:
v  Water Surface elevation
v  Velocity
42
Ordinary Flow
Roughness Sensitivity Analysis
v Water Surface elevation
v  Velocity
Considering the graph provided, it is easy to observe that by increasing the manning
coefficient (n), the water surface elevation is raised. However, generally speaking different
manning coefficient values (n), have provided almost the same water surface elevation
compared to the dimension of our channel. This hypothesis will be examined later in this
project.
An important point of this graph, is the behavior seen at the location of the bridge. It is clear
that regardless of the magnitude of the manning coefficient, the water surface elevation
approach to the same level for all conditions. This may indicate that in this specific location,
due to the contraction caused by the bridge piers, a critical condition has occurred. Checking
the Fr=1 in this location verifies this speculation. The results obtained from the HEC-RAS
model verifies that the flow is subcritical before and after this location while, when the flow
reaches the bridge, the flow is critical.
43
Ordinary Flow
Profile Output Table for reference scenario
44
Ordinary Flow
Sensitivity Analysis for Boundary Condition
Results: Water Surface
Noticeable rise in water velocity in cases 2 and 4 (water level tends to critical depth)
45
Ordinary Flow
Roughness Sensitivity Analysis
v  Water Surface elevation
v Velocity
Two points can we concluded from the velocity graph.
1.  The graph with higher Manning’s value causes lower velocity as expected.
2.  The increase in roughness results in the rise of the water surface elevation. The higher
water surface elevation yield lower velocity of the flow.
46
Ordinary Flow
Velocity sensitivity analysis
47
Peak Flow
v  Average discharge 561.12 m3/s (based on peak value of 200 –year hydrograph)
Levees
²  13 sections need adding levees to control flood plain.
²  Criteria for deciding whether to add levee or not:
1.  Considering the residential areas and facilities close to the flood plain.
2.  If the bed elevation is lower than water surface HEC-RAS will consider this
area as a flooded area, so levees are required to avoid this issue.
Peak Flow Properties
48
Peak Flow
Adding Levee Section 20
Before Levee
After Levee
49
Peak Flow
Adding Levee Section 18
Before Levee
After Levee
50
Peak Flow
Adding Levee Section 17
Before Levee
After Levee
51
Peak Flow
Adding Levee Section 16
Before Levee
After Levee
52
Peak Flow
Adding Levee Section 14
Before Levee
After Levee
53
Peak Flow
Adding Levee Section 13
Before Levee
After Levee
54
Peak Flow
Adding Levee Section 12
Before Levee
After Levee
55
Peak Flow
Adding Levee Section 11
Before Levee
After Levee
56
Peak Flow
Adding Levee Section 5
Before Levee
After Levee
57
Peak Flow
Adding Levee Section 4
Before Levee
After Levee
58
Peak Flow
Adding Levee
Section 3
Before Levee
After Levee
59
Peak Flow
Adding Levee
Section 2
Before Levee
After Levee
60
Peak Flow
Adding Levee Section 1
Before Levee
After Levee
61
Peak Flow
3D View (With Flood & After adding levee)
62
Peak Flow
Sensitivity analysis in case of adding levee and omitting cross sections
63
Peak Flow
Sensitivity analysis in case of adding levee and eliminating cross sections
Section Elevation Difference
16 0.3
13 0.4
9 0.2
Differences in water elevation
Comparing the graphs and the results of the two sets of data:
1.  No elimination of cross sections and No levees.
2.  With levees and eliminating some cross sections.
We can observe that in the upstream sections (16, 13, 9) of the eliminated cross
sections (15.1, 12.1, 8.2, 8.1) the elevation of the water is increased after adding the
levees and eliminating the mentioned cross sections by the values provided in the
above table.
m
m
m
64
Peak Flow
Sensitivity analysis in case of adding levee and eliminating cross sections
Comparing the graphs and the results of the two sets of data:
1.  No levees and No elimination in cross sections.
2.  With levees, No eliminating cross sections.
We can observe that the graph belonging to the case of no levee and no elimination
is always lower or equal to the one related to the case of having levees but no
elimination in cross sections.
Comparing the graphs and the results of the two sets of data:
1.  No levees and with elimination of cross sections.
2.  With levees, No eliminating cross sections.
One could notice that by eliminating the cross sections (case 1) the water surface
level would decrease.
65
Peak Flow
Sensitivity Analysis for Boundary Condition
To check the sensitivity of the results with respect to the boundary conditions, 5
sets of boundary conditions are considered and their results are compared:
1. Upstream Normal flow and Downstream Normal flow (S=0.0015)
2. Upstream Normal flow and Downstream Critical flow
3. Upstream Critical flow and Downstream Normal flow (S=0.0015) (Reference Scenario)
4. Upstream Critical flow and Downstream Critical flow
5. Upstream Normal flow and Downstream fixed Water Surface Elevation: 51.71
(45.71 Bed Elevation + 6 m Water Depth)
66
Peak Flow
Longitudinal Profile
67
Peak Flow
Velocity
68
Peak Flow
Sensitivity Analysis for Boundary Condition
Results
One could observe that different boundary condition would result in the same velocity
except in the case of sections in the downstream of the river in which the difference is due
to the different boundary conditions applied there.
69
Peak Flow
Roughness Sensitivity Analysis
In applying the Manning number the greatest difficulty lies in the determination of the
roughness coefficient n; there is no exact method of selecting the n value. In the present
study, comparison with similar system of the other rivers has been carried out based on the
database: “Verified Roughness Characteristics of Natural Channels” provided by USGS
website.
︎In the peak flow water is not only flowing in the main channel as it was in the case of
ordinary flow explained earlier. Left and right bank also contain a portion of water flow so
different manning coefficient in the banks is also applied.
︎
The roughness sensitivity is evaluated regarding two aspects:
In this analysis two aspects have been considered:
v  Water Surface elevation
v  Velocity
70
Peak Flow
Roughness Sensitivity Analysis
v Water Surface elevation
v  Velocity
For this type of flow, the result obtained in the case of ordinary flow are true. Moreover, it is
clear that regardless of the magnitude of the manning coefficient, the water surface elevation
approach to the same level for all conditions for the bridge section. Moreover it is observed
that the water surface along the channel is always above the critical depth. Meaning that
there is subcritical flow in the whole channel.
71
Peak Flow
Roughness Sensitivity Analysis
v Water Surface elevation
72
Peak Flow
Roughness Sensitivity Analysis
v  Water Surface elevation
v Velocity
Two points can we concluded from the velocity graph.
1.  The graph with higher Manning’s value causes lower velocity as expected.
2.  The increase in roughness results in the rise of the water surface elevation. The higher
water surface elevation yield lower velocity of the flow.
73
Peak Flow
Roughness Sensitivity Analysis
v  Water Surface elevation
v Velocity
74
Peak Flow
Roughness Sensitivity Analysis
Results:
q  ︎︎While the difference in the water surface elevation and velocity of both
peak and ordinary flow in the case of different (n) values is relatively
small, we could observe that the difference in the case of peak flow is
larger. In the other words, peak flow results are more sensitive to
manning coefficient.
q  To conclude, one could state that to use the manning coefficient
considering the similar river sections of the USGS and predict the case
of river Serio, is acceptable.
75
Unsteady Model
Unsteady model for 200-year Hydrograph
To model for the unsteady flow, all the parameters from steady models are
used. In this case different flow rates is considered for different sections of
the river based on the excel sheet provided.
§  Model conditions
§  Boundary condition
Upstream: 200-year hydrograph
Downstream: normal depth with slope of 0.0015
§  Initial condition
Initial discharge
76
Unsteady Model
Unsteady flow data
The original dataset is interpolated with 60 minute time interval. This time interval is
small enough with respect to the whole event history ( 200 years).
77
Longitudinal Profile of the corrected geometry
Unsteady Flow
78
Unsteady flow
3D View (Flooded Areas):
79
Unsteady Model
40
42
44
46
48
50
52
54
56
58
60
62
64
66
68
0 2000 4000 6000 8000 10000 12000 14000 16000
Steady Vs. Unsteady flow
bed
steady flow
unsteady flow
Comparison: Steady and Unsteady elevation analysis (at max. water profile)
80
Comparison: Steady and unsteady discharge analysis (at max. water profile)
Unsteady Model
525
530
535
540
545
550
555
560
565
0 2000 4000 6000 8000 10000 12000 14000 16000
Steady Vs. Unsteady
unsteady
steady
81
0
0.5
1
1.5
2
2.5
3
3.5
0 2000 4000 6000 8000 10000 12000 14000 16000
steady Vs. Unsteady
unsteady
steady
Comparison: Steady and unsteady velocity analysis (at max. water profile)
Unsteady Model
82
Unsteady Model
Results:
v  It can be observed that the maximum difference between the steady and
unsteady flow discharge values is 5.87 percent. This amount shows the loss of
Q by considering unsteady type of flow.
v  The values of discharge, velocity and water surface elevation are relatively
similar in the case of analyzing Serio river. This could be explained by the fact
that the difference between steady and unsteady values is dominant only if the
channel profile is long enough.
83
Two Dimensional (2D) Modeling
Theoretical Background
84
Two Dimensional (2D) Modeling
Theoretical Background
85
Two Dimensional (2D) Modeling
Theoretical Background
The 2D model depth averaged, mass and momentum conservation equations are:
The bed shear stress are computed by:
The turbulent normal and shear stresses are computed according to the
Boussinesq’s assumption as:
86
Two Dimensional (2D) Modeling
Benefits
Ø  ︎Ability to model more complex flows including
floodplain and underground flows
Ø  ︎Ability to consider impact of obstructions.
Ø  ︎ No need to force the geometry to be appropriate
for modeling
Limitations
v  If the phenomenon is abrupt, the 1D model
contains discontinuities that water would hardly
follow.
v  ︎Results are limited by the accuracy of the
assumptions, input data and the computing power
of the computer program.
v  Modeling complexity and precision are not a
substitute for sound engineering judgment
87
Two Dimensional (2D) Modeling
Comparing the results of 2-D with 1D
Since River 2D results 2 values for velocity along the X and Y axes,
and computes the water depth at each node, it is not possible to have
single longitudinal profiles for velocity and water surface for the river.
Therefore, the results are compared section by section
88
Two Dimensional (2D) Modeling
89
Two Dimensional (2D) Modeling
Comparison between 1D & 2D analysis (Section 9)
90
Two Dimensional (2D) Modeling
Comparison between 1D & 2D analysis (Section 10)
91
Two Dimensional (2D) Modeling
Comparison between 1D & 2D analysis (Section 11)
92
Two Dimensional (2D) Modeling
Comparison between 1D & 2D analysis (Section 12)
93
Two Dimensional (2D) Modeling
Comparison between 1D & 2D analysis (Section 13)
94
Two Dimensional (2D) Modeling
Comparison between 1D & 2D analysis (Section 14)
95
Two Dimensional (2D) Modeling
Comparison between 1D & 2D analysis (Section 15)
96
Two Dimensional (2D) Modeling
Comparison between 1D & 2D analysis (Section 16)
97
Two Dimensional (2D) Modeling
Comparison between 1D & 2D analysis (Section 17)
98
Two Dimensional (2D) Modeling
Comparison between 1D & 2D analysis (Section 18)
99
Two Dimensional (2D) Modeling
Comparison between 1D & 2D analysis (Section 20)
100
Two Dimensional (2D) Modeling
• General Comments
Below is mentioned several reasons to explain the
difference in the values of velocity obtained by 1D
and 2D Software:
v  ︎Hec-Ras considers only velocity for each section
along the channel (so perpendicular to the cross
sections), but River2D considers two components
for velocity (in X direction and Y direction).
v  In 2D modeling, lateral stresses are also
considered while in the 1D modeling only friction
losses are considered.
v  ︎Therefore, there is only one values for velocity in
1D, however in 2D, velocity varies along the
section and usually increase in main channel and
decreases in flood plains.
101
Sediment Transport
Basic characteristic of the sediment	
The value used :
102
Sediment Transport
103
Sediment Transport
m
104
Sediment Transport
105
Sediment Transport
106
Sediment Transport
107
Sediment Transport
Results:
² Where the value of τ* is greater than τ*critical we have bed load.
² As we can see in the previous graphs in the case of the peak flow in the
most of the sections we have bed load. But we have less sections with bed
loads in the ordinary case.
108
Sediment Transport
109
Sediment Transport
110
Sediment Transport
111
Sediment Transport
Conclusion :
Ø  It is verified by the graphs that we have suspended load if
the d50 is lower than ds critical (suspended)
Ø  As demonstrated in the graphs we will have suspended
load in more sections in peak flow in comparison with
ordinary flow.
Ø  Occurring the bed load is more probable than the
suspended load.
112
Sediment Transport
Ordinary flow :	
Distance River Sta Q Total Froude # Chl
Hydr Radius
Channel
Vel channel S (f,skin) τ0 τ* Critical τ*
14329	 20	 25	 0.2	 1.12	 0.68	 0.000176428	 1.938453484	 0.045	 0.008233323	
13860	 19	 25	 1.02	 0.41	 2.07	 0.006243145	 25.1105546	 0.045	 0.106653732	
13481	 18	 25	 0.11	 1.59	 0.44	 4.62967E-05 0.722131923	 0.045	 0.003067159	
12945	 17	 25	 0.26	 1.07	 0.85	 0.000292977	 3.075295304	 0.045	 0.013061907	
12458	 16	 25	 0.23	 0.75	 0.63	 0.000258488	 1.90182657	 0.045	 0.008077755	
11385	 15	 25	 0.4	 0.84	 1.14	 0.000727688	 5.996440197	 0.045	 0.02546908	
10899	 14	 25	 0.33	 0.79	 0.93	 0.000525579	 4.073181534	 0.045	 0.017300295	
10503	 13	 25	 0.12	 1.19	 0.41	 5.91579E-05 0.690603793	 0.045	 0.002933248	
9794	 12	 25	 0.37	 1.07	 1.2	 0.000583927	 6.129308287	 0.045	 0.026033419	
9219	 11	 25	 0.19	 1.19	 0.65	 0.000148687	 1.735753138	 0.045	 0.00737238	
8795	 10	 25	 0.16	 1.3	 0.58	 0.000105222	 1.341894695	 0.045	 0.005699519	
7893	 9	 25	 0.35	 0.62	 0.86	 0.000620844	 3.776097843	 0.045	 0.016038472	
6471	 8	 25	 0.18	 1.19	 0.63	 0.000139677	 1.630580877	 0.045	 0.006925675	
5490	 7	 25	 0.21	 1.07	 0.67	 0.000182031	 1.910726729	 0.045	 0.008115557	
4895	 6.15	 25	 0.41	 0.59	 1	 0.00089682	 5.190703582	 0.045	 0.022046821	
4875	 6.05	 25	 1	 0.37	 1.93	 0.006223292	 22.58868467	 0.045	 0.095942426	
4033	 6	 25	 0.17	 1.35	 0.62	 0.000114335	 1.51419691	 0.045	 0.006431349	
3532	 5	 25	 0.17	 1.2	 0.57	 0.00011307	 1.331065812	 0.045	 0.005653525	
2297	 4	 25	 0.26	 1.38	 1.02	 0.000300517	 4.068342874	 0.045	 0.017279744	
1501	 3	 25	 0.3	 0.93	 0.93	 0.000422827	 3.857581827	 0.045	 0.016384564	
1097	 2.1	 25	 0.33	 0.75	 0.91	 0.000539315	 3.968008523	 0.045	 0.016853587	
550	 2	 25	 0.19	 1.25	 0.69	 0.000156913	 1.924147718	 0.045	 0.008172561	
0	 1	 25	 0.3	 0.69	 0.79	 0.000454252	 3.07478475	 0.045	 0.013059738
113
Sediment Transport
Peak flow :	
Distance River Sta Q Total Froude # Chl
Hydr
Radius
Channel
Vel channel S (f,skin) τ0 τ* Critical τ*
14329	 20	 561.12	 0.41	 4.53	 2.89	 0.000494507	 21.97555494	 0.045	 0.093338239	
13860	 19	 561.12	 0.5	 3.87	 3.17	 0.00073397	 27.86496075	 0.045	 0.118352704	
13481	 18	 561.12	 0.37	 4.38	 2.56	 0.000405841	 17.43808512	 0.045	 0.074065941	
12945	 17	 561.12	 0.42	 2.85	 2.23	 0.000546166	 15.26997545	 0.045	 0.064857184	
12458	 16	 561.12	 0.27	 3.82	 1.69	 0.000212258	 7.954188054	 0.045	 0.033784353	
11385	 15	 561.12	 0.35	 3.46	 2.07	 0.000363368	 12.33366716	 0.045	 0.052385606	
10899	 14	 561.12	 0.41	 4	 2.69	 0.000505746	 19.84547336	 0.045	 0.084291001	
10503	 13	 561.12	 0.22	 4.3	 1.46	 0.000135287	 5.706806219	 0.045	 0.024238898	
9794	 12	 561.12	 0.34	 3.15	 1.93	 0.000357993	 11.06253522	 0.045	 0.046986643	
9219	 11	 561.12	 0.27	 3.23	 1.57	 0.000229106	 7.259533219	 0.045	 0.030833899	
8795	 10	 561.12	 0.4	 3.56	 2.41	 0.000474179	 16.56002489	 0.045	 0.070336497	
7893	 9	 561.12	 0.2	 3.21	 1.19	 0.000132718	 4.179289715	 0.045	 0.017750976	
6471	 8	 561.12	 0.34	 3.97	 2.21	 0.000344804	 13.42861671	 0.045	 0.057036259	
5490	 7	 561.12	 0.17	 4.15	 1.12	 8.34731E-05 3.398314584	 0.045	 0.014433888	
4895	 6.15	 561.12	 0.39	 3.42	 2.32	 0.00046357	 15.55288046	 0.045	 0.066058785	
4875	 6.05	 561.12	 0.41	 3.35	 2.38	 0.000501497	 16.48096149	 0.045	 0.070000686	
4033	 6	 561.12	 0.32	 5.01	 2.36	 0.000288325	 14.17060297	 0.045	 0.060187746	
3532	 5	 561.12	 0.26	 4.7	 1.77	 0.0001766	 8.142494607	 0.045	 0.03458416	
2297	 4	 561.12	 0.4	 3.2	 2.35	 0.000519729	 16.31533384	 0.045	 0.069297205	
1501	 3	 561.12	 0.52	 3.54	 3.18	 0.000831811	 28.88661936	 0.045	 0.122692063	
1097	 2.1	 561.12	 0.3	 3.39	 1.75	 0.000266881	 8.875369257	 0.045	 0.037696947	
550	 2	 561.12	 0.25	 3.45	 1.48	 0.000186469	 6.310938751	 0.045	 0.026804871	
0	 1	 561.12	 0.39	 3.75	 2.46	 0.000460967	 16.95782013	 0.045	 0.072026079
114
Sediment Transport
In this part we calculate sediment transport rate by following equations:
115
Sediment Transport
Calculating sediment transport (using different equation )
116
Sediment Transport
117
Sediment Transport
118
Sediment Transport
Result:
u  As can be observe from the graphs the least sediment transport ratio is for
Van Rijn equation and the highest sediment transport ratio correspond to
Nielsen equation.
u  However depending on qs morphological evolution of river bed will
change river condition (manning coefficient, river geometry and so on)
u  Considering the manning formula hf=10.29 n2 . D-5.33 . Q2 . L with respect
to the sediment transport, the value of friction losses and roughness are
changed. So for designing the channels for the long period of time the
average manning coefficient is normally considered in the most cases.

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Flood Risk Analysis for River Serio, Italy by using HECRAS & River 2D

  • 1. Flood Hydraulics project for the course Flood Risk Evaluation Prof. Alessio Radice Group Members v  Seyed Mohammad Sadegh (Arshia) Mousavi (836154) v  Abdolreza Khalili (832669) v  Omid Habibzadeh Bigdarvish (836722)
  • 2. General Presentation The Serio (Lombard: Sère[1][2]) is an Italian river that flows entirely within Lombardy, crossing the provinces of Bergamo and Cremona. It is 124 kilometres (77 mi) long and flows into the Adda at Bocca di Serio south of Crema. Its valley is known as the Val Seriana.
  • 3. 3 General Presentation General information •  Length: 125 km •  Area of basin: 1250 km2 •  Average discharge: around 25 m3/s •  Water used for hydropower (famous falls are activated some times every year) and irrigation Our models examines the last 15 km of the river, from Crema to the confluence with the Adda. Data provided: •  Cross sections (map and survey data) •  Flood hydrograph •  Geometry data incorporated into a project of Hec‐Ras •  Pictures of the reach
  • 4. 4 1-D Modeling – Introduction
  • 5. 5 Objective: 1‐D modeling of river flow in ordinary and peak conditions. Steps: ²  Cross section data: choosing extent of main channel and roughness values for main channel and floodplains ²  Completing geometry data: adding the bridge at section 6.1 ²  Choosing discharge data and boundary conditions ²  Choosing levees ²  Running models: v  Steady model with ordinary flow: Sensitivity analysis (roughness and BCs) and discussion v  Steady model with peak flow: Sensitivity analysis (geometry, levees, roughness, BCs) and discussion v  Unsteady model for 200-year hydrograph: Sensitivity analysis (outflow + storage, single or multiple) and discussion 1-D Modeling - Theoretical
  • 6. 6 Theoretical Background HEC-RAS as an 1-D modeling software is based on the Saint Venant Equations. These equations are obtained based on the following assumptions, generally satisfied in hydraulic processes: o  flow is one-dimensional. o  All the quantities can be described as continuous and derivable functions of longitudinal position (s) and time (t). o  Fluid is uncompressible. o  Flow is gradually varied, and the pressure is distributed hydrostatically. o  Bed slope is small enough to consider cross sections as vertical. o  Channel is prismatic in shape. o  Flow is fully turbulent. Saint Venant Equations: 1-D Modeling - Theoretical
  • 7. 7 For special cases, these equations can be simplified as follows: §  Steady flow with no temporal variation: §  Steady flow with no spatial and temporal variability (Uniform flow): In case of steady flow, modeling is simple: a constant discharge should be assign to the entire reach, and a boundary condition for water level which would be at upstream for supercritical flows or at downstream for subcritical flows. 1-D Modeling - Theoretical
  • 8. 8 Energy Head Loss The change in the energy head between adjacent sections equals the head loss. The head loss occurring between two cross-sections is consisting of the sum of the frictional losses and expansion or contraction losses. The energy head is given by: 1-D Modeling - Theoretical
  • 9. 9 In case of unsteady flow, an initial condition is necessary together with an upstream boundary condition (usually a discharge hydrograph) and a second boundary condition which must be upstream for supercritical flows or downstream for subcritical flow. Characteristic Depths Critical Depth dc: The depth for which the specific energy is minimum is called the critical depth. When dc>d the flow is called supercritical (velocity larger than that for critical flow). When dc<d the flow is subcritical. 1-D Modeling - Theoretical
  • 10. 10 Normal Depth d0: If no quantity varies with the longitudinal direction, the flow is called uniform, and the momentum equation representing the process is S0=Sf. The depth for which this happens is called the normal depth. For a given discharge, Sf is a decreasing function of water depth, therefore: d>d0 ⇒S0 >Sf d<d0 ⇒S0 <Sf 1-D Modeling - Theoretical
  • 11. 11 Steady model for the ordinary flow Length: 125 km Average discharge: 25 m3/s S0= 0.15% 1-D Modeling Description
  • 13. 13 Main channel bank stations The left and the right bank values are inserted in the HEC-RAS software considering the width of the channel in the map and trying to find the nodes having roughly the same distance. 1-D Modeling Description
  • 14. 14 Manning Roughness Coefficient: There is no exact method for selecting n values. At the present stage of knowledge to select a value of n actually means to estimate the resistance to flow in a given channel which is really a matter of intangibles. So for this issue, different individuals will obtain different results, such as: 1.  experience; comparison with similar systems 2.  calibration over past (and known) events 3.  sensitivity analysis For the Calibration of the main channel, left and right banks of the channel we considered the USGS data for the rivers. 1-D Modeling Description
  • 15. 15 Manning Coefficient: ²  The values of roughness for main channel, left and right banks are selected based on the map of the area and provided pictures of the sections. These values are obtained from the “Verified Roughness Characteristics of Natural Channels” provided by USGS website. ²  The Manning coefficient of main channel has been selected n=0.038 whereas for the sensitivity analysis considered n=0.028 and n=0.041. ²  In addition, different manning values have been observed for the three cases with respect to the Hec-Ras software’s table. 1-D Modeling Description Serio River Clark Fork River USGS N=0.028
  • 16. 16 Manning Coefficient (n) in Flood Plains: Left and Right Coefficients bank corresponding to n=0.028 1-D Modeling Description Left%Bank 0.035 Light%Brush%&%tress%in%winter Right%Bank 0.035 Light%Brush%&%tress%in%winter Left%Bank 0.035 Light%Brush%&%tress%in%winter Right%Bank 0.025 Short%Grass Left%Bank 0.035 Light%Brush%&%tress%in%winter Right%Bank 0.025 Short%Grass Left%Bank 0.025 Short%Grass Right%Bank 0.08 Heavy%stand%of%timber,%Few%down%trees Left%Bank 0.035 Light%Brush%&%tress%in%winter Right%Bank 0.08 Heavy%stand%of%timber,%Few%down%trees Left%Bank 0.035 Light%Brush%&%tress%in%winter Right%Bank 0.035 Light%Brush%&%tress%in%winter Left%Bank 0.025 Short%Grass Right%Bank 0.025 Short%Grass Left%Bank 0.028 Right%Bank 0.028 Left%Bank 0.028 Right%Bank 0.028 Left%Bank 0.025 Short%Grass Right%Bank 0.035 Light%Brush%&%tress%in%winter Left%Bank 0.035 Light%Brush%&%tress%in%winter Right%Bank 0.025 Short%Grass Left%Bank 0.035 Light%Brush%&%tress%in%winter Right%Bank 0.035 Light%Brush%&%tress%in%winter Left%Bank 0.035 Light%Brush%&%tress%in%winter Right%Bank 0.035 Light%Brush%&%tress%in%winter 6.15 7 Bridge%Sections%(Main%Channel%value) 8 8.1 8.2 5 6 6.05 2.1 3 4 1 2 Sections Left / Right Bank Value Description Left%Bank 0.025 Short%Grass Right%Bank 0.035 Light%Brush%&%tress%in%winter Left%Bank 0.035 Light%Brush%&%tress%in%winter Right%Bank 0.035 Light%Brush%&%tress%in%winter Left%Bank 0.025 Short%Grass Right%Bank 0.035 Light%Brush%&%tress%in%winter Left%Bank 0.045 Medium%to%dense%brush Right%Bank 0.025 Short%Grass Left%Bank 0.045 Medium%to%dense%brush Right%Bank 0.035 Light%Brush%&%tress%in%winter Left%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts Right%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts Left%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts Right%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts Left%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts Right%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts Left%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts Right%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts Left%Bank 0.035 Light%Brush%&%tress%in%winter Right%Bank 0.035 Light%Brush%&%tress%in%winter Left%Bank 0.045 Medium%to%dense%brush Right%Bank 0.035 Light%Brush%&%tress%in%winter Left%Bank 0.035 Light%Brush%&%tress%in%winter Right%Bank 0.035 Light%Brush%&%tress%in%winter Left%Bank 0.035 Light%Brush%&%tress%in%winter Right%Bank 0.035 Light%Brush%&%tress%in%winter Left%Bank 0.035 Light%Brush%&%tress%in%winter Right%Bank 0.035 Light%Brush%&%tress%in%winter 15.1 20 16 17 18 19 13 14 15 11 12 12.1 Value Description 9 10 Sections Left / Right Bank
  • 17. 17 Manning Coefficient (n) in Flood Plains: Left and Right Coefficients bank corresponding to n=0.038 1-D Modeling Description Left%Bank 0.05 Light%Brush%&%tress%in%winter Right%Bank 0.05 Light%Brush%&%tress%in%winter Left%Bank 0.05 Light%Brush%&%tress%in%winter Right%Bank 0.03 Short%Grass Left%Bank 0.05 Light%Brush%&%tress%in%winter Right%Bank 0.03 Short%Grass Left%Bank 0.03 Short%Grass Right%Bank 0.1 Heavy%stand%of%timber,%Few%down%trees Left%Bank 0.05 Light%Brush%&%tress%in%winter Right%Bank 0.1 Heavy%stand%of%timber,%Few%down%trees Left%Bank 0.05 Light%Brush%&%tress%in%winter Right%Bank 0.05 Light%Brush%&%tress%in%winter Left%Bank 0.03 Short%Grass Right%Bank 0.03 Short%Grass Left%Bank 0.038 Right%Bank 0.038 Left%Bank 0.038 Right%Bank 0.038 Left%Bank 0.03 Short%Grass Right%Bank 0.05 Light%Brush%&%tress%in%winter Left%Bank 0.05 Light%Brush%&%tress%in%winter Right%Bank 0.03 Short%Grass Left%Bank 0.05 Light%Brush%&%tress%in%winter Right%Bank 0.05 Light%Brush%&%tress%in%winter Left%Bank 0.05 Light%Brush%&%tress%in%winter Right%Bank 0.05 Light%Brush%&%tress%in%winter Bridge%Sections%(Main%Channel%value) Sections Left / Right Bank Value Description 1 2 2.1 3 4 5 8.2 8.1 6 6.05 6.15 7 8 Left%Bank 0.03 Short%Grass Right%Bank 0.05 Light%Brush%&%tress%in%winter Left%Bank 0.05 Light%Brush%&%tress%in%winter Right%Bank 0.03 Light%Brush%&%tress%in%winter Left%Bank 0.05 Short%Grass Right%Bank 0.03 Light%Brush%&%tress%in%winter Left%Bank 0.03 Medium%to%dense%brush Right%Bank 0.1 Short%Grass Left%Bank 0.05 Medium%to%dense%brush Right%Bank 0.1 Light%Brush%&%tress%in%winter Left%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts Right%Bank 0.05 Cleared%land%with%tree%stumps%but%heavy%sprouts Left%Bank 0.03 Cleared%land%with%tree%stumps%but%heavy%sprouts Right%Bank 0.03 Cleared%land%with%tree%stumps%but%heavy%sprouts Left%Bank 0.038 Cleared%land%with%tree%stumps%but%heavy%sprouts Right%Bank 0.038 Cleared%land%with%tree%stumps%but%heavy%sprouts Left%Bank 0.038 Cleared%land%with%tree%stumps%but%heavy%sprouts Right%Bank 0.038 Cleared%land%with%tree%stumps%but%heavy%sprouts Left%Bank 0.038 Light%Brush%&%tress%in%winter Right%Bank 0.038 Light%Brush%&%tress%in%winter Left%Bank 0.03 Medium%to%dense%brush Right%Bank 0.05 Light%Brush%&%tress%in%winter Left%Bank 0.05 Light%Brush%&%tress%in%winter Right%Bank 0.03 Light%Brush%&%tress%in%winter Left%Bank 0.05 Light%Brush%&%tress%in%winter Right%Bank 0.05 Light%Brush%&%tress%in%winter Left%Bank 0.05 Light%Brush%&%tress%in%winter Right%Bank 0.05 Light%Brush%&%tress%in%winter 14 15 15.1 16 Left / Right Bank Value Description 9 10 13 Sections 11 12 12.1 17 18 19 20
  • 18. 18 Manning Coefficient (n) in Flood Plains: Left and Right Coefficients bank corresponding to n=0.041 1-D Modeling Description Left%Bank 0.06 Light%Brush%&%tress%in%winter Right%Bank 0.06 Light%Brush%&%tress%in%winter Left%Bank 0.06 Light%Brush%&%tress%in%winter Right%Bank 0.035 Short%Grass Left%Bank 0.06 Light%Brush%&%tress%in%winter Right%Bank 0.035 Short%Grass Left%Bank 0.035 Short%Grass Right%Bank 0.12 Heavy%stand%of%timber,%Few%down%trees Left%Bank 0.06 Light%Brush%&%tress%in%winter Right%Bank 0.12 Heavy%stand%of%timber,%Few%down%trees Left%Bank 0.06 Light%Brush%&%tress%in%winter Right%Bank 0.06 Light%Brush%&%tress%in%winter Left%Bank 0.035 Short%Grass Right%Bank 0.035 Short%Grass Left%Bank 0.041 Right%Bank 0.041 Left%Bank 0.041 Right%Bank 0.041 Left%Bank 0.035 Short%Grass Right%Bank 0.06 Light%Brush%&%tress%in%winter Left%Bank 0.06 Light%Brush%&%tress%in%winter Right%Bank 0.035 Short%Grass Left%Bank 0.06 Light%Brush%&%tress%in%winter Right%Bank 0.06 Light%Brush%&%tress%in%winter Left%Bank 0.035 Light%Brush%&%tress%in%winter Right%Bank 0.06 Light%Brush%&%tress%in%winter 6.15 7 Bridge%Sections%(Main%Channel%value) 8 8.1 8.2 5 6 6.05 2.1 3 4 1 2 Sections Left / Right Bank Value Description Left%Bank 0.035 Short%Grass Right%Bank 0.06 Light%Brush%&%tress%in%winter Left%Bank 0.06 Light%Brush%&%tress%in%winter Right%Bank 0.06 Light%Brush%&%tress%in%winter Left%Bank 0.035 Short%Grass Right%Bank 0.06 Light%Brush%&%tress%in%winter Left%Bank 0.11 Medium%to%dense%brush Right%Bank 0.035 Short%Grass Left%Bank 0.11 Medium%to%dense%brush Right%Bank 0.06 Light%Brush%&%tress%in%winter Left%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts Right%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts Left%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts Right%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts Left%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts Right%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts Left%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts Right%Bank 0.08 Cleared%land%with%tree%stumps%but%heavy%sprouts Left%Bank 0.06 Light%Brush%&%tress%in%winter Right%Bank 0.06 Light%Brush%&%tress%in%winter Left%Bank 0.11 Medium%to%dense%brush Right%Bank 0.06 Light%Brush%&%tress%in%winter Left%Bank 0.06 Light%Brush%&%tress%in%winter Right%Bank 0.06 Light%Brush%&%tress%in%winter Left%Bank 0.06 Light%Brush%&%tress%in%winter Right%Bank 0.06 Light%Brush%&%tress%in%winter Left%Bank 0.06 Light%Brush%&%tress%in%winter Right%Bank 0.06 Light%Brush%&%tress%in%winter 15.1 20 16 17 18 19 13 14 15 11 12 12.1 Value Description 9 10 Sections Left / Right Bank
  • 19. 19 1-D Modeling Description Serio River Manning Coefficient (n) in Flood Plains: Left and Right Coefficients bank corresponding to n=0.028
  • 20. 20 1-D Modeling Description Manning Coefficient (n) in Flood Plains: Left and Right Coefficients bank corresponding to n=0.038 Serio RiverMoyie River
  • 21. 21 1-D Modeling Description Manning Coefficient (n) in Flood Plains: Left and Right Coefficients bank corresponding to n=0.041 Middle Fork River Serio River
  • 23. 23 Bridge: v  At the section 6.1, a bridge is added to the channel. v  We accomplished this by adding one section to the upstream, one section to downstream and one section at the location of the structure. v  The total width of the bridge is 10m. v  The distance between these three sections (6.05-6.1-6.15) is10m from the middle section of the bridge. 1-D Modeling Steady – Ordinary Flow
  • 24. 24 1-D Modeling Steady – Ordinary Flow Bridge Create a section before (6.15) Create a section after (6.05) Delete section 6.1 Insert the bridge (6.1)
  • 26. 26 Limitations Considerations of 1D Modeling v  Since HEC-RAS is a 1D modeling software, it cannot consider whether water can move across the main channel to the flood plains or not. Therefore, if the bed elevation at floodplain is lower than water surface, HEC-RAS will consider water flows into the flood plains. And in this case levee should be added to the section. For this issue, we have considered both view 3D multiple cross section plot and view cross sections. v  In ordinary flow (Q=25 m^3/sec), there are two necessity to add levees in Sections 2 and 8_1, after adding these levees water does not exist in the flood plains. v  The presence of levees is specially required for the steady peak flow and the unsteady simulation based on 200 years hydrograph. 1-D Modeling Description
  • 27. 27 1-D Modeling Description Adding Levee in Section 2 3D View Cross Section View
  • 28. 28 Levee Cross Section View 3D View 1-D Modeling Description Section 2 (After adding Levee)
  • 29. 29 1-D Modeling Description Adding Levee in Section 8.1 As can be seen, in the section 8.1, a levee is added to the right of the main channel. Since HEC-RAS is a 1-D modeling software, it cannot consider whether water can move across the main channel to the banks or not. Thus, if the water surface is higher than the bed elevation at the floodplain water, HEC-RAS will consider water flows into the banks. To avoid this issue, in the section 8.1 in our model, a levee has to be added.
  • 30. 30 1-D Modeling Description Section 8.1 (After adding Levee) Section 8.1 (Before adding Levee)
  • 31. 31 1-D Modeling Description – Ordinary Flow Overall 3D View after adding levee (All Sections )
  • 32. 32 Boundary Conditions Ø  The discharge for the ordinary flow is 25 m3/s. Ø  The boundary conditions for the river depend on the nature of the flow. In the case of subcritical flow, we have to input just downstream condition and for supercritical flows, just upstream condition is needed. Ø  By running the model with some assumed boundary conditions (critical flow at upstream and normal flow at downstream), it was noted that the Froude Number along the channel is lower than 1. Therefore, the flow is subcritical and just downstream boundary condition has to be set. To do so, a sensitivity analysis of the boundary condition need to be done. Ø  For the Reference scenario we have chosen the normal depth for the downstream and Critical depth for the upstream. 1-D Modeling Description
  • 34. 34 Ordinary Flow 3D View (without Flood)
  • 36. 36 Ordinary Flow Bridge Section (Sec. 6.1) The contraction in the bridge section causes the flow depth to change. Since the flow is subcritical, water elevation decreases after the bridge and gets close to the critical depth.
  • 37. 37 Ordinary Flow Sensitivity Analysis for Boundary Condition To check the sensitivity of the results with respect to the boundary conditions, 5 sets of boundary conditions are considered and their results are compared: 1. Upstream Normal flow and Downstream Normal flow (S=0.0015) 2. Upstream Normal flow and Downstream Critical flow 3. Upstream Critical flow and Downstream Normal flow (S=0.0015) (Reference Scenario) 4. Upstream Critical flow and Downstream Critical flow 5. Upstream Normal flow and Downstream fixed Water Surface Elevation: 47.51 (45.71 Bed Elevation + 1.8 m Water Depth)
  • 38. 38 1-D Modeling Description Water Surface for different boundary conditions
  • 39. 39 Ordinary Flow Results: Velocity Conditions Noticeable rise in water velocity in cases 2 and 4 (water level tends to critical depth) Velocity for different boundary conditions
  • 40. 40 Ordinary Flow Sensitivity Analysis for Boundary Condition Results 1.  In whole profile (except bridge section) different boundary condition in upstream makes no change in water profile. Because water level is over critical depth in whole reach (subcritical flow) and just in case of a supercritical flow upstream boundary condition affect our water profile. 2.  At this project (subcritical flow) the downstream boundary condition affect the water profile. Water level variation is occurred in the last 4 stations (downstream).
  • 41. 41 Ordinary Flow Roughness Sensitivity Analysis In applying the Manning number the greatest difficulty lies in the determination of the roughness coefficient n; there is no exact method of selecting the n value. In the present study, comparison with similar system of the other rivers has been carried out based on the database: “Verified Roughness Characteristics of Natural Channels” provided by USGS website. ︎In ordinary flow water exists only in main channel therefore the simulation is only dependent on the manning coefficient of main channel and not left and right banks. Therefore for flood plains same manning coefficient has been chosen. ︎To study the roughness sensitivity, the manning coefficients are once increased from n=0.038 (reference coefficient) to n=0.041 and once decreased from n=0.038 to 0.028 The roughness sensitivity is evaluated regarding two aspects: In this analysis two aspects have been considered: v  Water Surface elevation v  Velocity
  • 42. 42 Ordinary Flow Roughness Sensitivity Analysis v Water Surface elevation v  Velocity Considering the graph provided, it is easy to observe that by increasing the manning coefficient (n), the water surface elevation is raised. However, generally speaking different manning coefficient values (n), have provided almost the same water surface elevation compared to the dimension of our channel. This hypothesis will be examined later in this project. An important point of this graph, is the behavior seen at the location of the bridge. It is clear that regardless of the magnitude of the manning coefficient, the water surface elevation approach to the same level for all conditions. This may indicate that in this specific location, due to the contraction caused by the bridge piers, a critical condition has occurred. Checking the Fr=1 in this location verifies this speculation. The results obtained from the HEC-RAS model verifies that the flow is subcritical before and after this location while, when the flow reaches the bridge, the flow is critical.
  • 43. 43 Ordinary Flow Profile Output Table for reference scenario
  • 44. 44 Ordinary Flow Sensitivity Analysis for Boundary Condition Results: Water Surface Noticeable rise in water velocity in cases 2 and 4 (water level tends to critical depth)
  • 45. 45 Ordinary Flow Roughness Sensitivity Analysis v  Water Surface elevation v Velocity Two points can we concluded from the velocity graph. 1.  The graph with higher Manning’s value causes lower velocity as expected. 2.  The increase in roughness results in the rise of the water surface elevation. The higher water surface elevation yield lower velocity of the flow.
  • 47. 47 Peak Flow v  Average discharge 561.12 m3/s (based on peak value of 200 –year hydrograph) Levees ²  13 sections need adding levees to control flood plain. ²  Criteria for deciding whether to add levee or not: 1.  Considering the residential areas and facilities close to the flood plain. 2.  If the bed elevation is lower than water surface HEC-RAS will consider this area as a flooded area, so levees are required to avoid this issue. Peak Flow Properties
  • 48. 48 Peak Flow Adding Levee Section 20 Before Levee After Levee
  • 49. 49 Peak Flow Adding Levee Section 18 Before Levee After Levee
  • 50. 50 Peak Flow Adding Levee Section 17 Before Levee After Levee
  • 51. 51 Peak Flow Adding Levee Section 16 Before Levee After Levee
  • 52. 52 Peak Flow Adding Levee Section 14 Before Levee After Levee
  • 53. 53 Peak Flow Adding Levee Section 13 Before Levee After Levee
  • 54. 54 Peak Flow Adding Levee Section 12 Before Levee After Levee
  • 55. 55 Peak Flow Adding Levee Section 11 Before Levee After Levee
  • 56. 56 Peak Flow Adding Levee Section 5 Before Levee After Levee
  • 57. 57 Peak Flow Adding Levee Section 4 Before Levee After Levee
  • 58. 58 Peak Flow Adding Levee Section 3 Before Levee After Levee
  • 59. 59 Peak Flow Adding Levee Section 2 Before Levee After Levee
  • 60. 60 Peak Flow Adding Levee Section 1 Before Levee After Levee
  • 61. 61 Peak Flow 3D View (With Flood & After adding levee)
  • 62. 62 Peak Flow Sensitivity analysis in case of adding levee and omitting cross sections
  • 63. 63 Peak Flow Sensitivity analysis in case of adding levee and eliminating cross sections Section Elevation Difference 16 0.3 13 0.4 9 0.2 Differences in water elevation Comparing the graphs and the results of the two sets of data: 1.  No elimination of cross sections and No levees. 2.  With levees and eliminating some cross sections. We can observe that in the upstream sections (16, 13, 9) of the eliminated cross sections (15.1, 12.1, 8.2, 8.1) the elevation of the water is increased after adding the levees and eliminating the mentioned cross sections by the values provided in the above table. m m m
  • 64. 64 Peak Flow Sensitivity analysis in case of adding levee and eliminating cross sections Comparing the graphs and the results of the two sets of data: 1.  No levees and No elimination in cross sections. 2.  With levees, No eliminating cross sections. We can observe that the graph belonging to the case of no levee and no elimination is always lower or equal to the one related to the case of having levees but no elimination in cross sections. Comparing the graphs and the results of the two sets of data: 1.  No levees and with elimination of cross sections. 2.  With levees, No eliminating cross sections. One could notice that by eliminating the cross sections (case 1) the water surface level would decrease.
  • 65. 65 Peak Flow Sensitivity Analysis for Boundary Condition To check the sensitivity of the results with respect to the boundary conditions, 5 sets of boundary conditions are considered and their results are compared: 1. Upstream Normal flow and Downstream Normal flow (S=0.0015) 2. Upstream Normal flow and Downstream Critical flow 3. Upstream Critical flow and Downstream Normal flow (S=0.0015) (Reference Scenario) 4. Upstream Critical flow and Downstream Critical flow 5. Upstream Normal flow and Downstream fixed Water Surface Elevation: 51.71 (45.71 Bed Elevation + 6 m Water Depth)
  • 68. 68 Peak Flow Sensitivity Analysis for Boundary Condition Results One could observe that different boundary condition would result in the same velocity except in the case of sections in the downstream of the river in which the difference is due to the different boundary conditions applied there.
  • 69. 69 Peak Flow Roughness Sensitivity Analysis In applying the Manning number the greatest difficulty lies in the determination of the roughness coefficient n; there is no exact method of selecting the n value. In the present study, comparison with similar system of the other rivers has been carried out based on the database: “Verified Roughness Characteristics of Natural Channels” provided by USGS website. ︎In the peak flow water is not only flowing in the main channel as it was in the case of ordinary flow explained earlier. Left and right bank also contain a portion of water flow so different manning coefficient in the banks is also applied. ︎ The roughness sensitivity is evaluated regarding two aspects: In this analysis two aspects have been considered: v  Water Surface elevation v  Velocity
  • 70. 70 Peak Flow Roughness Sensitivity Analysis v Water Surface elevation v  Velocity For this type of flow, the result obtained in the case of ordinary flow are true. Moreover, it is clear that regardless of the magnitude of the manning coefficient, the water surface elevation approach to the same level for all conditions for the bridge section. Moreover it is observed that the water surface along the channel is always above the critical depth. Meaning that there is subcritical flow in the whole channel.
  • 71. 71 Peak Flow Roughness Sensitivity Analysis v Water Surface elevation
  • 72. 72 Peak Flow Roughness Sensitivity Analysis v  Water Surface elevation v Velocity Two points can we concluded from the velocity graph. 1.  The graph with higher Manning’s value causes lower velocity as expected. 2.  The increase in roughness results in the rise of the water surface elevation. The higher water surface elevation yield lower velocity of the flow.
  • 73. 73 Peak Flow Roughness Sensitivity Analysis v  Water Surface elevation v Velocity
  • 74. 74 Peak Flow Roughness Sensitivity Analysis Results: q  ︎︎While the difference in the water surface elevation and velocity of both peak and ordinary flow in the case of different (n) values is relatively small, we could observe that the difference in the case of peak flow is larger. In the other words, peak flow results are more sensitive to manning coefficient. q  To conclude, one could state that to use the manning coefficient considering the similar river sections of the USGS and predict the case of river Serio, is acceptable.
  • 75. 75 Unsteady Model Unsteady model for 200-year Hydrograph To model for the unsteady flow, all the parameters from steady models are used. In this case different flow rates is considered for different sections of the river based on the excel sheet provided. §  Model conditions §  Boundary condition Upstream: 200-year hydrograph Downstream: normal depth with slope of 0.0015 §  Initial condition Initial discharge
  • 76. 76 Unsteady Model Unsteady flow data The original dataset is interpolated with 60 minute time interval. This time interval is small enough with respect to the whole event history ( 200 years).
  • 77. 77 Longitudinal Profile of the corrected geometry Unsteady Flow
  • 78. 78 Unsteady flow 3D View (Flooded Areas):
  • 79. 79 Unsteady Model 40 42 44 46 48 50 52 54 56 58 60 62 64 66 68 0 2000 4000 6000 8000 10000 12000 14000 16000 Steady Vs. Unsteady flow bed steady flow unsteady flow Comparison: Steady and Unsteady elevation analysis (at max. water profile)
  • 80. 80 Comparison: Steady and unsteady discharge analysis (at max. water profile) Unsteady Model 525 530 535 540 545 550 555 560 565 0 2000 4000 6000 8000 10000 12000 14000 16000 Steady Vs. Unsteady unsteady steady
  • 81. 81 0 0.5 1 1.5 2 2.5 3 3.5 0 2000 4000 6000 8000 10000 12000 14000 16000 steady Vs. Unsteady unsteady steady Comparison: Steady and unsteady velocity analysis (at max. water profile) Unsteady Model
  • 82. 82 Unsteady Model Results: v  It can be observed that the maximum difference between the steady and unsteady flow discharge values is 5.87 percent. This amount shows the loss of Q by considering unsteady type of flow. v  The values of discharge, velocity and water surface elevation are relatively similar in the case of analyzing Serio river. This could be explained by the fact that the difference between steady and unsteady values is dominant only if the channel profile is long enough.
  • 83. 83 Two Dimensional (2D) Modeling Theoretical Background
  • 84. 84 Two Dimensional (2D) Modeling Theoretical Background
  • 85. 85 Two Dimensional (2D) Modeling Theoretical Background The 2D model depth averaged, mass and momentum conservation equations are: The bed shear stress are computed by: The turbulent normal and shear stresses are computed according to the Boussinesq’s assumption as:
  • 86. 86 Two Dimensional (2D) Modeling Benefits Ø  ︎Ability to model more complex flows including floodplain and underground flows Ø  ︎Ability to consider impact of obstructions. Ø  ︎ No need to force the geometry to be appropriate for modeling Limitations v  If the phenomenon is abrupt, the 1D model contains discontinuities that water would hardly follow. v  ︎Results are limited by the accuracy of the assumptions, input data and the computing power of the computer program. v  Modeling complexity and precision are not a substitute for sound engineering judgment
  • 87. 87 Two Dimensional (2D) Modeling Comparing the results of 2-D with 1D Since River 2D results 2 values for velocity along the X and Y axes, and computes the water depth at each node, it is not possible to have single longitudinal profiles for velocity and water surface for the river. Therefore, the results are compared section by section
  • 89. 89 Two Dimensional (2D) Modeling Comparison between 1D & 2D analysis (Section 9)
  • 90. 90 Two Dimensional (2D) Modeling Comparison between 1D & 2D analysis (Section 10)
  • 91. 91 Two Dimensional (2D) Modeling Comparison between 1D & 2D analysis (Section 11)
  • 92. 92 Two Dimensional (2D) Modeling Comparison between 1D & 2D analysis (Section 12)
  • 93. 93 Two Dimensional (2D) Modeling Comparison between 1D & 2D analysis (Section 13)
  • 94. 94 Two Dimensional (2D) Modeling Comparison between 1D & 2D analysis (Section 14)
  • 95. 95 Two Dimensional (2D) Modeling Comparison between 1D & 2D analysis (Section 15)
  • 96. 96 Two Dimensional (2D) Modeling Comparison between 1D & 2D analysis (Section 16)
  • 97. 97 Two Dimensional (2D) Modeling Comparison between 1D & 2D analysis (Section 17)
  • 98. 98 Two Dimensional (2D) Modeling Comparison between 1D & 2D analysis (Section 18)
  • 99. 99 Two Dimensional (2D) Modeling Comparison between 1D & 2D analysis (Section 20)
  • 100. 100 Two Dimensional (2D) Modeling • General Comments Below is mentioned several reasons to explain the difference in the values of velocity obtained by 1D and 2D Software: v  ︎Hec-Ras considers only velocity for each section along the channel (so perpendicular to the cross sections), but River2D considers two components for velocity (in X direction and Y direction). v  In 2D modeling, lateral stresses are also considered while in the 1D modeling only friction losses are considered. v  ︎Therefore, there is only one values for velocity in 1D, however in 2D, velocity varies along the section and usually increase in main channel and decreases in flood plains.
  • 101. 101 Sediment Transport Basic characteristic of the sediment The value used :
  • 107. 107 Sediment Transport Results: ² Where the value of τ* is greater than τ*critical we have bed load. ² As we can see in the previous graphs in the case of the peak flow in the most of the sections we have bed load. But we have less sections with bed loads in the ordinary case.
  • 111. 111 Sediment Transport Conclusion : Ø  It is verified by the graphs that we have suspended load if the d50 is lower than ds critical (suspended) Ø  As demonstrated in the graphs we will have suspended load in more sections in peak flow in comparison with ordinary flow. Ø  Occurring the bed load is more probable than the suspended load.
  • 112. 112 Sediment Transport Ordinary flow : Distance River Sta Q Total Froude # Chl Hydr Radius Channel Vel channel S (f,skin) τ0 τ* Critical τ* 14329 20 25 0.2 1.12 0.68 0.000176428 1.938453484 0.045 0.008233323 13860 19 25 1.02 0.41 2.07 0.006243145 25.1105546 0.045 0.106653732 13481 18 25 0.11 1.59 0.44 4.62967E-05 0.722131923 0.045 0.003067159 12945 17 25 0.26 1.07 0.85 0.000292977 3.075295304 0.045 0.013061907 12458 16 25 0.23 0.75 0.63 0.000258488 1.90182657 0.045 0.008077755 11385 15 25 0.4 0.84 1.14 0.000727688 5.996440197 0.045 0.02546908 10899 14 25 0.33 0.79 0.93 0.000525579 4.073181534 0.045 0.017300295 10503 13 25 0.12 1.19 0.41 5.91579E-05 0.690603793 0.045 0.002933248 9794 12 25 0.37 1.07 1.2 0.000583927 6.129308287 0.045 0.026033419 9219 11 25 0.19 1.19 0.65 0.000148687 1.735753138 0.045 0.00737238 8795 10 25 0.16 1.3 0.58 0.000105222 1.341894695 0.045 0.005699519 7893 9 25 0.35 0.62 0.86 0.000620844 3.776097843 0.045 0.016038472 6471 8 25 0.18 1.19 0.63 0.000139677 1.630580877 0.045 0.006925675 5490 7 25 0.21 1.07 0.67 0.000182031 1.910726729 0.045 0.008115557 4895 6.15 25 0.41 0.59 1 0.00089682 5.190703582 0.045 0.022046821 4875 6.05 25 1 0.37 1.93 0.006223292 22.58868467 0.045 0.095942426 4033 6 25 0.17 1.35 0.62 0.000114335 1.51419691 0.045 0.006431349 3532 5 25 0.17 1.2 0.57 0.00011307 1.331065812 0.045 0.005653525 2297 4 25 0.26 1.38 1.02 0.000300517 4.068342874 0.045 0.017279744 1501 3 25 0.3 0.93 0.93 0.000422827 3.857581827 0.045 0.016384564 1097 2.1 25 0.33 0.75 0.91 0.000539315 3.968008523 0.045 0.016853587 550 2 25 0.19 1.25 0.69 0.000156913 1.924147718 0.045 0.008172561 0 1 25 0.3 0.69 0.79 0.000454252 3.07478475 0.045 0.013059738
  • 113. 113 Sediment Transport Peak flow : Distance River Sta Q Total Froude # Chl Hydr Radius Channel Vel channel S (f,skin) τ0 τ* Critical τ* 14329 20 561.12 0.41 4.53 2.89 0.000494507 21.97555494 0.045 0.093338239 13860 19 561.12 0.5 3.87 3.17 0.00073397 27.86496075 0.045 0.118352704 13481 18 561.12 0.37 4.38 2.56 0.000405841 17.43808512 0.045 0.074065941 12945 17 561.12 0.42 2.85 2.23 0.000546166 15.26997545 0.045 0.064857184 12458 16 561.12 0.27 3.82 1.69 0.000212258 7.954188054 0.045 0.033784353 11385 15 561.12 0.35 3.46 2.07 0.000363368 12.33366716 0.045 0.052385606 10899 14 561.12 0.41 4 2.69 0.000505746 19.84547336 0.045 0.084291001 10503 13 561.12 0.22 4.3 1.46 0.000135287 5.706806219 0.045 0.024238898 9794 12 561.12 0.34 3.15 1.93 0.000357993 11.06253522 0.045 0.046986643 9219 11 561.12 0.27 3.23 1.57 0.000229106 7.259533219 0.045 0.030833899 8795 10 561.12 0.4 3.56 2.41 0.000474179 16.56002489 0.045 0.070336497 7893 9 561.12 0.2 3.21 1.19 0.000132718 4.179289715 0.045 0.017750976 6471 8 561.12 0.34 3.97 2.21 0.000344804 13.42861671 0.045 0.057036259 5490 7 561.12 0.17 4.15 1.12 8.34731E-05 3.398314584 0.045 0.014433888 4895 6.15 561.12 0.39 3.42 2.32 0.00046357 15.55288046 0.045 0.066058785 4875 6.05 561.12 0.41 3.35 2.38 0.000501497 16.48096149 0.045 0.070000686 4033 6 561.12 0.32 5.01 2.36 0.000288325 14.17060297 0.045 0.060187746 3532 5 561.12 0.26 4.7 1.77 0.0001766 8.142494607 0.045 0.03458416 2297 4 561.12 0.4 3.2 2.35 0.000519729 16.31533384 0.045 0.069297205 1501 3 561.12 0.52 3.54 3.18 0.000831811 28.88661936 0.045 0.122692063 1097 2.1 561.12 0.3 3.39 1.75 0.000266881 8.875369257 0.045 0.037696947 550 2 561.12 0.25 3.45 1.48 0.000186469 6.310938751 0.045 0.026804871 0 1 561.12 0.39 3.75 2.46 0.000460967 16.95782013 0.045 0.072026079
  • 114. 114 Sediment Transport In this part we calculate sediment transport rate by following equations:
  • 115. 115 Sediment Transport Calculating sediment transport (using different equation )
  • 118. 118 Sediment Transport Result: u  As can be observe from the graphs the least sediment transport ratio is for Van Rijn equation and the highest sediment transport ratio correspond to Nielsen equation. u  However depending on qs morphological evolution of river bed will change river condition (manning coefficient, river geometry and so on) u  Considering the manning formula hf=10.29 n2 . D-5.33 . Q2 . L with respect to the sediment transport, the value of friction losses and roughness are changed. So for designing the channels for the long period of time the average manning coefficient is normally considered in the most cases.