Assessment of the Automation Algorithm for TDR Bridge - Ohio ...
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ODOT Project Review Session Presentation<br />
— Development <strong>of</strong> <strong>TDR</strong> Real Time <strong>Bridge</strong><br />
Scour Monitoring System<br />
April 17, 2009<br />
Xiong (Bill) Yu 1 , Ph.D., P.E. and Xinbao Yu 2<br />
1 Assistant Pr<strong>of</strong>essor, Department <strong>of</strong> Civil Engineering, Case<br />
Western Reserve University, xxy21@case.edu, 216-368-6247<br />
2 Graduate Research Assistant, Currently, research engineer,<br />
Louisiana DOT/Louisiana Transportation Research Center
Outline<br />
• Introduction<br />
• Literature review: scour monitoring<br />
practice and technologies<br />
• Validation <strong>of</strong> Time Domain Reflectometry<br />
<strong>for</strong> scour monitoring<br />
• <strong>TDR</strong> scour measurements in various<br />
environments<br />
• Development <strong>of</strong> a field <strong>TDR</strong> scour sensor<br />
• Summary and conclusions, and future<br />
work<br />
2
Introduction<br />
1.1 Motivation <strong>for</strong> <strong>Bridge</strong> Scour Monitoring<br />
• 1987, <strong>the</strong> Schoharie Creek <strong>Bridge</strong> on <strong>the</strong> New York State Thruway<br />
• 1989, <strong>the</strong> US 51 bridge over <strong>the</strong> Hatchie River in Tennessee<br />
• 1995, <strong>the</strong> I-5 bridges over Arroyo Pasajero in Cali<strong>for</strong>nia<br />
National <strong>Bridge</strong><br />
Inspection<br />
Standards (NBIS)<br />
Minimum 2 year<br />
inspection<br />
frequency<br />
3
1.2 Fundamentals <strong>of</strong> <strong>Bridge</strong> Scour<br />
• Definition<br />
• A dynamic process<br />
Pier scour depth in a sand-bed stream as a function <strong>of</strong> time (Richardson 1995)<br />
4
Classification<br />
• General Scour<br />
• Aggradation and Degradation<br />
• Contraction Scour<br />
• Local Scour<br />
Different Types <strong>of</strong> Scour in a Typical <strong>Bridge</strong> Cross Section (Wang 2004).<br />
5
Contraction scour<br />
Two manmade features that create a contracted<br />
section in a channel (Sheppard and Renna 2005)<br />
An example <strong>of</strong> manmade causeway islands that create a<br />
channel contraction (Sheppard and Renna 2005)<br />
6
Local Scour<br />
• Pier scour and abutment scour<br />
Scour design references<br />
Complex flows around a bridge pier (Hamill 1999)<br />
HEC-18, Evaluating Scour at <strong>Bridge</strong>s<br />
HEC-20, Stream Stability at Highway <strong>Bridge</strong>s<br />
HEC-23, <strong>Bridge</strong> Scour and Stream Instability<br />
Countermeasures-Experience, Selection, and Design Guidance<br />
7
1.3 <strong>Bridge</strong> Scour Study<br />
• Analytical Methods<br />
Vortex, scour depth, assumption <strong>of</strong> <strong>the</strong> scour shape, determination <strong>of</strong><br />
critical shear stress or critical velocity, and continuity equation<br />
• Physical Modeling<br />
• Numerical Simulation<br />
Photo <strong>of</strong> a pier scour flume test<br />
8
Physical Modeling<br />
Parameters related to fluid properties<br />
• g: acceleration due to gravity<br />
• ρ: density <strong>of</strong> <strong>the</strong> fluid<br />
• υ: kinematic viscosity <strong>of</strong> fluid<br />
Parameters related to flow properties<br />
• y1 : approach flow depth<br />
d<br />
• V1: approach mean flow velocity<br />
s<br />
Parameters related to sediment properties b<br />
• ρ: density <strong>of</strong> <strong>the</strong> sediment<br />
• d50 : median sediment size<br />
• σg: geometric standard deviation <strong>of</strong> sediment size<br />
distribution<br />
• cohesion <strong>of</strong> sediment<br />
Parameters related to <strong>the</strong> bridge pier<br />
• shape <strong>of</strong> <strong>the</strong> bridge pier<br />
• width <strong>of</strong> <strong>the</strong> bridge pier<br />
• alignment <strong>of</strong> <strong>the</strong> bridge pier<br />
Breusers et al. 1997<br />
⎛<br />
⎞<br />
⎜<br />
y1<br />
V1<br />
ρV1b<br />
V1<br />
b<br />
= f K<br />
⎟<br />
s,<br />
Kθ<br />
, , , , , , σ g<br />
⎜<br />
⎟<br />
⎝<br />
b gy µ Vc<br />
d<br />
1<br />
50 ⎠<br />
9
Numerical Simulation<br />
• 1D simulation such as HEC-RAS and WSPRO<br />
• 2D simulation such as Flo2dh and SED2D<br />
• 3D simulation such as Flow3D, FLUENT, and CCHE3D<br />
Screen shot <strong>of</strong> bridge<br />
scour analysis in HEC-<br />
RAS<br />
Example <strong>of</strong> flow field by<br />
Flo2dh (Yu and Yu 2008)<br />
10
Numerical Simulation<br />
• 1D simulation such as HEC-RAS and WSPRO<br />
• 2D simulation such as Flo2dh and SED2D<br />
• 3D simulation such as Flow3D, FLUENT, and CCHE3D<br />
Simulated local scour hole around<br />
a bridge pier (NCCHE n.d.)<br />
Simulated complex turbulent flow around<br />
bridge piers (Ge 2004)<br />
11
Numerical Simulation<br />
• 3D simulation such as Flow3D, FLUENT, and CCHE3D<br />
turbulent flow<br />
two-phase flow: air, water, sediment<br />
fluid sediment interaction<br />
According to <strong>the</strong> previous research, it<br />
is found that <strong>the</strong> bottleneck <strong>of</strong> <strong>the</strong><br />
state-<strong>of</strong>-<strong>the</strong>-art <strong>of</strong> <strong>the</strong> local scour<br />
simulation lies in <strong>the</strong> accurate<br />
modeling <strong>of</strong> <strong>the</strong> sediment behavior and<br />
<strong>the</strong> interaction between <strong>the</strong> flow and<br />
bed variation.<br />
12
Field observation<br />
• A co-operative National <strong>Bridge</strong> Scour Project in 1987 to collect<br />
scour data at bridges during floods by USGS and FHWA<br />
• The second USGS field-collection funded by FHWA (2005)<br />
Muller and Wagner (2005) … a deficiency that is primarily a reflection <strong>of</strong> <strong>the</strong> difficulty in<br />
collecting <strong>the</strong> necessary data. Accurate and complete field measurements <strong>of</strong> scour are<br />
difficult to obtain because <strong>of</strong> complex hydraulic conditions at bridges during floods, inability<br />
to get skilled personnel to bridge sites during floods, and problems associated with existing<br />
measuring equipment.<br />
13
Outline<br />
• Introduction<br />
• Literature review: scour monitoring<br />
practice and technologies<br />
• Validation <strong>of</strong> Time Domain Reflectometry<br />
<strong>for</strong> scour monitoring<br />
• <strong>TDR</strong> scour measurements in various<br />
environments<br />
• Development <strong>of</strong> a field <strong>TDR</strong> scour sensor<br />
• Summary and conclusions, and future<br />
work<br />
14
Literature review: scour monitoring<br />
practice and technologies<br />
• Fixed instruments<br />
• Portable instruments<br />
• Visual inspection<br />
15
2.1 Motivation <strong>for</strong> Scour Instrumentation<br />
• Hunt (2005)<br />
safety <strong>for</strong> <strong>the</strong> traveling public<br />
a reduced number <strong>of</strong> underwater and/or regular<br />
inspections<br />
early identification <strong>of</strong> problems prior to a diving inspection<br />
insight into site-specific scour processes<br />
Hawaii DOT, validation <strong>of</strong> HEC-18 equations by sonar<br />
devices<br />
Good instrumentation is essential <strong>for</strong> making proper<br />
decision, Georgia 1994 flood, 1000 bridge closed<br />
16
2.1 Motivation <strong>for</strong> Scour Instrumentation<br />
(cont.)<br />
• Challenges <strong>for</strong> scour monitoring instrumentations<br />
• Criteria <strong>for</strong> <strong>the</strong> instrumentation<br />
Mandatory Criteria<br />
•Capability <strong>for</strong> installation on or near a bridge pier<br />
or abutment<br />
•Ability to measure maximum scour depth within<br />
an accuracy <strong>of</strong> 0.3 m (1 ft)<br />
•Ability to obtain scour depth readings from above<br />
<strong>the</strong> water or from a remote site<br />
•Operable during storm and flood conditions<br />
Site conditions that cause<br />
interference or damage to<br />
<strong>the</strong> fixed scour monitoring<br />
systems (Hunt 2005)<br />
Desirable Criteria<br />
•Capability to be installed on most existing<br />
bridges or during construction <strong>of</strong> new bridges<br />
•Capability to operate in a range <strong>of</strong> flow<br />
conditions<br />
•Capability to withstand ice and debris<br />
•Vandal resistant<br />
•Operable and maintainable by highway<br />
maintenance personnel<br />
17
2.2 National Practice <strong>of</strong> Developing<br />
Instrumentation <strong>for</strong> Scour Monitoring<br />
• Zabilansky, 1996<br />
White River Junction, Vermont<br />
Instrumented fish and sediment chains<br />
(Zabilansky 1996)<br />
18
• Lagasse and Price 1997<br />
NCHRP Project 21-3, Instrumentation <strong>for</strong><br />
Measuring Scour at <strong>Bridge</strong> Piers and Abutments<br />
1. Sounding rods: manual or mechanical device<br />
(rod) to probe streambed;<br />
2. Buried or driven rods: device with sensors on<br />
vertical support, place or driven to streambed;<br />
3. Fathometers: commercially available sonic finder;<br />
and<br />
4. O<strong>the</strong>r buried devices: active or inert buried sensor<br />
(e.g., buried transmitter).<br />
Products: Sonic fathometers and a magnetic sliding<br />
collar device<br />
19
• Mueller and Landers 1999<br />
development <strong>of</strong> portable instruments <strong>for</strong> bridge<br />
scour monitoring<br />
1. physical probing such as sounding poles<br />
and sounding weights;<br />
2. sonar such as single-beam sonar, side<br />
scan, multi-beam, and scanning sonar;<br />
3. geophysical such as seismic instruments;<br />
4. and o<strong>the</strong>r such as underwater camera<br />
and green laser sensor<br />
Products: a low-cost echo sounder and a<br />
te<strong>the</strong>red kneeboard to deploy <strong>the</strong> transducer<br />
20
• Mueller and Landers 1999<br />
PVC-pontoon float <strong>for</strong> deploying a<br />
transducer<br />
A remote-control boat being<br />
tested near a pier<br />
21
• Schall and Price 2004<br />
NCHRP Project 21-07, portable scour instruments<br />
Products<br />
a portable scour monitoring device<br />
a fully instrumented articulated arm truck<br />
Articulated arm truck making a scour<br />
measurement (Schall and Price 2004)<br />
22
National practice <strong>of</strong> scour monitoring<br />
• Hunt 2005, a syn<strong>the</strong>sis study<br />
Total number <strong>of</strong> bridge sites with<br />
fixed scour monitoring<br />
instrumentation<br />
States with fixed scour monitoring<br />
installations<br />
23
2.3 Technologies <strong>for</strong> Scour Monitoring<br />
• Sonar<br />
• Magnetic Sliding Collar (MSC)<br />
• Time Domain Reflectometry (<strong>TDR</strong>)<br />
Sonar<br />
SOund NAvigation and Ranging<br />
active and passive<br />
echo sounders, fathometers, and acoustic depth sounders<br />
•Theory<br />
V (in feet per second) = 4388+<br />
(11.25 temperature (in F)) + (0.0182<br />
depth (in feet)) + salinity (in parts-perthousand)<br />
24
Sonar (cont.)<br />
A sonar system <strong>for</strong> bridge scour<br />
monitoring (Nassif et al. 2002)<br />
Schematic <strong>of</strong> a sonar scour monitoring<br />
system over Fire Island Inlet (Hunt 2005)<br />
25
Sonar (cont.)<br />
• wave frequency<br />
200 kHz<br />
• beam width Illustration <strong>of</strong> transducer beamwidth<br />
(Muller and Landers 1999)<br />
Effect <strong>of</strong> beamwidth on measured depth<br />
(Muller and Landers 1999)<br />
26
Sonar (cont.)<br />
• Data Acquisition<br />
• Limitations<br />
Fathometer data recorded with 200 kHz<br />
transducer (fathometer n.d.)<br />
1. at least 3 m and velocities less than 4 m/s<br />
2. turbulence, air entrainment, and heavy suspendedsediment<br />
3. noise from multiple reflections, and echoes from <strong>the</strong><br />
shoreline, water bottom, and/or piers<br />
27
Magnetic Sliding Collar<br />
• NCHRP Project 21-3 by Lagasse and Price (1997)<br />
• Basic Concepts<br />
A sliding magnetic collar on stainless steel<br />
pipe with driving point (Cooper et al. 2000).<br />
Schematic plot <strong>of</strong> magnetic sliding collar<br />
(Fukui and Otuka n.d.)<br />
• Limitations: shallow stream, refill, accuracy<br />
28
Time Domain Reflectometry<br />
Dowding and Pierce (1994)<br />
Yankielun and Zabilansky<br />
(1999)<br />
29
Basics<br />
Concepts<br />
EM Wave<br />
v<br />
p<br />
=<br />
c<br />
µ ε<br />
A <strong>TDR</strong> system<br />
r<br />
r<br />
A schematic plot <strong>of</strong> a <strong>TDR</strong> system<br />
Relative Voltage (V)<br />
1.25<br />
0.75<br />
0.25<br />
-0.25<br />
-0.75<br />
K<br />
a<br />
⎛<br />
= ⎜<br />
L<br />
= ⎜<br />
L<br />
=<br />
⎜<br />
⎝ L<br />
a<br />
p<br />
⎞<br />
⎟<br />
⎟<br />
⎠<br />
V s/2<br />
2<br />
Apparent Length, L a<br />
-1.25<br />
0 1 2 3 4 5 6 7 8<br />
Scaled Distance (m)<br />
A <strong>TDR</strong> wave<strong>for</strong>m<br />
EC<br />
b<br />
1 ⎛ ⎞<br />
⎜<br />
V ⎞<br />
= ⎜<br />
V ⎞ s<br />
= ⎜<br />
V s<br />
= − 1 ⎟<br />
C ⎜ ⎟<br />
⎝V<br />
⎟<br />
⎝V<br />
⎟<br />
⎝V<br />
f ⎠<br />
V f<br />
30
Reflection at Interface<br />
Reflection coefficient<br />
ρ =<br />
Air, Ka=1<br />
Z<br />
Z<br />
2<br />
2<br />
−<br />
+<br />
Z<br />
Z<br />
1<br />
1<br />
=<br />
K<br />
K<br />
a,<br />
1<br />
a,<br />
1<br />
−<br />
+<br />
K<br />
K<br />
a,<br />
2<br />
a,<br />
2<br />
Saturated soil, Ka=20~40 depending on density<br />
Water, Ka=81<br />
Change <strong>of</strong> impedance will cause<br />
reflection <strong>of</strong> EM wave<br />
Air<br />
Water<br />
Sediment<br />
<strong>TDR</strong> sensor <strong>for</strong> <strong>Bridge</strong> scour<br />
monitoring
Signal Analysis<br />
Topp et al. (1982)<br />
Baker and Allmaras (1990)<br />
32
Outline<br />
• Introduction<br />
• Literature review: scour monitoring<br />
practice and technologies<br />
• Validation <strong>of</strong> Time Domain Reflectometry<br />
<strong>for</strong> scour monitoring<br />
• <strong>TDR</strong> scour measurements in various<br />
environments<br />
• Development <strong>of</strong> a field <strong>TDR</strong> scour sensor<br />
• Summary and conclusions, and future<br />
work<br />
33
Validation <strong>of</strong> Time Domain Reflectometry<br />
<strong>for</strong> Scour Monitoring<br />
• <strong>TDR</strong> Measurements <strong>of</strong> Simulated Scour in laboratory<br />
• <strong>Algorithm</strong>s <strong>for</strong> <strong>TDR</strong> Signal Interpretation<br />
Sediment<br />
Photo <strong>of</strong> fine sand<br />
100%<br />
80%<br />
60%<br />
40%<br />
20%<br />
0%<br />
1.00<br />
Grain diameter (mm)<br />
0.10<br />
0.01<br />
Grain size distribution <strong>of</strong> fine sand<br />
% passing<br />
34
Experiment Setup and Procedure<br />
• Sand deposit gradually added while maintaining a<br />
constant water level<br />
• At each stage, a <strong>TDR</strong> signal is obtained
Data acquisition<br />
36
Voltage(V)<br />
Test results<br />
0.4<br />
0.0<br />
-0.4<br />
-0.8<br />
-1.2<br />
Increase <strong>of</strong> thickness <strong>of</strong> sediments<br />
thickness <strong>of</strong> sediments: 16cm<br />
thickness <strong>of</strong> sediments: 12cm<br />
thickness <strong>of</strong> sediments: 8cm<br />
thickness <strong>of</strong> sediments: 4cm<br />
thickness <strong>of</strong> sediments: 0cm<br />
0 2 4<br />
Length(m)<br />
6 8<br />
Increment Thickness (cm) K a,m EC b,m<br />
Sand<br />
added<br />
Sand Water mS/m g<br />
1 0 24 87.27 23.25 0<br />
2 4 20 74.43 20.982 3542<br />
3 8 16 62.92 17.953 3195<br />
4 12.5 11.5 50.01 14.82 3915<br />
5 16 8 44.85 13.593 3220<br />
6 20.5 3.5 31.62 10.394 3540<br />
7 21.7 2.3 32 9.578 990<br />
8 23.5 0.5 28.87 8.374 1731<br />
<strong>TDR</strong> wave<strong>for</strong>ms <strong>for</strong> different scour depth 37
Test results (cont.)<br />
K a,m<br />
K a,m<br />
90<br />
80<br />
70<br />
60<br />
50<br />
40<br />
30<br />
20<br />
100<br />
80<br />
60<br />
40<br />
20<br />
0<br />
y = -2.4799x + 84.418<br />
R² = 0.9891<br />
0 5 10 15 20 25<br />
Thickness <strong>of</strong> Sediment Layer(cm)<br />
Fine sand in tap water<br />
Fine sand in 250ppm NaCl solution<br />
Fine sand in 500ppm NaCl solution<br />
Fine sand in 750ppm NaCl solution<br />
0 5 10 15 20 25 30 35<br />
Thickness <strong>of</strong> sand layer (cm)<br />
EC b,m(mS/m)<br />
25<br />
20<br />
15<br />
10<br />
Saline water<br />
EC b,m<br />
Tap water<br />
120<br />
110<br />
100<br />
90<br />
80<br />
70<br />
60<br />
50<br />
40<br />
30<br />
20<br />
10<br />
5<br />
0<br />
y = -0.6294x + 23.224<br />
R² = 0.997<br />
0 5 10 15 20 25<br />
Thickness <strong>of</strong> Sediment Layer(cm)<br />
Fine sand in tap water<br />
Fine sand in 250ppm NaCl solution<br />
Fine sand in 500ppm NaCl solution<br />
Fine sand in 750ppm NaCl solution<br />
0 5 10 15 20 25 30 35<br />
Thickness <strong>of</strong> sand layer (cm)<br />
38
3.2 <strong>Algorithm</strong>s <strong>for</strong> <strong>TDR</strong> Signal Interpretation<br />
• Dielectric mixing <strong>for</strong>mula <strong>for</strong> scour estimation<br />
n<br />
α ( K ) = υ ( K )<br />
a,<br />
m<br />
∑<br />
i=<br />
1<br />
i<br />
a,<br />
i<br />
L 1 Ka,<br />
w + L2<br />
Ka,<br />
bs = L Ka,<br />
m<br />
K<br />
K<br />
a,<br />
m<br />
a,<br />
w<br />
=<br />
x<br />
L<br />
⎛<br />
⎜<br />
⎜<br />
⎝<br />
K<br />
K<br />
a,<br />
bs<br />
a,<br />
w<br />
α<br />
⎞<br />
−1⎟<br />
+ 1<br />
⎟<br />
⎠<br />
(Birchak et al. 1974)<br />
Water L1<br />
Sediment L2<br />
Setting <strong>the</strong> thickness <strong>of</strong> sediment L2 equal to x<br />
Dielectric scour estimation equation<br />
Approximate linear relationship between √K a,m and<br />
sediment thickness<br />
Sediment thickness can be estimated from measured K a,m<br />
39
Mixing Formula <strong>for</strong> Dielectric Constant and<br />
its Application<br />
Measured and<br />
predicted √K a,m /√K a,w<br />
versus sediment<br />
thickness<br />
Estimated thickness <strong>of</strong> sand layer (cm)<br />
30<br />
25<br />
20<br />
15<br />
10<br />
5<br />
0<br />
Fine sand in tap water<br />
Fine sand in 250ppm solution<br />
Linear Fit <strong>of</strong> Estimated thickness <strong>of</strong> sand layer<br />
Equation<br />
Weight<br />
Residual Sum<br />
<strong>of</strong> Squares<br />
Adj. R-Square<br />
Estimated<br />
thickness <strong>of</strong><br />
sand layer<br />
y = a + b*x<br />
No Weighting<br />
2.3419<br />
0.99859<br />
0 5 10 15 20 25 30 35<br />
Measured thickness <strong>of</strong> sand layer (cm)<br />
Value Standard Error<br />
Intercept 0 --<br />
Slope 0.98828 0.01315<br />
Thickness <strong>of</strong> sand layer estimated by <strong>the</strong><br />
dielectric constant mixing <strong>for</strong>mula<br />
40
Mixing Formula <strong>for</strong> Electrical Conductivity and<br />
its Application<br />
EC<br />
b,<br />
bs<br />
L1<br />
+ EC<br />
L<br />
, m<br />
w<br />
w<br />
L2<br />
L<br />
EC<br />
Akie's<br />
Law : Formation<br />
ECb<br />
⇒<br />
EC<br />
= 1−<br />
=<br />
f L1<br />
( 1−<br />
n )<br />
L<br />
b,<br />
m<br />
Factor<br />
1<br />
F<br />
ECb<br />
=<br />
EC<br />
= n<br />
– Approximate linear relationship between ECb,m and<br />
sediment thickness at a given electrical conductivity <strong>of</strong><br />
water<br />
– Predict sediment thickness from measured electrical<br />
conductivity ECb,m , bs<br />
w<br />
f<br />
b φ=2a<br />
L1<br />
L2<br />
L<br />
R1<br />
R2<br />
R
Mixing Formula <strong>for</strong> Electrical Conductivity and<br />
its Application<br />
ECb,<br />
m<br />
ECb,<br />
w =<br />
f x L − x<br />
n +<br />
L L<br />
Conductivity <strong>of</strong> Water(ms/m)<br />
30<br />
25<br />
20<br />
15<br />
10<br />
5<br />
0<br />
Estimated thickness <strong>of</strong> sand layer (cm)<br />
35 Fine sand in tap water<br />
Fine sand in 250ppm solution<br />
30<br />
Linear Fit <strong>of</strong> Estimated thickness <strong>of</strong> sand layer<br />
25<br />
20<br />
15<br />
10<br />
5<br />
0<br />
-5<br />
Equation y = a + b*x<br />
Weight No Weightin<br />
Residual Sum<br />
<strong>of</strong> Squares<br />
2.13288<br />
Adj. R-Square 0.99874<br />
Value Standard Err<br />
Estimated Intercept 0 --<br />
thickness <strong>of</strong><br />
sand layer<br />
Slope 1.0001<br />
6<br />
0.01255<br />
0 5 10 15 20 25 30 35<br />
Measured thickness <strong>of</strong> sand layer (cm)<br />
Estimated conductivity <strong>of</strong> water<br />
Measured conductivity <strong>of</strong> tap water<br />
0 5 10 15 20 25<br />
Thickness <strong>of</strong> Sand Layer (cm)
sqrt(Ka)/sqrt(kw)<br />
Empirical Equation Procedures <strong>for</strong> Application<br />
in <strong>Bridge</strong> Scour Monitoring<br />
• Dielectric constant<br />
1.0<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
Tap water<br />
250ppm<br />
500ppm<br />
750ppm<br />
Linear Fit <strong>of</strong> All Data<br />
Y = 1.00354 -0.43321 * X<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
Sand thickness/Total thickness <strong>of</strong> water and sand<br />
√K a,m /√K a,w versus <strong>the</strong><br />
normalized thickness <strong>of</strong><br />
sediment layer<br />
ECb/ECb,w<br />
• Electrical conductivity<br />
1.1<br />
1.0<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
0.4<br />
0.3<br />
Tap water<br />
250ppm<br />
500ppm<br />
750ppm<br />
Linear Fit <strong>of</strong> All Data<br />
Y = 1.02032 -0.66686 * X<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
Sand thickness/Total thickness <strong>of</strong> water and sand<br />
EC b,m/EC b,w versus <strong>the</strong><br />
normalized thickness <strong>of</strong><br />
sediment layer
Scour Prediction Based on Design Equations<br />
sqrt(Ka)/sqrt(kw)<br />
Step 1. Estimate scour depth;<br />
Step 2. Estimate electrical conductivity <strong>of</strong> water<br />
Step 3. Estimate density <strong>of</strong> sediment<br />
1.0<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
Measured Ka<br />
Step a)<br />
Y = 1 -0.43 * X<br />
Sand thickness ratio<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
sand thickness/Length <strong>of</strong> probe below water surface<br />
x r<br />
ECb/ECb,w<br />
1.1<br />
1.0<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
0.4<br />
0.3<br />
Conductivity <strong>of</strong> water<br />
Step b)<br />
Y = 1 -0.67 * X<br />
Sand thickness ratio<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
Sand thickness/Final sand thickness<br />
x r
River condition assessment<br />
• Electrical conductivity <strong>of</strong> water<br />
• Sediment in<strong>for</strong>mation: dry density, porosity<br />
K<br />
ECb,<br />
m<br />
ECb,<br />
w =<br />
f x L − x<br />
n +<br />
L L<br />
a,<br />
bs<br />
⎛ L L − x ⎞<br />
= ⎜ Ka<br />
, m − Ka,<br />
w ⎟<br />
⎝ x x ⎠<br />
2<br />
(1- θ)G s<br />
θ ρ d<br />
−6<br />
3<br />
−4<br />
2<br />
−2<br />
−2<br />
θ = 4.<br />
3×<br />
10 K a − 5.<br />
5×<br />
10 K a + 2.<br />
92×<br />
10 K a − 5.<br />
3×<br />
10 Topp Eq.
Results by Using Design Equation<br />
• Estimated sediment thickness<br />
Measured sand thickness/Total<br />
thickness <strong>of</strong> water and sand<br />
1.2<br />
1<br />
0.8<br />
0.6<br />
0.4<br />
0.2<br />
0<br />
1:1<br />
+5%<br />
-5%<br />
0 0.2 0.4 0.6 0.8 1 1.2<br />
Measured sand thickness/Total thickness <strong>of</strong> water and<br />
sand
Results by Using Design Equation<br />
• Estimated electrical conductivity <strong>of</strong> water<br />
Estimated water conductivity(ms/m)<br />
140<br />
120<br />
100<br />
80<br />
60<br />
40<br />
20<br />
0<br />
1:1<br />
+5%<br />
-%5<br />
0 20 40 60 80 100 120 140<br />
<strong>TDR</strong> measured water conductivity(ms/m)
Results by Using Design Equation<br />
• Estimated density <strong>of</strong> sediments<br />
<strong>TDR</strong> Estimated Sediments Dry density(g/cm 3 )<br />
1.8<br />
1.7<br />
1.6<br />
1.5<br />
1.4<br />
1.3<br />
1.2<br />
Predicted_Tap water<br />
Predicted_750ppm<br />
Predicted_500ppm<br />
Predicted_250ppm<br />
1:1<br />
+5%<br />
-5%<br />
1.4 1.5 1.6 1.7<br />
Actual Dry density(g/cm 3 )
Scour Estimation Based on Detecting <strong>the</strong><br />
Reflection at Water/Sediment Interface<br />
Reflection detection methods<br />
Relative Votage<br />
0.4<br />
0.2<br />
0<br />
-0.2<br />
-0.4<br />
-0.6<br />
-0.8<br />
-1<br />
Identified location <strong>of</strong> reflections<br />
by <strong>the</strong> automatic signal<br />
analyses<br />
(1)Probe beginning<br />
(2)Water/sediment interface<br />
(3)End <strong>of</strong> probe<br />
-1.2<br />
0 2 4<br />
Length(m)<br />
6 8<br />
1<br />
2<br />
3<br />
49
<strong>Algorithm</strong> <strong>of</strong> signal analysis<br />
Input <strong>the</strong> original <strong>TDR</strong> signal to <strong>the</strong> MATLAB work<br />
space; name <strong>the</strong> signal with “y”.<br />
Use 7 points averaging method to smooth <strong>the</strong> original wave<strong>for</strong>m<br />
Get <strong>the</strong> data points behind <strong>the</strong> peak point in <strong>the</strong> smoo<strong>the</strong>d curve, and calculate <strong>the</strong><br />
slop <strong>of</strong> this selected curve section<br />
Use Max and Min function to find <strong>the</strong> maximum and minimum slop.<br />
Maximum slope point is <strong>the</strong> second reflection point<br />
Polyfit <strong>the</strong> minimum slop line using 7 points centered <strong>the</strong> minimum<br />
<strong>the</strong> slope point, find <strong>the</strong> intersection with line y=ymax , this is <strong>the</strong><br />
first reflection point<br />
Find <strong>the</strong> maximum slope point between <strong>the</strong> maximum and minimum slope point.<br />
Find <strong>the</strong> first point be<strong>for</strong>e <strong>the</strong> maximum slope point that has negative slope, use<br />
Max function find <strong>the</strong> maximum slope point between this point and minimum slope<br />
point. This is <strong>the</strong> second reflection point<br />
Determination <strong>of</strong> apparent length: = (index <strong>of</strong> <strong>the</strong> second reflection point – index <strong>of</strong> <strong>the</strong><br />
second reflection point)*8/2047; Thus we can get <strong>the</strong> physical length <strong>of</strong> water layer<br />
thickness.<br />
50
Sample results<br />
0.01<br />
0<br />
-0.01<br />
-0.02<br />
First derivative (only <strong>the</strong> section after <strong>the</strong> first peak point)<br />
-0.03<br />
0 500 1000 1500 2000 2500<br />
Index <strong>of</strong> data points<br />
Voltage(V)<br />
0.5<br />
0<br />
-0.5<br />
-1<br />
Reflection points on <strong>the</strong> smoo<strong>the</strong>d wave<strong>for</strong>m<br />
-1.5<br />
0 500 1000 1500 2000 2500<br />
Index <strong>of</strong> data points<br />
30<br />
Measured scour based on<br />
reflection detection<br />
<strong>TDR</strong> measured scour depth (cm)<br />
35 fine sand in tap water<br />
fine sand in 250ppm saline water<br />
1:1 line<br />
25<br />
20<br />
15<br />
10<br />
5<br />
0<br />
Reflection detection<br />
0 5 10 15 20 25 30 35<br />
Measured scour depth (cm)<br />
51
Outline<br />
• Introduction<br />
• Literature review: scour monitoring<br />
practice and technologies<br />
• Validation <strong>of</strong> Time Domain Reflectometry<br />
<strong>for</strong> scour monitoring<br />
• <strong>TDR</strong> scour measurements in various<br />
environments<br />
• Development <strong>of</strong> a field <strong>TDR</strong> scour sensor<br />
• Summary and conclusions, and future<br />
work<br />
52
Monitoring <strong>of</strong> Simulated Scour in Various<br />
Soil and Water Conditions<br />
• Testing materials<br />
53
Test Results<br />
Fine Sand<br />
Normalized dielectric constant<br />
1.0<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
0.4<br />
0.3<br />
0.2<br />
0.1<br />
0.0<br />
Equation y = a + b*x<br />
Adj. R-Squ 0.99597<br />
Value Standard Error<br />
Concatenat Intercept 1.00376 0.00319<br />
Concatenat Slope -0.434 0.00531<br />
Fine sand in tap water<br />
Fine sand in 250ppm NaCl solution<br />
Fine sand in 500ppm NaCl solution<br />
Fine sand in 750ppm NaCl solution<br />
Desing equation <strong>for</strong> fine sand<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
Normalized thickness <strong>of</strong> sediment layer<br />
Normalized electrical conductivity<br />
1.1<br />
1.0<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
0.4<br />
0.3<br />
0.2<br />
0.1<br />
0.0<br />
Equation y = a + b*<br />
Adj. R-Sq 0.99007<br />
Value Standard<br />
Concaten Intercept 1.02032 0.0078<br />
Concaten Slope -0.66686 0.01262<br />
Fine sand in tap water<br />
Fine sand in 250ppm NaCl solution<br />
Fine sand in 500ppm NaCl solution<br />
Fine sand in 750ppm NaCl solution<br />
Design equation <strong>for</strong> fine sand<br />
Normalized <strong>TDR</strong> measurements <strong>for</strong> fine sand<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
Normalized thickness <strong>of</strong> sediment layer<br />
54
Normalized dielectric constant<br />
1.0<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
0.4<br />
0.3<br />
0.2<br />
0.1<br />
0.0<br />
Coarse sand<br />
Equation<br />
Adj. R-Square<br />
Concatenate<br />
y = a + b*x<br />
0.99687<br />
Value Standard Error<br />
Intercept 0.99824 0.00414<br />
Slope -0.42083 0.0068<br />
Coarse sand in 500ppm NaCl solution<br />
Washed coarse sand in 500ppm NaCl solution<br />
Linear fit<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
Normalized thickness <strong>of</strong> sediment layer<br />
Normalized electrical conductivity<br />
1.1<br />
1.0<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
0.4<br />
0.3<br />
0.2<br />
0.1<br />
0.0<br />
Equation<br />
Adj. R-Square<br />
Concatenate<br />
y = a + b*x<br />
0.95481<br />
Normalized <strong>TDR</strong> measurements <strong>for</strong> coarse sand<br />
Value Standard Error<br />
Intercept 1.02652 0.02283<br />
Slope -0.59837 0.03751<br />
Coarse sand in 500ppm NaCl solution<br />
Washed coarse sand in 500ppm NaCl solution<br />
Linear fit<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
Normalized thickness <strong>of</strong> sediment layer<br />
55
Normalized dielectric constant<br />
Gravel<br />
1.0<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
0.4<br />
0.3<br />
0.2<br />
0.1<br />
0.0<br />
Equation y = a + b*x<br />
Adj. R-Square 0.99215<br />
Value Standard Error<br />
Concatenate Intercept 0.99574 0.00425<br />
Concatenate Slope -0.31801 0.00686<br />
Gravel in tap water<br />
Gravel in 500ppm NaCl solution<br />
Washed gravel in 500ppm NaCl solution<br />
Linear Fit<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
Normalized thickness <strong>of</strong> sediment layer<br />
Normalized electrical conductivity<br />
1.1<br />
1.0<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
0.4<br />
0.3<br />
0.2<br />
0.1<br />
0.0<br />
Equation<br />
Adj. R-Square<br />
Concatenate<br />
y = a + b*x<br />
Normalized <strong>TDR</strong> measurements <strong>for</strong> gravel<br />
0.96387<br />
Value Standard Error<br />
Intercept 1.00171 0.01593<br />
Slope -0.54842 0.02572<br />
Gravel in tap water<br />
Gravel in 500ppm NaCl solution<br />
Washed gravel in 500ppm NaCl solution<br />
Linear Fit <strong>of</strong> Concatenate<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
Normalized thickness <strong>of</strong> sediment layer<br />
56
Normalized dielectric constant<br />
1.0<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
0.4<br />
0.3<br />
0.2<br />
0.1<br />
0.0<br />
Coarse Sand and Gravel Mixture<br />
Equation<br />
Adj. R-Square<br />
Normalized dielectric<br />
constant<br />
y = a + b*x<br />
0.99605<br />
Value Standard Error<br />
Intercept 1.00613 0.00911<br />
Slope -0.48865 0.01375<br />
Coarse sand and gravel mixture in 500ppm NaCl solution<br />
Linear fit<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
Normalized thickness <strong>of</strong> sediment layer<br />
Normalized electrical conductivity<br />
1.1<br />
1.0<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
0.4<br />
0.3<br />
0.2<br />
0.1<br />
0.0<br />
Equation y = a + b*x<br />
Adj. R-Square 0.99181<br />
Value Standard Error<br />
Normalized Intercept 1.02449 0.02064<br />
electrical<br />
conductivity<br />
Slope -0.76812 0.03118<br />
Coarse sand and gravel mixture in 500ppm NaCl solution<br />
Linear fit<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
Normalized thickness <strong>of</strong> sediment layer<br />
Normalized <strong>TDR</strong> measurements <strong>for</strong> coarse sand and gravel mix<br />
57
Scour Estimation Equation <strong>for</strong> Different Soils<br />
Applying mixing <strong>for</strong>mula to saturated sediment<br />
Solve <strong>for</strong> porosity n<br />
Average<br />
porosity<br />
a<br />
w<br />
( − n)<br />
Ka<br />
, s Ka<br />
bs<br />
n K , + 1 = ,<br />
n<br />
=<br />
Slope <strong>of</strong><br />
equation (3)<br />
K<br />
K<br />
a,<br />
bs<br />
a,<br />
w<br />
−<br />
−<br />
Theoretically Predicted and Empirical Fitted Slope <strong>of</strong> Design Equations<br />
K<br />
K<br />
fitted slope <strong>of</strong><br />
equation (3)<br />
a,<br />
s<br />
a,<br />
s<br />
Slope <strong>of</strong><br />
equation (4)<br />
fitted slope <strong>of</strong><br />
equation (4)<br />
Fine sand 0.417 -0.424 -0.434 -0.670 -0.667<br />
Coarse sand 0.422 -0.421 -0.421 -0.666 -0.598<br />
Gravel 0.569 -0.314 -0.318 -0.511 -0.548<br />
mixture 0.356 -0.468 -0.489 -0.730 -0.768<br />
K<br />
K<br />
a,<br />
m<br />
a,<br />
w<br />
b,<br />
w<br />
=<br />
x ⎛<br />
⎜<br />
L ⎜<br />
⎝<br />
ECb, m f<br />
EC<br />
=<br />
K<br />
K<br />
a,<br />
bs<br />
a,<br />
w<br />
⎞<br />
−1⎟<br />
+ 1<br />
⎟<br />
⎠<br />
x ( n −1)<br />
+ 1<br />
L<br />
58
<strong>TDR</strong> measurements <strong>of</strong> scour <strong>for</strong> different<br />
sediments (based on dielectric constant)<br />
Normalized <strong>TDR</strong> measured thickness <strong>of</strong> sediment layer<br />
1.2<br />
1.0<br />
0.8<br />
0.6<br />
0.4<br />
0.2<br />
0.0<br />
Fine sand in tap water<br />
Fine sand in 250ppm NaCl solution<br />
Fine sand in 500ppm NaCl solution<br />
Fine sand in 750ppm NaCl solution<br />
Coarse sand in 500ppm NaCl solution<br />
Gravel in tap water<br />
Gravel in 500ppm NaCl solution<br />
+5% error<br />
Washed coarse sand in 500ppm NaCl solution<br />
Washed gravel in 500ppm NaCl solution<br />
Coarse sand and gravel mixture in 500ppm NaCl solution<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
-5% error<br />
Normalized physically measured thickness <strong>of</strong> sediment layer<br />
<strong>TDR</strong> measurements (dielectric constant) versus physical measurements (cm<br />
ruler) <strong>of</strong> thickness <strong>of</strong> sediment layer <strong>for</strong> all sediments.<br />
59
<strong>TDR</strong> measurements <strong>of</strong> scour <strong>for</strong> different<br />
sediments (based on electric conductivity)<br />
Normalized <strong>TDR</strong> measured thickness <strong>of</strong> sediment layer<br />
1.2<br />
1.0<br />
0.8<br />
0.6<br />
0.4<br />
0.2<br />
0.0<br />
-0.2<br />
Fine sand in tap water<br />
Fine sand in 250ppm NaCl solution<br />
Fine sand in 500ppm NaCl solution<br />
Fine sand in 750ppm NaCl solution<br />
Coarse sand in 500ppm NaCl solution<br />
Gravel in tap water<br />
Gravel in 500ppm NaCl solution<br />
Washed coarse sand in 500ppm NaCl solution +5% error<br />
Washed gravel in 500ppm NaCl solution<br />
Coarse sand and gravel mixture in 500ppm NaCl solution<br />
-5% error<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
Normalized physically measured thickness <strong>of</strong> sediment layer<br />
<strong>TDR</strong> measurements (electric conductivity) versus physical<br />
measurements (cm ruler) <strong>of</strong> thickness <strong>of</strong> sediment layer <strong>for</strong> all<br />
sediments.<br />
60
Scour Monitoring in Water <strong>of</strong> High<br />
Electrical Conductivity<br />
Wave<strong>for</strong>m be<strong>for</strong>e and after using insulated probe<br />
(Drnevich et al. 2003)<br />
61
Insulated <strong>TDR</strong> probe<br />
2000ppm NaCl solution<br />
Wave<strong>for</strong>ms by insulated probe<br />
Voltage (V)<br />
0.4<br />
0.2<br />
0.0<br />
-0.2<br />
-0.4<br />
-0.6<br />
-0.8<br />
-1.0<br />
Thickness <strong>of</strong> sediment layer 0cm<br />
Thickness <strong>of</strong> sediment layer 4.8cm<br />
Thickness <strong>of</strong> sediment layer 10.6cm<br />
Thickness <strong>of</strong> sediment layer 15.1cm<br />
Thickness <strong>of</strong> sediment layer 20.8cm<br />
Thickness <strong>of</strong> sediment layer 25.6cm<br />
Thickness <strong>of</strong> sediment layer 30.5cm<br />
-1.2<br />
0 1 2 3 4 5 6 7 8 9<br />
Scaled distance (m)<br />
62
Dielectric constant by insulated probe<br />
Normalized dielectric constant<br />
1.00<br />
0.95<br />
0.90<br />
0.85<br />
0.80<br />
0.75<br />
0.70<br />
Equation y = a + b*x<br />
Adj. R-Square 0.97485<br />
Normalized dielectric<br />
constant<br />
Normalized dielectric<br />
constant<br />
Value Standard Error<br />
Intercept 0.9862 0.01008<br />
Slope -0.25473 0.01667<br />
0.0 0.2 0.4 0.6 0.8 1.0<br />
Normalized thickness <strong>of</strong> sediment layer<br />
Normalized dielectric constant versus<br />
normalized thickness <strong>of</strong> sediment layer.<br />
K = wK + 1−<br />
n<br />
c<br />
n<br />
coating<br />
( ) n<br />
w K<br />
a<br />
Predicted Ka<br />
40<br />
35<br />
30<br />
25<br />
20<br />
15<br />
Predicted value using Equation 4.3<br />
1:1<br />
15 20 25 30 35 40<br />
Ka measured by coated <strong>TDR</strong> probe<br />
Predicted dielectric constant versus<br />
that measured by coated probe.<br />
Dielectric constant (coated -> uncoated)<br />
(Ferré et al. 1996)<br />
63
Scour Monitoring in Turbulent Flow<br />
Entrapped Air<br />
Scour measurement in water with entrapped air<br />
Voltage (V)<br />
0.5<br />
0.0<br />
-0.5<br />
-1.0<br />
Signal with low air<br />
bubble concentration<br />
Signal with high air<br />
bubble concentration<br />
-1 0 1 2 3 4 5 6 7 8 9<br />
Scaled distance(m)<br />
Signal with no air bubble<br />
Effect <strong>of</strong> air bubble on <strong>TDR</strong> wave<strong>for</strong>m<br />
64
Effect <strong>of</strong> air bubbles on dielectric<br />
constant<br />
Dielectric constant<br />
90<br />
80<br />
70<br />
60<br />
50<br />
40<br />
30<br />
20<br />
No air<br />
Low air bubble concentraion<br />
High air bubble concentraion<br />
0 5 10 15 20 25 30<br />
Thickness <strong>of</strong> sand layer (cm)<br />
65
Effect <strong>of</strong> suspended sediments<br />
Scour measurement in water<br />
with suspended sediments<br />
Dielectric constant<br />
versus time<br />
66
Scour monitoring in water with varying<br />
Water Level<br />
Part <strong>of</strong> sensor in air<br />
Air water interface End <strong>of</strong> probe<br />
Sensor head<br />
Screen shot <strong>of</strong> wave<strong>for</strong>m analysis program<br />
67
“Dry Scour”<br />
Dry scour depth by <strong>TDR</strong> (cm)<br />
35<br />
30<br />
25<br />
20<br />
15<br />
10<br />
5<br />
0<br />
Dry scour depth by <strong>TDR</strong><br />
Linear Fit <strong>of</strong> Dry scour depth by <strong>TDR</strong><br />
Equation<br />
Weight<br />
Residual Sum<br />
<strong>of</strong> Squares<br />
Adj. R-Square<br />
y = a + b*x<br />
No Weighting<br />
24.13911<br />
Relative voltage(V)<br />
0 5 10 15 20 25 30 35<br />
Dry scour depth by ruler (cm)<br />
0.98586<br />
1.2<br />
0.6<br />
0.0<br />
-0.6<br />
-1.2<br />
Value Standard Error<br />
Dry scour depth Intercept 0 --<br />
Dry scour depth Slope 1.08463 0.05801<br />
Pure air<br />
Increase thickness <strong>of</strong> wet sand layer<br />
Air/wet sand interface<br />
0 3 6<br />
Scaled distance(m)<br />
Zoom in View<br />
Pure wet sand<br />
Dry scour wave<strong>for</strong>ms<br />
Dry scour depth by <strong>TDR</strong><br />
68
A Comparison <strong>of</strong> <strong>TDR</strong> and Ultrasound<br />
Method<br />
• Background <strong>of</strong> Ultrasonic Method<br />
Ultrasonic<br />
transducer<br />
ater<br />
ediment<br />
Ultrasound<br />
pulse generator<br />
Oscilloscope<br />
Schematic <strong>of</strong> a typical ultrasonic<br />
testing system<br />
Votage(mv)<br />
400<br />
Pulse signal<br />
200<br />
0<br />
-200<br />
-400<br />
-600<br />
-800<br />
1st reflection at <strong>the</strong> water and sediment interface<br />
Round trip time from water surface to<br />
water and sediment interface<br />
-0.5 0 0.5 1 1.5 2 2.5<br />
x 10 6<br />
-1000<br />
Time(ns)<br />
A typical ultrasonic signal<br />
69
Test setup<br />
70
Voltage(V)<br />
Results<br />
0.5<br />
0.0<br />
-0.5<br />
-1.0<br />
-1.5<br />
Thickness <strong>of</strong> water layer: 30.5cm<br />
Thickness <strong>of</strong> water layer: 23cm<br />
Thickness <strong>of</strong> water layer:15.9cm<br />
Thickness <strong>of</strong> water layer: 9cm<br />
Thickness <strong>of</strong> water layer: 2.5cm<br />
Thickness <strong>of</strong> water layer: 0cm<br />
0 2 4 6 8<br />
Length(m)<br />
Decreas in thickness<br />
<strong>of</strong> water layer<br />
a) Variations <strong>of</strong> <strong>TDR</strong> signals with scour<br />
depth; b) Variations <strong>of</strong> ultrasonic signals<br />
with scour depth.<br />
Voltage(mv)<br />
Voltage(mv)<br />
Voltage(mv)<br />
Voltage(mv)<br />
1000<br />
0<br />
thickness <strong>of</strong> water layer: 30.5cm<br />
-1 0 1 2 3 4 5 6<br />
x 10 5<br />
-1000<br />
Time(ns)<br />
thickness <strong>of</strong> water layer: 23cm<br />
1000<br />
0<br />
-1 0 1 2 3 4 5 6<br />
x 10 5<br />
-1000<br />
Time(ns)<br />
thickness <strong>of</strong> water layer: 15.9cm<br />
1000<br />
0<br />
-1 0 1 2 3 4 5 6<br />
x 10 5<br />
-1000<br />
Time(ns)<br />
thickness <strong>of</strong> water layer: 9cm<br />
1000<br />
0<br />
-1 0 1 2 3 4 5 6<br />
x 10 5<br />
-1000<br />
Time(ns)<br />
71
Measurements <strong>of</strong> scour<br />
Sensor measured water thickness (Normalized)<br />
1.2<br />
1<br />
0.8<br />
0.6<br />
0.4<br />
0.2<br />
0<br />
-0.2<br />
<strong>TDR</strong> method 1<br />
0 0.2 0.4 0.6 0.8 1 1.2<br />
1:1<br />
Ultrasonic method<br />
<strong>TDR</strong> method 2<br />
Ruler measured water thickness(Normalized)<br />
Prediction <strong>of</strong> scour depth using <strong>TDR</strong> and<br />
Ultrasonic method (<strong>TDR</strong> method 1; and<br />
<strong>TDR</strong> method 2)<br />
<strong>TDR</strong> method 1<br />
K<br />
K<br />
a,<br />
m<br />
a,<br />
w<br />
=<br />
x ⎛<br />
⎜<br />
L ⎜<br />
⎝<br />
K<br />
K<br />
a,<br />
bs<br />
a,<br />
w<br />
⎞<br />
−1⎟<br />
+ 1<br />
⎟<br />
⎠<br />
<strong>TDR</strong> method 2:<br />
Design equation<br />
72
ECb,w(ms/m)<br />
Electric conductivity <strong>of</strong> water and dry<br />
density <strong>of</strong> sediment by <strong>TDR</strong><br />
120<br />
100<br />
80<br />
60<br />
40<br />
20<br />
Measured by <strong>TDR</strong><br />
Measured by Ec Meter<br />
0<br />
0 5 10 15 20 25 30 35<br />
Sediment thickness(cm)<br />
Prediction <strong>of</strong> electrical conductivity<br />
<strong>of</strong> water versus depth<br />
Dry density(g/cm^3)<br />
2.5<br />
2<br />
1.5<br />
1<br />
0.5<br />
0<br />
Predicted<br />
Measured<br />
0 5 10 15 20 25 30 35<br />
Sediment thickness(cm)<br />
Sediment densities predicted by <strong>TDR</strong><br />
versus depth<br />
73
Comparison <strong>of</strong> <strong>TDR</strong> and Ultrasonic Method<br />
• Both <strong>TDR</strong> and ultrasonic methods can accurately measure scour depth.<br />
• <strong>TDR</strong> system:<br />
– Inexpensive, automatic<br />
– More in<strong>for</strong>mation<br />
• sediment status (density) and water conditions (electrical conductivity)<br />
– Accuracy can be affected by electromagnetic interference and signal<br />
attenuation in <strong>the</strong> cable length.<br />
– Local measurement. Multiplexing is needed to map <strong>the</strong> scour hole shape.<br />
• Field <strong>TDR</strong> probes need to be rugged and inexpensive<br />
• Deployment <strong>of</strong> <strong>the</strong> <strong>TDR</strong> probes also needs to be well planned.<br />
• Ultrasound method:<br />
– Post-event scour measurement.<br />
– Coupling with water requires transducer maintained below <strong>the</strong> water level.<br />
– Also a local measurement.<br />
• ultrasonic transducer can be moved to determine <strong>the</strong> shape <strong>of</strong> river bed after<br />
scour event.<br />
– Interpretation <strong>of</strong> ultrasonic signal can be challenging especially <strong>for</strong> complex<br />
river bed territories.<br />
• Background noise<br />
• Expertise needed <strong>for</strong> a sound interpretation <strong>of</strong> measurement results.
Outline<br />
• Introduction<br />
• Literature review: scour monitoring<br />
practice and technologies<br />
• Validation <strong>of</strong> Time Domain Reflectometry<br />
<strong>for</strong> scour monitoring<br />
• <strong>TDR</strong> scour measurements in various<br />
environments<br />
• Development <strong>of</strong> a field <strong>TDR</strong> scour sensor<br />
• Summary and conclusions, and future<br />
work<br />
75
5.1 Introduction<br />
• <strong>TDR</strong> Measurements in Highly Conductive Materials<br />
remote diode shortening<br />
coated <strong>TDR</strong> probes<br />
• Sampling Area <strong>of</strong> Coated <strong>TDR</strong> Probe and <strong>the</strong> Effective<br />
Measured Dielectric Constant<br />
The sample volume is <strong>the</strong> region <strong>of</strong> <strong>the</strong> porous medium that contributes to <strong>the</strong><br />
total probe response: changes in <strong>the</strong> properties <strong>of</strong> <strong>the</strong> porous medium outside<br />
this volume do not have significant influence on <strong>the</strong> response <strong>of</strong> <strong>the</strong> instrument.<br />
Ka e ∫∫ Ka<br />
Ω<br />
( x,<br />
y)<br />
w(<br />
x,<br />
y)<br />
, = dA<br />
( ) ( ) ( ) ⎟ ⎛<br />
⎞<br />
2<br />
2<br />
w x,<br />
y = | E x,<br />
y | / ⎜<br />
∫∫|<br />
Eo<br />
x,<br />
y | dA<br />
⎝ Ω<br />
⎠<br />
f<br />
∫∫<br />
Ω<br />
∑<br />
100×<br />
wi<br />
Ai<br />
wh =<br />
w dA<br />
i<br />
Ferré et al. (1998)<br />
76
5.2 Use <strong>of</strong> FEMLAB <strong>for</strong> <strong>TDR</strong> Probe Design<br />
a,<br />
e<br />
K a, 1 (5)<br />
K a, 2 (10)<br />
I<br />
K = +<br />
0. 5K<br />
a,<br />
1 0.<br />
5K<br />
a,<br />
2<br />
K a, 1 (5)<br />
II<br />
K<br />
−1<br />
a,<br />
e<br />
K a, 2 (10)<br />
−1<br />
−1<br />
= 0.<br />
5K<br />
a,<br />
1 + 0.<br />
5K<br />
a,<br />
2<br />
77
FEMLAB model <strong>of</strong> Case I<br />
B.C.s<br />
78
Electric field, Case I<br />
79
Electric energy density, Case I<br />
Electric energy density (contour and color)<br />
and electric field (arrow)<br />
80
• Effective measured dielectric constant<br />
• Case II<br />
K<br />
W<br />
, =<br />
e,<br />
n<br />
a e<br />
We,<br />
o<br />
W e, n <strong>for</strong> case I is 2.39E-10 (Joule/m)<br />
W e, o is 3.18E-11 (Joule/m)<br />
K a, e=7.51<br />
Analytical solution 7.5<br />
Case II: solved electric potential (color and<br />
contour line) and electric field (arrow).<br />
81
Electric energy density, Case II<br />
Electric energy density (contour and color) and electric field (arrow)<br />
The effective measured dielectric constant:6.95<br />
Analytical solution: 6.67<br />
82
Sampling area<br />
∫∫<br />
Ω<br />
∑<br />
100 × We<br />
A i i<br />
f = wh<br />
W dA<br />
ei<br />
Sampling area <strong>of</strong> Case I<br />
at 90% energy level<br />
Sampling area <strong>of</strong> Case II at<br />
90% energy level<br />
83
5.3 Coated <strong>TDR</strong> CS605 Moisture Probe<br />
FEMLAB model<br />
Electric-energy density <strong>for</strong> saline water<br />
and sampling area (90% total energy)<br />
Electric-energy density <strong>for</strong> saline water and<br />
sampling area (90% total energy, uncoated probe)<br />
84
5.3 Coated <strong>TDR</strong> CS605 Moisture Probe<br />
Saturated sediment<br />
Electric-energy density <strong>for</strong> saturated sand and<br />
sampling area (90% total energy, coated probe)<br />
Calculated effective measured<br />
dielectric constant by <strong>the</strong><br />
coated <strong>TDR</strong> probe<br />
Effective measured dielectric constant<br />
40<br />
35<br />
30<br />
25<br />
20<br />
Electric-energy density <strong>for</strong> saturated sand and<br />
sampling area (90% total energy, uncoated probe)<br />
Effective measured dielectric constant<br />
Linear Fit <strong>of</strong> Effective measured dielectric constant<br />
Equation y = a + b*x<br />
Weight<br />
No Weighting<br />
Residual Sum <strong>of</strong><br />
Squares<br />
8.10454<br />
Adj. R-Square<br />
0.99831<br />
Value Standard Error<br />
Effective measure Intercept 0 --<br />
Effective<br />
measured<br />
dielectric constant<br />
Slope 0.99026 0.01538<br />
20 25 30 35 40<br />
<strong>TDR</strong> measured dielectric constant<br />
85
5.4 A New Field <strong>TDR</strong> Scour Sensor<br />
Photo <strong>of</strong> a <strong>TDR</strong> strip sensor<br />
Photo <strong>of</strong> <strong>the</strong> prototype strip bridge<br />
scour sensor<br />
86
Lab Evaluation <strong>of</strong> Strip Scour Sensor<br />
Scour sensor <strong>for</strong> field application<br />
Voltage (V)<br />
0.3<br />
0.2<br />
0.1<br />
0.0<br />
-0.1<br />
-0.2<br />
-0.3<br />
-0.4<br />
Water<br />
thickness <strong>of</strong> sand: 36cm<br />
thickness <strong>of</strong> sand: 44cm<br />
thickness <strong>of</strong> sand: 55cm<br />
thickness <strong>of</strong> sand: 74cm<br />
thickness <strong>of</strong> sand: 86cm<br />
thickness <strong>of</strong> sand: 99cm<br />
0 500 1000 1500 2000<br />
Distance (points)<br />
Wave<strong>for</strong>ms <strong>for</strong> simulated scour<br />
87
Results<br />
Reflection<br />
at<br />
air/water<br />
interface<br />
( point<br />
index)<br />
Reflection<br />
at<br />
water/sand<br />
interface<br />
( point<br />
index)<br />
Reflection<br />
at <strong>the</strong> end <strong>of</strong><br />
probe<br />
( point<br />
index)<br />
water<br />
depth<br />
(cm)<br />
sand<br />
depth<br />
(cm)<br />
Ka, w Ka, s Ka, mix<br />
972 1305 1450 63.1 35.9 26.59 15.6 22.3<br />
972 1270 1435 54.8 44.2 28.23 13.3 20.9<br />
976 1201 1408 43.2 55.8 25.90 13.1 18.2<br />
972 1105 1381 25 74 27.02 13.3 16.3<br />
976 1046 1368 12.9 86.1 28.11 13.4 15.0<br />
971 N.A. 1343 N.A. 99.0 N.A. 13.5 13.5<br />
Normalized measured<br />
dielectric constant<br />
Normalized K a, mix<br />
0.9<br />
0.8<br />
0.7<br />
0.6<br />
0.5<br />
0.4<br />
0.3<br />
0.2<br />
0.1<br />
0.0<br />
y = -0.5023x + 0.9887<br />
R² = 0.9787<br />
0.0 0.2 0.4 0.6 0.8 1.0 1.2<br />
Normalized sand thickness<br />
88
FEMLAB Analysis <strong>of</strong> <strong>the</strong> Per<strong>for</strong>mance <strong>of</strong><br />
<strong>the</strong> Strip Scour Sensor<br />
89
A zoom in view <strong>of</strong> <strong>the</strong> strip scour sensor<br />
Dielectric constant:<br />
Tape: 3.0<br />
Teflon: 2.1<br />
Air: 1 fiber glass U-channel: 6<br />
90
Electric potential<br />
Sensor in water<br />
91
Sampling area, tap water<br />
Field <strong>of</strong> energy-density and sampling area<br />
(filled with tap water)<br />
92
Sampling area, saturate sand<br />
Field <strong>of</strong> energy-density and sampling area<br />
(filled with saturated sand).<br />
93
• Effective measured dielectric constant<br />
– Tap water: 26.2 (numerical simulation), 26.6<br />
<strong>TDR</strong> measurement<br />
– Saturated sand: 13.3 (numerical simulation),<br />
13.3 <strong>TDR</strong> measurement<br />
• Calibration equation<br />
K =<br />
−<br />
−<br />
a,<br />
r<br />
2<br />
59. 50 + 7.<br />
93K<br />
a,<br />
m 0.<br />
12K<br />
a,<br />
m<br />
Real dielectric constant<br />
60<br />
55<br />
50<br />
45<br />
40<br />
35<br />
30<br />
25<br />
Real dielectric constant<br />
Polynomial Fit <strong>of</strong> Real dielectric constant<br />
12 14 16 18 20 22<br />
Measured dielectric constant<br />
Model<br />
Polynomial<br />
Equation<br />
y = Intercept + B1*x^1 + B2*x^2<br />
Weight<br />
No Weighting<br />
Residual Sum <strong>of</strong><br />
Squares<br />
4.13799<br />
Adj. R-Square<br />
0.99099<br />
Value Standard Error<br />
Intercept -59.50104 20.48274<br />
Real dielectric<br />
constant<br />
B1<br />
B2<br />
7.92859<br />
-0.12049<br />
2.33675<br />
0.06493<br />
94
Scour measurement<br />
<strong>TDR</strong> measured scour depth (cm)<br />
70<br />
60<br />
50<br />
40<br />
30<br />
20<br />
10<br />
0<br />
<strong>TDR</strong> measured scour depth<br />
Linear Fit <strong>of</strong> Estimated scour depth<br />
Equation<br />
Weight<br />
Residual Sum<br />
<strong>of</strong> Squares<br />
Adj. R-Square<br />
y = a + b*x<br />
No Weighting<br />
1.69151E-27<br />
-10<br />
-10 0 10 20 30 40 50 60 70<br />
Physically measured scour depth (cm)<br />
1<br />
Value Standard Error<br />
<strong>TDR</strong> measured Intercept -0.85292 1.49463E-14<br />
scour depth Slope 1.00054 3.72837E-16<br />
<strong>TDR</strong> measured scour versus<br />
physically measured scour<br />
95
Outline<br />
• Introduction<br />
• Literature review: scour monitoring practice<br />
and technologies<br />
• Validation <strong>of</strong> Time Domain Reflectometry <strong>for</strong><br />
scour monitoring<br />
• <strong>TDR</strong> scour measurements in various<br />
environments<br />
• Development <strong>of</strong> a field <strong>TDR</strong> scour sensor<br />
• Summary and conclusions, and future work<br />
96
Laboratory Observations and <strong>Algorithm</strong><br />
<strong>of</strong> Signal Interpretation<br />
• Normalized measured dielectric constant is linearly<br />
related to normalized sediment thickness<br />
• Normalized measured electric conductivity is linearly<br />
related to normalized sediment thickness<br />
• Salinity has minor effect on normalized measured<br />
dielectric constant.<br />
• Scour measurements based on dielectric constant is<br />
more stable.<br />
• Dielectric and electric mixing <strong>for</strong>mulas can be used to<br />
explain <strong>the</strong> observed linear relationship and to estimate<br />
scour depth from measured Ka and EC<br />
• Scour depth can also be estimated by indentifying <strong>the</strong><br />
reflection at water/sediment interface<br />
97
Laboratory Observations and <strong>Algorithm</strong><br />
<strong>of</strong> Signal Interpretation (cont.)<br />
• Empirical equation can be used to estimate scour depth<br />
• Dry density and electric conductivity <strong>of</strong> water can be<br />
determined from <strong>TDR</strong> signals.<br />
• Analyses algorithms can be implemented <strong>for</strong> automation.<br />
98
Evaluation <strong>of</strong> <strong>TDR</strong> under Various<br />
Conditions and Signal Interpretation<br />
• <strong>Algorithm</strong> works <strong>for</strong> different sediments.<br />
Dielectric scour estimation is more stable.<br />
• Insulated probe <strong>for</strong> highly conductive water<br />
• <strong>TDR</strong> works in air entrapped water, turbid water<br />
• Works in water with changing surface level<br />
Better submerged in water<br />
• Works in “dry scour”, but special interpretation<br />
algorithm is needed.<br />
• Scour measurements are real-time and<br />
accurate.<br />
99
Numerical Analysis <strong>of</strong> <strong>the</strong> Per<strong>for</strong>mance <strong>of</strong> <strong>the</strong><br />
Coated <strong>TDR</strong> Probe<br />
• Electric field <strong>of</strong> <strong>TDR</strong> probes can be analyzed by FEMLAB.<br />
• Effective measured dielectric constant by coated probes and<br />
its sampling area can be determined from FEMLAB results.<br />
• Coated probe can reduce sampling area and energy loss.<br />
Development <strong>of</strong> a New Field <strong>TDR</strong> Scour Sensor<br />
• The field scour sensor can accurately measure scour depth.<br />
• The presented calibration can be used to determine <strong>the</strong> real<br />
dielectric constant measured by <strong>the</strong> sensor.<br />
• The sampling area <strong>of</strong> <strong>the</strong> sensor is smaller <strong>the</strong> drilled hole.<br />
• Field calibration can completed at first installation by using<br />
sensor <strong>of</strong> different length.<br />
100
Future work<br />
•Continue to develop<br />
<strong>the</strong> field scour sensor<br />
• Calibrate existing<br />
scour prediction<br />
equations<br />
•Develop numerical<br />
simulation <strong>of</strong> bridge<br />
scour<br />
<strong>Bridge</strong> site<br />
Installation under Planning <strong>for</strong> <strong>Ohio</strong> State Route 122<br />
<strong>Bridge</strong> over Great Miami River<br />
101
Installation Planning<br />
• Site visit conducted<br />
• Permission obtained<br />
• Frequent communications with project partner GRL/PDI<br />
• Office visit and planning meeting between<br />
subcontractors three times<br />
• There was delay due to wea<strong>the</strong>r conditions and change<br />
<strong>of</strong> personnel<br />
• Field installation to be accomplished by Summer or Fall,<br />
2009<br />
• Extension <strong>of</strong> project deadline
Acknowledgement<br />
• <strong>Ohio</strong> Department <strong>of</strong> Transportation, Office <strong>of</strong> Research<br />
and Development<br />
Bill Krouse and Brandon Collett<br />
• GRL/PDI<br />
Frank Rausche, Garland Likins<br />
• Case School <strong>of</strong> Engineering<br />
• Nancy A. Longo<br />
• Jim Berilla<br />
103
Thanks!<br />
104
Connection to ano<strong>the</strong>r<br />
scour monitoring location<br />
(might or might not be <strong>for</strong><br />
<strong>the</strong> same pier)<br />
Schema <strong>of</strong> <strong>TDR</strong> Scour monitoring<br />
system (not to scale)<br />
Rugged housing <strong>for</strong> <strong>TDR</strong><br />
monitoring electronics<br />
(multiple scour probes can be<br />
monitored simultaneously)<br />
Connection to ano<strong>the</strong>r<br />
scour monitoring<br />
location<br />
Coaxial cable<br />
(hold to pier with<br />
fixtures to prevent<br />
motion)<br />
Scour probe made <strong>of</strong><br />
steel pipes (by<br />
driving or predrilled<br />
holes
Connection pipe with<br />
internal two way thread to<br />
connect steel pipe and<br />
conversion head<br />
Steel pipes (insulation<br />
coating might apply;<br />
length varies)<br />
Fig.7 a) (Left) Components <strong>of</strong> <strong>TDR</strong> scour probe; b) (Right) Schematic <strong>of</strong> <strong>TDR</strong> Scour Probe (Not to scale)<br />
Coaxial cable connect<br />
to <strong>TDR</strong> electronics<br />
Water level<br />
Sediment level