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· University of Minnesota St. Anthony Falls Hydraulic Laboratory Project Report No. 270 HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS by Charles C. S. Song, Qizhong Guo and Yifan Zheng Prepared for METROPOLITAN SANITARY DISTRICT OF GREATER CHICAGO Chicago, Illinois 60611 March 1988

HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

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Page 1: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

· University of Minnesota St. Anthony Falls Hydraulic Laboratory

Project Report No. 270

HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

by

Charles C. S. Song,

Qizhong Guo

and

Yifan Zheng

Prepared for

METROPOLITAN SANITARY DISTRICT OF GREATER CHICAGO Chicago, Illinois 60611

March 1988

Page 2: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

The University of Minnesota is committed to the policy that all persons shall have equal access to its programs, facilities, and employment without regard to race, creed, color, sex, national origin, or handicap.

Page 3: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

[,

TABLE OF CONTENTS

Page No.

List of Figures ..................................... II •• , •• !I •• II' •• iii

I.. 1:NTRODUCTION .............. II •• \I , II ..................... , ...... , • 1

II. THE MIX8D TRANSIENT FLOW MODEL ••••••••••••••••••••••••• 2

Ill. CALIBRATION OF MAINSTREAM MODEL ••••••••••••.••••••••••• 4

IV.

V.

GENERAL TRANSIENT CHARACTERISTICS • ...... , , .. II ........................ .. 6

A. The Filling Process •••••••••••••••••••••••••••••••• 6

1. Mainstream System--existing conditions ••••••••• 6 2. Mainstream System--with reservoir at

downs tream end .... til " .. , ... , .... , ........ II ................... ..

3. Calum.et System .................................................... . 4. Storage Volume--stage relationship •••••••••••••

Some Transient Problems ••••••••••••••••••••••••••••

1. The air blow-off phenomenon •••••••••••••••••••• 2. The Geyser process •••• , •••• , •••••••••••• " ••••• 3. The Safety Criterion •••• " •••••••••••••••••••••

7 7 8

9

9 10 12

SOLUTION ALTERNATIVES FOR MAINSTREAM SYSTEM 16

A. Short Term Solutions ................................................. 1. 2. 3.

Storm A Storm B Storm C

................. , ..... , .. , ............ .

............................ II ... " .................. ., ..... ..

........................... , ............................ ..

16

16 17 17

B. Long Term Solutions ., ••••••••••••••••••• ,.......... 17

1. Storm A with Gate Control - reservoir initially elUp t y ....................... ,..................... J 7

2. Storm A with Gate Control - res~rvoir partially full .................. ,........................ 18

3. Storms Band C 'i7ith Gate Control - reservoir

4. 5.

i n1 t ia11y em.pty .................................. . Storm C with Surge Structure - modified OS-53 Storm C, trade-off between surge structure

.I,e 18

and gate control.............................. 19

i

Page 4: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

VI. SOLUTION ALTERNATIVES FOR CALUMET SYSTEM

VII.

VIII.

IX.

A.

B.

Short Term Solutions

1-2.

September 26, 1986 storm ••••••••••••••••••••••. Maximum design storm •••••••••••••••.••.•••.•••.

Long-Term Solutions

THE DES PLAINES SYSTEM ........................................................... ..

A. B. C.

South System ............................................................................ .. South-Middle Sys tern .............................................................. .. Complete System ••••••••••••••••••••••••••••••••••••

SOLUTION ALTERNATIVES FOR 13A SYSTEM •••••••••••••••••••

A. B. C.

Existing Estimated Peak Inf1o~l Condition ••••••••••• Future Planned Peak Inflow Condition •••••••••••••••• Dropshaft Design Capacity Inflow Condition •••••••••

CONCLUSIONS AND RECOMMENDATIONS

Figures 1 through 71

ii

Page No.

20

20 20

2 I

22

22 22 23

24

24 24 25

26

Page 5: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

, ..

Figure No.

1

2

3

4

5

6

7

8

9

10

11

12

13

14

,rf 15

16

17

LIST OF FIGURES

Mainstream system configuration for modeling purposes.

Comparison of measured and calculated water level at the downstream end, October 3, 1986, storm.

Comparison of measured and calculated water level at downstream end, September 26, 1986, storm.

Stationing of mainstream system excluding all branch tunnels.

Instantaneous hydraulic gradelines showing pressurization surge, October 3, 1986, storm.

Instantaneous hydraulic grade lines showing reflected surge, October 3, 1986, storm.

Instantaneous hydraulic grade lines after the second reflection, October 3, 1986, storm.

Water depth at three selected stations with reservoir, no inflow restriction, October 3, 1986, st.orm.

Total inflow rate, maximum storm partially controlled.

Instantaneous hydraulic gradelines, reservoir initially empty.

Existing Calumet System configuration for modeling purposes.

Future Calumet System configuration for modeling purpose.

Correlation between storage volume and depth at downstream end,Mainstream System.

Correlation between storage volume and depth at downstream end, Calumet System.

Qualitative comparison ~t water surface profiles between static condition and dynamic condition.

Comparison of actual storage and static storage-Uainstream System.:

Comparison of actual storage and estimated storage based on depth at two points - t,minstream System.

iii

Page 6: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

...

Figure No.

18 Comparison of actual storage and static storage - Calumet System.

19

20

U

22

23

24

25

26

27

28

29

30

31

32

13

14

15

36

Comparison of actual storage and estimated storage based on depth at two points - Calumet System.

A sketch of Dropshaft-Drift Tube System for geyser analysis.

Time variation of water depth in dropshaft due to slow rise in tunnel pressure without resonance.

Time variation of water depth in dropshaft due to rapid rise in tunnel pressure without resonance.

Time variation of water depth in dropshaft due to slow rise in tunnel pressure with resonance.

Mainstream system excluding the 13A, Nashville and Lawrence Avenue branch tunnels.

Total inflow hydrograph for short term solution, Storm A.

Time variation of water depth at upstream and downstream ends, stort-term solution, Storm A.

Time variation of water depth at DS-53 and the upstream end, short-term solution, Storm A.

Total inflow hydrograph for short-term solution, Storm B.

Time variation of water depth at upstream and downstream ends, short-term solution, Storm B.

Total inflow hydrograph for short-term solution, Storm C.

Time variation of water depth at upstream and downstream ends, short-term solution, Storm C.

Time variation of water depth at DS-53 and upstream end, short-term solution, 8torm C.

Total inflow hydrograph, long-term solution, Storm A, reservoir initially empty •

Time variation of water depth at three stations, long-term solution, Storm A, reservoir initially empty.

Total inflow hydrograph, long-term solution, Storm A, reservoir initially partially full.

Time variation of water depth at three key stations, long­term solution, Storm A, reservoir initially partially full.

iv

Page 7: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

\:!

\~

Figure No.

37 Total inflow hydrograph, long-term solution, Storm Band C, Reservoir initially empty.

38 Time variation of water depth at three key stations, 10ng­term solution, Storm Band C, reservoir initially empty.

39 Instantaneous hydraulic gradelines, long-term solution, Storm Band C, reservoir initially empty.

40 Time variation of water depth at three key stations; 10ng­term structural solution, Storm C, reservoir initially ~npty.

41 Time variation of water depth at three key stations, 10ng­term solution based on inflow control and surge structure, Storm C, reservoir initially empty.

42 Total inflow hydrograph for Calumet System due to September 26, 1986, storm.

43 Time variation of water depth at three key stations.

44 Total overflo", hydrograph.

45 Total inflow hydrograph, short-term solution, maximum design flow.

46 Time variation of water depth and five key stations, short­term solution, maximum design flow.

47 Total inflow hydrograph, maximum design flow A.

48 Time variation of water depth at six key stations, maximum design flow.

49 Time variation of water depth at reservoir, maximum design flow.

50 Des Plaines South System configuration for modeling purpose.

51 Des Plaines South-Middle System configuration for modeling purpose.

52 Des Plaines complete system configuration for modeling purpose.

53 Total controlled inflow hydrograph, South Des Plaines System.

54 Time variation of water depth, South Des Plaines System.

55 Instantaneous hydraulic gradelines, South Des Plaines System.

v

Page 8: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

Figure No.

56 Total inflow hydrograph - South-Middle System.

57 Time variation of water depth at the ends of the main tunnel, South-Middle System.

58 Time variation of water depth in Riverside Branch, South-Middle System.

59 Instantaneous hydraulic guidelines.

60 Total inflow hydrograph - Complete Des Plaines System.

61 Time variation of water depth at upstream ends of branch tunnels - complete Des Plaines System.

62 Instantaneous hydraulic gradelines.

63 13A tunnel model system configuration.

64 Time variation of water surface elevation at downstream end, existing peak flow.

65 Time variation of water surface elevation at DS.6l, existing peak flow.

66 Overflow hydrograph from L3A tunnel, existing peak flow.

67 Time variation of water surface elevation at downstream end, future peak flow.

68 Time variation of water surface elevation at DS.61, future peak flow.

69 Overflow hydrograph from 13A tunnel, future peak flow.

70 Time variation of water surface elevation at downstream end, dropshaft design capacity inflow.

71 Time variation of water surface elevation at DS.6l, dropshaft design capacity inflow.

72 Overflow hydrograph from l3A tunnel, dropshaft design capacity inflow.

73 Conditions for dropshaft-drift tube resonance.

vi

Page 9: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

\.1

I. INTRODUCTION

Under the agreement of November 1, 1986, between the Metropolitan Sanitary District of Greater Chicago and the University of Minnesota, the St. Anthony Falls Hydraulic Laboratory of the University conducted mathematical modeling of the recently completed portions of the Tunnel and Reservoir Plan (TARP), both the Mainstream System and the Calumet System of Greater Chicago, for the purpose of establishing optimum operating procedures and additional structures to control hydraulic transient problems. The scope of the work was later extended to include the Ues Plaines System and the 13A tunnel when operated independently of the Mainstream System.

The fully dynamic transient mixed flow mathematical model (MXTRANS) developed at the University of Minnesota was used for this study. In order to enhance the confidence level of the modeling results, attempts were first made to reproduce the transient phenomena observed in the Mainstream System during the storm events of October 3, 1986, September 26, 1986, and October 18, 1985. The work is described in Section III, Calibration of Mainstream Model.

After studying the detailed mechanisms of the air blow-off and geyser process in the Mainstream System, a set of safety criteria were established. These criteria were later used to determine the effectivenss of various solution alternatives. General transient characteristics and the safety criteria are described in Section IV.

Various short-term and long-term solution alternatives for all four systems were studied, and the results described in Sections V, VI, VII, and VIII. Short-term solutions are based mainly on inflow controls using the structures that exist at the present time along with proposed orifice controls. Because only limited means are available, the solutions are mostly effective to storms that are less than the maximum design storm. Long-term solutions are based on the condition after the planned storage reservoirs at the downstream ends of the Mainstream System and Calumet System have been completed. These solutions may include inflow control, additional construction of surge structures, and some structural modifica­tion.

This report summarizes the work completed under this contract.

Page 10: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

II. THE MIXED TRANSIENT FLOW MODEL

The flow to be simulated is very unsteady and contains highly dynamic phenomena such as pressurization surge and resonance. The model used must be able to simultaneously calculate unsteady open channel flows and unsteady pressurized flow including the abrupt change that occurs at the shock or the surge front.

The well-known St. Venant equations

(1)

~ + ~ + av + g(s - s ) g ax a t v ax f 0 o (2)

are used to represent the unsteady open channel flow. In the above equations, y is the flow depth, v is the flow velocity, c is the gravity wave speed, So is the channel slope, Sf is the energy slope, and g is the acceleration due to gravity.

The corresponding equations for unsteady pressurized flow are:

!l. + av + av + ( ) 0 g ax at v ax g Sf - So =

in which a is the pressure wave speed while y takes the meaning of piezometric head measured from the tunnel invert.

(3)

(4)

The systems of equations (1) ~ (4) are solved by the method of characteristics. "Because the transition from the open channel flow condition to pressurized flow condition must be abrupt, as in the case of a hydraulic jump, the special shock boundary conditions must be applied. It was shown by Songl , for a pressurization surge or a positive surge, where three characteristic equations plus two shock boundary conditions can be used to calculate five unk~owns at the interface. These five unknowns are

ICharles C. S. Song, "Modeling of Mixed-Transient Flow," Proceedings, Vol. 1, SECTAM XII, Auburn University, May 10-11, 1984.

2

Page 11: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

v and y on both sides of the interface and the speed of the interface movement. The model can also simulate the negative surge which occurs during the depressurization process.

A number of other boundary conditions representing junctions~ dropshafts, reservoirs, and other accessories are also provided in the model. Inflow hydrographs, outflow conditions, and other active or passive flow control methods can also be included in the input data file. Velocity, depth, discharge~ and other variables at any location and any time may be specified as outputs.

In principle, if all data are accurate, the model should require no calibration. In practice, however, there may be some uncertainties in the input data that some adjustment to the original input data may be necessary. In the case of the TARP system, the greatest uncertainty exists in the inflow data.

3

Page 12: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

Ill. CALInRATlON OF t1A[NSTREAM MODEL

For the mathematical modeling purpose, the simplified Mainstream System configuration, ;:is shown in Fig. 1, is Ilsed. The system consists of a main tunnel and six branch tunnels. Numbers shmm in Fig. 1 are the station numbers used in the model for the purpose of defining different spgments of the system. Each junction is represented by three stations for Identification of three connecting segments. The entire system is divided Into 242 finite segments of 1000 feet each. Some of the dropshafts located close tl) each other are combined so that a total of 82 shafts and inflow pOint:; are explicitly represented in the model. Each shaft is assumed to Ill' dI rectly attached to the tunnel, and the detailed geometry including the approach conduit is ignored.

Three storm events of October 3, 1986, September 26, 1986, and October 18, 1985, were used for calibration purposes. According to field personnel, the field data of the October 3, 1986, storm are most complete and reliable. There are some uncertainties on the actual gate settings during the October 18, 1985, storm. The September 26, 1986, storm was relatively small, and the transient was mild. Therefore, the October 3, lQ86, data are the most useful datil for calibration purposes. Inflow hydrographs for each storm were furnished by Mr. Clint J. Keifer, who generated the hydrogrilph with another model using the measured rainfall datil as input!J. The Mainstream System Model, using the synthetic hydrographs and the field records of the actual gate operating procedure as I npuUl, calculates the time history of discharge and head at all stations. TII~ M~tropolitan SanitRry District ~lso furnished the data on the head mt':ISllred at the down8tream end for each stor,u. The measured and the eOlilpllted heads at the downstream end of the system were compared and used aB the primary means of judging th\~ accuracy of the model. It turned out that the model needed practically no adjustment.

The calculated water level at the downstream end of the Mainstream System due to the October 3, 1986, storm is compared with the measured vallWs in Fig. 2. Similar comparisons for the September 26, 1986, storm are shown in Fig. 3. ijecause ther,~ are too ,uany uncertainties on the gate operating conditions, no meaningful comparison for the October 18, 1985, storm Is possible. There are good general agreements between the results of mathematical modeling and the measurements.

The two most important factorg that affect the results of simulation are the inflow hydrographs and the amount of water initially stored in the syst(~m. Since there is no actual i.nflow data available, the synthetic 1 nf LIHI hydrographs were accepted a'l being accurate for calibration purpose!J. The initial storage in the system was estimated from the mpastll"ed water level at the downstr.eam end, 'lssuming that the water was stat [onary and level. In reality, if the water is flowing, the water Hllr(ace lnay not be level. Fortunately, the assumption is validated for the ~1a Lns!: ream System because the init ial storag(~s are the same for both sta-

4

Page 13: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

tionary and flowing water in the early filling process. The error in the initial storage volume may significantly affect the timing of the sharp rises in water level, each signaling the complete pressurization of the main tunnel or a branch tunnel.

5

Page 14: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

IV. GENERAL TRANSIENT CHARACTERISTICS

A. The Filling Process

1. Mainstream System--existing condition

A series of computer simulations were carried out based on the system configuration as shown in Fig. 1, representing the existing condition of the Mainstream System. The results along the main tunnel as shown in Fig. 4 are studied in detail. Oepending on the amount of water initially stored in the tunnel, a downstream portion of the tunnel is pressurized at the beginning of the inflow. As the tunnel continues to fill and the pressurized portion expands, surge develops at the interface between the pressurized zone and the free surface zone. The magnitude of the surge (jump in head) increases as the inflow rate increases. This situation is illustrated by the three instantaneous hydraulic gradelines shown in Fig. 5. Note that the station number shown in this figure refers to that of Fig. 4.

Water is flowing in the opposite direction across the surge front. Water is flowing in the downstream direction ahead of the surge but flowing in the upstream direction behind the surge. The water surface is far from level, and water is rushing towards the upstream end. When the surge front first arrives at the upstream end, at 157 min. as shown in Fig. 6, a large amount of backflow causes water to be squeezed into the dropshaft, raising the water level very rapidly. The smaller the diameter of the shaft, the higher the water level will rise due to this first surge. This high head thus generated at the upstream end now travels downstream as a reflected surge, causing head in the tunnel to surge up once again. At about 159 min., a somewhat weaker surge develops at the downstream end and starts to move upstream. When the two surges, one from upstream and one from downstream, collide at about 163 min., head near DS 52 and DS 53 rises very rapidly. When the reflected surge arrives at the downstream end at about 175 min., it is reflected again and starts to move upstream. Instantaneous hydraulic gradelines after this time are shown in Fig. 7. Clearly, the water in the tunnel rocks as the tunnel is being filled to the ground level.

When the first pressurization surge arrives at a junction, it may break up into two surges; one continues to move along the main tunnel and the other moves along the branch tunnel. Due to the same mechanism just described for the main tunnel, the upstream end of the branch channel may also reflect the surge. Thus, each branch also contributes to surging and rocking of certain characteristic periods. Since the South Fork branch usually fills first, any station downstream experiences first pressure peak due to the filling of this branch. This phenomenon was quite prominent during the October 18, 1985, storm which started when storage was relatively small.

6

Page 15: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

2. Mainstream System--with reservoir at downstream end

A reservoir having the total storage capacity of 32,000 acre-feet and the depth of 196 feet is assumed to exist at the downstream end of the system as shown in Fig. 1. In this case the detailed filling process will depend on the storm size and the amount of water initially stored in the reservoir. If the reservoir water level is initially at or near the crown of the tunnel and the October 3, 1986, storm is the input, then the tunnel will fill from the downstream end and proceed upstream. The pressurization surge intensity will increase in the upstream direction creating signifi­cant transient conditions. As shown in Fig. 8, surge conditions still exist in midstream and upstream portions of the tunnel. Insufficient conveyance capacity caused by the backwater effect is responsible for the strong surge.

When the reservoir is initially empty and inflow is larger, then pressurization may initiate somewhere in the midstream of the tunnel due to inadequate conveyance. A simulation run was made with a partially controlled maximum storm hydrograph as shown in Fig. 9. As indicated by the instantaneous hydraulic gradelines plotted in Fig. 10, two pressurization surges, one moving upstream and the other moving downstream, are generated. The surge that moves upstream will collide with the upstream end and cause a rapid head increase at t=110 minutes. The downstream moving surge behaves quite differently because of the reservoir. When the positive surge first arrives at the downstream end, it is immediately eliminated, and the head is reduced to that of the reservoir. At this time the reservoir reflects a negative surge which will travel upstream. This negative surge cannot travel very far upstream before its direction is reversed and becomes a positive surge again because of the large pressure gradient. The reservoir will eliminate the second positive surge and reflect another negative surge. The process repeats itself until the reservoir water level reaches the crown of the tunneL The pressurization is thus completed.

3. Calumet System

The simplified configuration for modeling purposes of the existing calumet system is shown in Fig. 11. The system consists of the main tunnel and three branches. The entire system is divided into 219 finite elements of 500 ft each. Because the proposed Thornton reservoir is approximately 22,500 ft away from the main tunnel, the model configuration for future conditions is changed as shown in Fig. 12.

The overall slope of the main tunnel of the Calumet System is many times greater than the slope of the Mainstream System. Increased conveyance due to increased slope make the Calumet System unlikely to pressurize from the midsection of the tunnel. Pressurization invariably initiates at the downstream end, with or without the proposed reservoir.

7

Page 16: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

4. Storage Volume--stage relationship

Inflow control is a possible means of preventing surge related problems. Since the surge intensity is strongly related to the total Lnflow rate during the final stage of the filling process, it is necessary to limit the inflow rate as the tunnel approaches the full condition. The real time Information on the amount of water stored in the system Ls needed to operate the inflow control gates. At the present time the volume of water stored is calculated from the water level data taken at the downstream end of the Mainstream System and by assuming that the water surface is level over the entire system, i.e. hydrostatic condition.

Under a dynamic condition the water surface profile in an open channel flow portion is not level and actual volume may be quite different from that estimated by the depth data at the downstream end alone. The correlations between the storage volume and the water depth at the downstream end under three different conditions for the Mainstream System are shown in Fig. 13. Similar plots for the Calumet System are shown in Fig. 14. In each of these figures, the solid line represents the case when the volume was calculated by assuming static conditions, the broken line represents the storage volume calculated by the model under the dynamic condition of October 3, 1986, storm, and the dashed line represents the dynamic condition of the September 26, 1986, storm.

According to Fig. 13, static approach for the Mainstream System may overpredict the storage by as much as 10 percent while, according to Fig. 14, static approach for the calumet system may underpredict the storage by as much as 65 percent. The different trend shown for the two systems may be explained by the difference in the slope of the tunnels. Qualitative sketches of water surface profiles under the static condition and under a dynamic condition for the two systems are shown in Fig. 15. For the Mainstream System which has a very small slope, the static-free surface extends very far upstream resulting in overprediction. In contrast, for the Calumet System which has a large slope, much of the upstream portion may contain no water under static conditions, but will have flowing water under a dynamic condition. The differences between static prediction and the actual dynamic storage are likely to be greater for longer storms and vice versa.

Real time depth data at more than one station along the main tunnel are clearly required to improve the storage estimation. Numerical experimentations were carried out to determine the method of improving the storage volume calculation. It was found that depth data at two stations, one at the downstream end and one near the upstream end, would be sufficient to make very accurate storage volume calculations. The basic form of the equation needed is given as follows.

(5)

in which

V total estimated storage

8

Page 17: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

."

" Vo(Y1) = static storage volume

V1 (Y1' Y2) = correction due to dynamic effect

The correction term tn Eq. 5 for the Mainstream System is given by

The corresponding equations for the Calumet System are:

(8)

" V1 (Y1' Y2) = 70,000 D2"l100 + Y2 - y1 1 , if Y2 > D2 (9)

In the above equations, Y1 is the measured water depth or piezometric head at the downstream end of each system, and Y2 is the measured water depth or piezometric head at the Roosevelt Road construction shaft for the ~1ainstream System and at St. 3+90 for the Calumet System. D2 is the diameter of the tunnel at the location where Y2 is being measured.

To visualize the improvement on tlte storage volume calculation due to the inclusion of the correction term V1(Y1, Y2) in Eq. 5, Figs. 16, 17, 18, and 19 are preparKd. Figure 16 shows the correlation between the static storage value Vo (Y1) and the actual value V calculated by the dynamic model for two storm conditions for the Mainstream System, without downstream reservoir present. Figure 16 shows the correlation between the corrected storage volume V given by Eq. 5 and the actual volume V. The deviations of these curves from the straight diagonal l:i.ne represent the error of estimation. Similar curves for the Calumet Syskem are shown in Figs. 18 and 19. Considerable ilnprovement of V over Vo is quite ev'i­dent. It should be noted that Eqs. 5 N 9 are applicable to any, storm but only to the system with no reservoir. New equations have to be derived after the reservoirs are constructed.

B. Some Transient Problems

1. The air blow-off phenomenon

When a pressurization surge reaches an upstream end during the filling process, water will rise rapidly in the dropshafts near the upstream end. Water levels in other dropshafts will also rise as the surge reflected by the upstream end travels downstream.

9

Page 18: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

The rising water will then push air inside the dropshaft upward, exerting pressure on the cover. The magnitude of the air pressure depends on the speed of the rising water level and the type of cover grating. Extremely large pressure can be generated if the cover is air tight. Since all covers 1n the Mainstream System are either fully grated with area ratios of 0.54 or half grated with area ratio of 0.27, it i.s unlikely that air pressure alone can cause damaging effects.

Assuming steady amounts of air flowing through the cover grating, the force acting on the cover due to the air flow may be calculated by

(10)

where CD == [1 + 0.707 1(1-f) ]2/f2 (11)

f area ratio.

Pa density of air

V = average air speed in dropshaft a

A == total cover area

According to Eqs. 10 and 11, air flow velocity required to lift unsecured cover is 131 fps for the fully grated case and 31 fps for the half grated case. The three storms used for calibration did not generate large enough air speed to uplift the cover.

2. The Geyser process

When a water column in a dropshaft rises very slowly to the levels of the connecting pipe, the water may back into the connecting pipe. But if the water column rises too rapidly, it may overshoot the connecting pipe and impact the cover. The impact force is given by

F == pa V(1-f)A (12)

where p = density of water, and a = speed of pressure wave. According to this equation, the velocity of the water column needed to uplift the half grated and unsecured cover is only 0.1 fps.

If Eq. 12 is not a relevant estimation of the lift force, then the steady flow velocity needed to lift the cover based on Eqs. 10 and 11, with appropriate change in variables from those of air to water, are 4.6 fps for the fully grated cover and 1.1 fps for the half grated cover. Clearly,

10

Page 19: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

only a very small water velocity is needed to lift the cover once water level exceeds the cover level.

An independent mathematical model of a Dropshaft-Drift Tube System as sketched in Fig. 20 was constructed and used to quantify the geyser problem. This model assumes that the surge in the main tunnel imposes a sudden rise in pressure at the downstream end of the drift tube. The surge pressure transmitting through the drift tube acts on the water column in the dropshaft and causes it to move.

The motion of water column in the dropshaft can be described by the following continuity and momentum equations.

(13)

2 P A H d H = - P g H A - T A + Pd A.

s dt2 sop s (14)

where As = cross-sectional area of dropshaft

Ad cross-sectional area of drift tube

Ap wetted area of dropshaft

H water column height

Pd pressure at the bottom of dropshaft

Vd velocity at drift tube entrance

TO shear stress on wetted area of dropshaft

Qi inflow rate from connecting pipe

The drift tube of length L is divided into a number of finite elements. The flow in each of the elements is equivalent to a finite difference model of the drift tube with its upstream condition described by Eqs. 13 and 14. The time dependent pressure calculated by the }iainstream System model at the corresponding location is used as the downstream end boundary condition of the drift tube-dropshaft model.

Figure 21 shows a typical time variation of water depth in a dropshaft due to a fairly slow rise in the tunnel pressure. It shows that a linear increase in the tunnel pressure results in an oscillatory increase in the water depth in the dropshaft. Figure 22 shows a similar result when the tunnel pressure rises more rapidly due to surge. All other conditions being equal, more rapid rise in tunnel pressure produces larger amplitude oscillation of the water depth. Clearly, large intensity surge in the tunnel will cause a geyser due to oscillation, even if the final equilibrium condition may indicate no overflow.

Figure 23 shows a special case when there is a resonance condition due to matching of the natural frequency of the water column in the

II

Page 20: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

dropshaft and the natural frequency of the drift tube. Even with a fairly slow rIse in the tunnel pressure, the water column oscillation may grow large enough to cause a geyser.

The natural frequency of a water column of height 8m is given by

(15)

The natural frequency of a drift tube of length L and pressure wave speed a is

Clearly, the resonance condition

lJL L 1T 1i1 a

m 1

(16)

(17)

must be avoided. According to Eq. 17, the resonance condition is deter­mined by three variables Hm , L, and a. Out of these variables 8m and L are readily determined from the physical dimensions. On the other hand the wave speed a is highly dependent on the air content of the flow and dif­ficult to determine. Figure 73 shows the relationship between the air con­tent and the wave speed length of drift tunnel at resonance condition.

3. The Safety Criterion

The analysis of the previous section clearly indicates that the geyser phenomenon depends on the surge intensity as well as other factors. Since the Mainstream and other system models do not include the detailed dropshaft-drift tube configuration, a simplified and general safety criterion is needed to determine the effectiveness of any surge mitigation method. Let,

and

8 = H + h m (18)

(19)

where Hand Hm are the instantaneous and the mean values of the water depth in the dropshaft and Pd is the instantaneous pressure at the base of the dropshaft. In this way, hand yare the fluctuating components of the water depth and the pressure head, respectively. By substituting Eqs. 18 and 19 into Eqs. 13 and 14 and linearizing, the following equation is obtained:

12

Page 21: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

:.

(20)

where

f dh ~ dt = damping factor

s

f Darcy-Weisbach friction coefficient.

Assuming an oscillatory forcing function, we may write

y = Yo sin wt (21)

(22)

This assumption is justified by the results of the mathematical model described in the last section indicating that the drift tube modifies any pressure change in the tunnel to an oscillatory force of frequency fd'

Equation 20 is the differential equation of a typical vibrating mass-spring system with a variable damping factor. If we ignore the variability of ~ and take it to be a constant, then it is possible to write the general solution of Eq. 20 in a closed form. Assuming that the exiting head is a harmonic function

y = Yo sinwt (23)

the general solution of Eq. 20 is

h -~ t cos ~k2 _ ~2 t + C2 F-1 = e (C si k -t; t) 1

+ B sin (wt - ~) (24)

where

gy _ w2 )2 + 4~2w2]-1/2 B = H 0 [(k2 (25)

m

13

Page 22: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

~ = tan 2z.;1JJ

Ti,e constants of integration Cl and C2 may be determined by the initial conditions, I.e.

h h o

and at t o

(26)

(27)

Two special cases are important to the gysering problem. These are described as follows:

1) Free oscillations

Assuming that the geometry of the drops haft and the drift tunnel is such that k * IJJ and resonance does not exist, the water column in the dropshaft will undergo a free oscillation when excited by a surge in the main tunnel. Its motion is described by the first term on the right-hand side of Eq. 24, and the maximum amplitude of oscillation is given by

h max C .... /Hm I1g

U m

(28)

where Um is the speed of head rise in the main tunnel and Cl is a constant that must be determined by calibration. ~eferring to Fig. 20, the oscillatory water column will touch the cover if

H + h ) H m max s

where Hs is the cover elevation. By comparing Eqs. 28 and 29, it is possible to derive the following safety equation

H - H s m ~ m U

g m

If Nf is greater than one, then a free oscillation of the water column caused by the surge will produce a geyser.

2) Resonance oscillation

(29)

(30)

If the natural frequencies of the drops haft k matches the frequency of the forcing function IJJ (which is also equal to the natural frequency of the drift tunnel) then the maximum amplitude of oscillation is deter­mined by the second term on the right side of Eq. 24. It is given by

14

Page 23: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

h '" max

By comparing this equation with Eq. 29 the following safety equation is obtained.

(31)

(32)

where C2 is a constant to be determined by calibration. Using the event of October 3, 1986, it was determined that C1 = 4.6 and C2 = 40.

15

Page 24: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

V. SOLUTION ALTERNATIVES FOR MAINSTREAM SYSTEM

~fEective solution alternatives depend very much on the storm size to be conside~ed. In order to assist the decision making process, the following three sto~ms are used in the analysis.

Storm A: The largest of the three calibration stonns, October 18, 1985 storm, is used as a standard sto~m.

Sto~m B: A storm that causes maximum design inflow for 3.5 hours.

Sto~m c: A storm that causes maximum design inflow for indefinite periods of time.

For the analysis that follows, the 13A, Nashville and Lawrence Avenue 13ranch tunnels are assumed to be closed, and the Mainstream System excluding these three branches is shown in Fig. 24.

The safety criterion given in Section IV-B is used to determine the effectiveness of any surge mitigation method. Nf is applied at upstream ends, and Nr is applied at US-53.

A. Short Term Solutions

Presently there are flow control gates located at DS.3, 8, 9, 10, 11, 12,13,14, IS, 17, 19, 20, 21, 25, 26, 27, 28, 29, 30, 35, 38, 39, 40, 41, 45, 47, 49, 50, 51, 52, 53, 54, 55, 57, 58, 60, 61, 61A, 64, 66 67R, 70 73, 75, 76, 79, 80, 82, 83, 84, 85, 86, 88, 90, 91, 97, 100, 104, 106, 107, and 109. 92% of the potential inflow can be eliminated when these gates are all closed. In addition fixed orifices are being planned for dropshaft Nos. 16, 22, 42, 43, 71, 81, 87, 89, 93, 94, 95, 96, 98, 99, and 105 to limit inflow to a maximum of 1/3, the maximum inflow rate possible at each site.

1. Storm A

It is possible to mitigate the surge problem by limiting inflow using the existing gates. The gates at dropshafts Nos. 27, 28, and 29 (Racine Ave. pumping station) should start to close when the system is 50 percent full. All other control gates are closed at 70 percent full. All gates are assumed to require 10 minutes to complete closing.

The total inflow hydrograph for this operation is plotted in Fig. 25. The variation of water depth at the upstream end and the downstream end are plotted in Fig. 26. The water depth variation at St. 93 (DS-53) is compared with that of the upstream end in Fig. 27. These figures clearly show the existence of surges as the system is being filled.

16

Page 25: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

"

The computed surge oscillation numbers are Nf indicating only DS-53 is at a marginal condition.

2. Storm B

0.88 and N r

1.0

The modeling results indicate that the existing control gates are not sufficient to prevent geysering. It requires two additional control gates at DS-l and DS-114. It also requires all the planned fixed orifices to be in place.

The gates at dropshafts Nos. 27, 28, and 29 should start to close when the tunnel is 30 percent full. All other control gates should be closed at 40 percent full. The gate closing time is 10 minutes.

Total inflow hydrograph for this case is plotted in Fig. 28. The variation of water depth with time at the downstream end and upstream end are plotted in Fig. 29. The surge oscillation numbers are Nf = 0.80 and N := 1.0.

r

3. Storm C

Fixed orifices must be provided for all ungated. dropshafts or, alternatively, some additional controllable gates are needed. The results of simulation with existing control gates plus fixed orifices at all ungated dropshafts are presented here.

The gate operating procedure is identical to that of Storm B.

Total inflow hydrograph for this case is shown in Fig. 30. Because of the increased number of fixed orifices, the restricted inflow after gates closure for this case is smaller than that of Storm B. Reduced inflow rate compensates for increase duration. Time variation of water depth at upstream and downstream ends are shown in Fig. 31. A similar plot for DS-53 is shown in Fig. 32. The surge oscillation factors are Nf = 0.32 and N == 1.0.

r

It should be noted that for all three storms analyzed the critical condition is determined by the resonance condition at dropshaft No. 53.

B. Long Term Solutions

A 32,000 acre-feet reservoir using the }kCook Quarry is planned for the purpose of increasing storage capacity and reducing flooding problems. Because of the conveyance limitation as described previously, however, the surge and geyser problems cannot be completely eliminated without further controls.

1. Storm A with Gate Control - reservoir initially empty

The filling process is somewhat different for different initial storage conditions. ~~en the reservoir is initially empty, then the tunnel is at its full conveyance capacity and the reservoir can contribute to surge reduction.

17

Page 26: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

In this case only the gates at dropshaft Nos. 27, 28, and 29 need to be closed when the tunnel, excluding the reservoir, is 75 percent full. The total inflow hydrograph for this case is shown in Fig. 33. The time variation of water depths at the upstream end, downstream end, and DS-53 are shown in Fig. 34. This figure indicates that the tunnel at both ends remains open (not pressurized) for the entire duration of the storm. Due to the conveyance limitation, however, the midp'ortion of the tunnel is pressurized and the resonance condition at DS-53 dictates the safety of the system. The surge oscillation numbers are Nf • 0 and Nr = 0.65.

2. Storm A with Gate Control - reservoir partially full

The condition considered here is the case when the water level in the reservoir is just at the crown of the tunnel at the downstream end. Reductions in conveyance and the remaining storage capacity in the tunnel causes more severe surge problems in the middle portion of the system.

To avoid the geyser problem at DS-53, it is necessary to start closing all gates when the tunnel is 80 percent full. Figure 35 shows the total' inflow hydrograph, and Fig. 36 shows the corresponding time variations of water depths at three stations. The surge oscillation numbers are Nf • 0 and N ~ 0.71.

r

3. Storms Band C with Gate Control - reservoir initially empty

Gate closure should start when the tunnel is 50 percent full to cut off 80 percent of flow coming in from the gated dropshaft. This can be accomplished by completely closing the gates responsible for 80 percent of gated inflow.

The total inflow rate is shown in Fig. 37. The time variation of water depths at three stations are shown in Fig. 38. Instantaneous hydraulic gradelines showing the movement of surges are plotted in Fig. 39. This figures clearly show that the problem is in the midsection of the tunnel. The oscillation numbers are Nf ~ 0 and Nr ~ 1.0.

4. Storm C with Surge Structure - modified US-53

Previous analysis has clearly indicated that the resonance instability of DS-53 is always most critical after the construction of the reservoir. Therefore, the first priority of structural modification is the removal of the r~sonance condition at DS-53. After this is done, it is necessary to enlarge the shaft diameter at the Ilpstream end to 100 feet.

With the structural modification described above, the total Storm C hydrographs are allowed to enter the system. Time variation of water depth at three key locations are shown in Fig. 40. The critical location now shifts to the upstream end (Station 1 in Fig. 40). The relevant oscillation number is Nf = 1.0 in this case.

18

Page 27: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

5. Storm C, trade-off between surge structure and gate control

The relative gat ion. is equal

purpose of this run is to provide additional information on the effectiveness of surge structure and inflow control in surge miti­It is assumed that the diameter of the shaft at the upstream end to 70 feet and the resonant condition has been removed.

In this case the inflow from the gated dropshafts should be reduced 50 percent when the tunnel is 50 percent full. The corresponding total inflow hydrograph is shown in Fig. 9 and the time variation of water depth at three key stations are shown in Fig. 41. It is interesting to note that there are positive and negative surges near the reservoir that alternately move downstream and upstream.

19

Page 28: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

VI. SOLUTION ALTERNATIVES FOR CALUMET SYSTEM

The Calumet system is presently accepting only slnall amounts of inflow and has not experienced any surge related problem. However,the potential for a geyser problem cannot be ruled out when the system becomes fully operational in the near future. A storage reservoir is also planned for this system sometime in the future. Therefore, the short-term condition without reservoir and the long-term condition with reservoir are analyzed. The largest of the three past storms, September 26, 1986, storm, and the maximum design inflow rates were considered. In the following tests, all tunnels are assumed to be connected and the whole system operates as a unit.

A. Short Term Solutions

1. Sepember 26, 1986 storm

The total inflow hydrograph due to the September 26, 1986, storm is shown in Fig. 42. The tunnel is assumed to be initially empty. River water level is assumed to be at elevation +2 and overflow is allowed when the level in certain dropshafts exceed the river level. Time variation of water depth at three key stations are plotted in Fig. 43. This figure clearly indicates the existence of surges in the system. However, the oscillation coefficient is substantially less than one (Nf = 0.411) indi­cating that surge is not strong enough to produce a geyser. The tunnel will eventually fill up and overflow will occur. Total overflow hydrograph is shown in Fig. 44.

No inflow control is necessary in this case.

2. Maximum design storm

The analysis indicates that the surge will be severe enough (Nf = 1.45) to cause a geyser if the maximum design storm is allowed to enter unrestricted.

Presently there are six gated dropshafts (CS - 7, 8, 10, 11, 12, 13) which can be used to control the inflow. By trial, it was determined that the geyser problem will not exist if all six gates are closed within 10 minutes after the tunnel is 75% filled. The corresponding total inflow hydrograph is shown in Fig. 45. Time variation of water depth of five key stations are shown in Fig. 46. The calculated oscillation number is Nf = 0.81.

20

Page 29: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

B. Long-Term Solutions

The planned Thornton Reservoir enables the system to take all the inflows due to the September 26 storm without causing geyser problems. Geyser problems do not exist even for the maximum design flow if the reser­voir is initially empty. The total inflow hydrograph used for this analysis is shown in Fig. 47. Here the inflow rate is allowed to linearly increase to the maximum value in 75 minutes. Time variation of six key locations are shown in Fig. 48. It is interesting to point out that the water level at the treatment plant rises very slowly due to the existence of the reservoir although there are surges indicated by rapid level rises at other stations further upstream. The time variation of water depth in the reservoir is shown in Fig. 49. The computed oscillation coefficient is Nf '" 0.15.

It is reasonable to expect that, if the tunnel is initially 100 percent full, sudden and large amounts of inflow are not allowable, even when the reservoir is operational. The dynamics of surge would depend on the initlal storage level, the rate of increase of the inflow rate, and the maximum inflow rate. Time and funding do not allow a complete parametric study. For the purpose of illustrating the type of analysis that may be carried out in the future, two additional example runs were made. 'Both runs assume the total inflow hydrograph to be as shown in Fig. 47. The tunnel was assumed to be initially 50 percent full for the first run and 75 percent full for the second run. Both cases indicated no geyser problem although the surge problem progressively worsened as the initial storage increased. The calculated values of Nf is 0.31 for the first run and 0.38 for the second.

21

Page 30: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

VII. THE DES PLAINES SYSTEM

The Des Plaines System is to be constructed in three stages. These are the South System, South-Middle System, and the complete system. The system's configurations for modeling purposes are shown in Figs. 50, 51, and 52, respectively. Maximum design inflow rates were used for all three cases. All dropshafts are assumed to be fully gated. The purpose of the analysis is to determine the time of gate closure so that water will not reach the elevation of any flood gate at any time.

Since there are many possible combinations of individual gate closing schedules, a comprehensive study cannot be carried out at this time. All gates are assumed to be operated simultaneously and closed at the same time.

A. South System

The inflows are assumed to increase from zero to the maximum design values of 80 minutes. As the tunnel fills, the inflow will be cut down to zero in such a way that there will not be any excessive surge during the process and that the tunnel is filled at the end. Simulation results indicate that, if the maximum inflow is suddenly cut-off at a time when the tunnel is nearly full, strong oscillations will occur. The water column in some dropshafts may oscillate by as much as 50 feet. For structural safety it is desirable to avoid oscillations of this magnitude.

After a number of trial runs, a satisfactory gate closing procedure was found: start gate closing when the system is 50 percent full, cut-off two-thirds of the flow in 20 minutes, wait until the system is 75 percent full and resume gate closing, and complete the closing in 20 minutes. The resulting total inflow hydrograph is shown in Fig. 53. The calculated time dependent water depth at the upstream and downstream ends of the system are shown in Fig. 54. The oscillatory motion shown in this figure caused by gate closure may become unacceptably severe if the gate is closed too rapidly. Instantaneous hydraulic grade1ines plotted in Fig. 55 show the surge movement.

The system is 94.5% full at the end of the operation.

B. South-Middle System

In addition to gate closure, it is assumed that a pump station located at the downstream end can be activated to withdra,., 200 cfs from the system whenever necessary. For simplicity sake, the model assumes that the pumping rate of 200 cfs is used as soon as the inflow rate exceeds 200 cfs.

A satisfactory gate operating procedure is to start gate closing when the system is 75% full, cut off the two-thirds of the inflow in 10 minutes, resume gate closing when the system is 90% full, and close the gate until

22

Page 31: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

total inflow is equal to 200 cfs. The corresponding total inflow hydrograph is plotted in Fig. 56. The time variation of water depth at two ends is shown in Fig. 57 and similar plots for two other stations are shown in Fig. 58. Instantaneous hydraulic gradelines are shown in Fig. 59.

The system is filled to 92.2% at the end of the operation.

C. Complete System

The operating procedure described for the South-Middle System is also satisfactory for the complete system.

Figure 60 shows the total inflow hydrograph. Time variation of water depth at the upstream ends of three branch tunnels is shown in Fig. 61. Instantaneous hydraulic grade1ines along the main tunnel are shown in Fig. 62. Very steep slopes near the upstream end prevent the surge from reaching the upstream end. The tunnel is 95% filled at the end of the operation.

23

Page 32: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

VIII. SOLUTION ALTERNATIVES FOR l3A SYSTEM

The outflow from the l3A tunnel to the Main Stream Tunnel is blocked and the branch tunnel is assumed to be independent. There is an overflow structure at the downstream end to relieve the tunnel and prevent flooding. The overflow structure consists of a 10.5'x13.5' exit conduit with invert elevation at -9.5'. There is a flap gate preventing river water from entering the tunnel. When the tunnel water level at D861 exceeds that of river water, assumed to be at elevation 0, overflow is assumed to take place through an orifice.

Three sets of inflow rates: (1) existing estimated peak, (2) future planned peak, and (3) dropshaft design capacity were used as the inflow rates. The total flow rates are 1003 cfs, 1805 cfs, and 3322 cfs, respec­tively. The objectives of flow control are to limit the maximum water level at DS.61 to be less than 18 feet and to prevent geysering everywhere in the system.

The system configuration for modeling purposes is shown in Fig. 63.

A. Existing Estimated Peak Inflow Condition

The inflow rate at each dropshaft is assumed to be constant and equal to the existing estimated peak flow. The time variation of water surface elevation at the downstream end is shown in Fig. 64. The corresponding plot for D8.61 is shown in Fig. 65. At t = 100 minutes, the flow has attained an equilibrium condition and the water level becomes independent of time. Surge does not produce very sharp peaks and the water level at DS.61 stores under elevation 18 ft all the time. No possibility of a geyser is indicated. The overflow hydrograph is shown in Fig. 66.

B. Future Planned Peak Inflow Condition

The system overloads under restricted future planned peak inflow con­ditions. Two problems are noted in this case. Because of rather high inflow rates at Station 5 (DS.55), the junction becomes pressurized rather early and produces large air space between the junction and the surge front luoving upstream from the downstrearn end. This situation should be avoided because large waterhammer pressure may be generated when two surge fronts collide. The second problem is the violation of water level constraint at D8.61 due to the inflow rate exceeding the overflow capacity. At the request of the client, the analysis was carried out based on an assumption that inflow control gates will be installed at all dropshafts.

After several trial runs, a satisfactory control procedure was found. First the inflow at DS.55 should be limited to 200 cfs by presetting the gate at the proper opening. Second, the inflow at station 40 (DS.I) should be reduced from the original 460 cfs to 230 cfs in ten minutes as soon as the water level at D8.6l reaches elevation 8.

24

Page 33: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

Time variation of water surface elevation at the downstream end is shown in Fig. 67. The corresponding plot for DS.61 is shown in Fig. 68. The water surface approaches the limiting condition slowly without violating the constraint. The overflow hydrograph is plotted in Fig. 69. No geyser problem exists.

c. Dropshaft Design Capacity Inflow Condition

The total inflow in this case exceeds that of the last case by a large margin. Clearly, this amount of inflow is not acceptable.

Undoubtedly, there are a number of possible gate control procedures. After several trail runs, a possible control procedure, not necessarily optimum, was found. First, the inflow at DS.55, must be limited to 100 cfs from the beginning of the storm to prevent premature pressurization at the junction. Inflow from all dropshafts are cut-off in 10 minutes starting when the water surface at DS.61 reaches elevation -77 ft. According to the computer output, all gates will start closing at t - 23 minutes but the additional inflow taking place during the 10 minutes closing time is sufficient to fill the tunnel. If desirable, gate closing could start earlier but leave some inflow to continue after the gate operation.

Time dependent water surface elevation at the downstream end and at nS.6l are shown, respectively, in Figs. 70 and 71. The calculated overflow is shown in Fig. 72. Eecause of larger initial inflow rate, the flow is more dynamic in this case than the previous two cases. The flow oscilla­tion causes overflow to take place in two separate time periods.

The system operates satisfactorily under the assumed operating condition.

25

Page 34: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

IX. CONCLUSIONS AND RECOMMENDATIONS

The mechanisms of air blow-off and geysering have been identified and possible solutions recommended. l3ecause the mathematical model outputs were compared with some field data and showed good agreement, the modeling results should be reasonably reliable. Following is a list of some significant conclusions:

1. Some air flowing out of the tunnel through dropshafts or air vent when tunnel is filling is inevitable. With existing grating of covers, no structural damage due to air flow should occur.

2. Geysering is basically caused by a rapid rise of water level in dropshafts due to pressurization surge. For a dropshaft with long drift tube, such as DS.53, resonance may magnify the problem of geysering.

3. For DS.53 of the Main Stream System, it appears that the resonance is made possible by a reduction in pressure wave speed due to entrained air bubbles. Estimated relationships between dropshaft height, drift table length, and the air concentration are shown in Fig. 73.

4. The transient problems can be controlled with proper inflow control. Satisfactory control procedures have been identified and described in this report. These control procedures are not necessarily optimum because optimum conditions depend on objectives and require considerable search efforts.

5. Inflow control or other surge mitigating is necessary for the Main Stream System even after the construction of the planned reservoir at the downstream end. This is due to insufficient coveyance.

6. There is a choice between a construction of a surge mitigating reservoir at the upstream end and the use of inflow control when the planned reservoir for the Main Stream System is in place.

7. The situation for the Calumet System is quite different from that of the Main Stream System. It has sufficient conveyance so that the presence of the planned reservoir can prevent the surge problem.

8. For the Des Plaines System, the gate closures may be carried out in two steps to avoid large amplitude oscillation while large amounts of flow can be captured and the system is nearly full at the end.

26

Page 35: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

9. Because there is an overflow structure at the downstream end, the l3A tunnel is relatively easier to control. It needs no control with the existing estimated peak flow condition.

10. Because of the difference between dynamic and static conditions, the Main Stream System and the Calumet System controls should not be based on the water level measured at a single location. The control should be based on the actual volume of water stored in the system. Good estimates of storage volume can be made by using water surface elevations measured at two stations sufficiently far apart.

Some recommendations as listed below are offered.

1. The resonance problem at DS.53 should be solved on a priority basis because it is the most likely location for a geyser to occur.

2. More detailed analysis is needed for the actual solution of DS.53, short or disconnecting it from the Main Stream System.

3. All solution procedures described in the report are satisfactory from the transient point oE view, but not necessarily optimum from operational or other possible viewpoints. Therefore, either the procedures should be further refined by analysis or field trials before regarded as final.

4. Any control procedure described in this report is based on a given inflow hydrograph. In actual conditions, the inflow rate is not known, and therefore, the control procedure based on storage volume alone may cause risks. Two types of risks may be considered. If the operating procedure based on large storms is adopted, then the risk is under utilization of the tunnel. On the other hand, if the operating procedure is based on small storms, then the risk is geysering and safety. For this reason a risk analysis is recommended.

5. One practical method of reducing the risk described above is to base the control on storage volume plus the rate of increase of the storage. Recause the rate of increase of storage volume reflects the inflow rate which also reflects the storm size, the control method based on these two values should greatly reduce the risk. This method is recommended because it may be more practical than a method based on weather forecasts.

6. The storage volume-water surface elevation relationships given in this report apply only to the cases without reservoirs. The relationships should be redetermined in the future when reservoirs are constructed.

7. The long-term solutions for Main Stream and Calumet Systems are based on the assumption that the tunnels are connected to

27

Page 36: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

the reservoirs at all times and there is no gate or valves to impede the flow. Further analysis is needed if the flow between the tunnel and reservoir is to be disrupted for draining or other reasons.

28

Page 37: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

- - - - - -- - - - - - -

Lawrence Ave. Tun. 44 45 6 68

Chicago River 105 "J:+..-1 13

112 106

132 South Fork 142

141 133

Nashville Ave. 179 ~~--~

195 180 13A Tunnel

73rd St. ----+I

245 25 Station

... .\ .. Under construction

(proposed)

Four separate tunnel systems serve Chicago and 15 suburbs.

201

Figure 1. Mainstream system configuration and stationing for rnodelin~ purposes.

Page 38: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0-r ________ ~ __________ ~ ________ ~ ________ ~ ________ ~ ________ ~ __________ L_ ________ J_ ________ ~

g

I I

~~ 01

I ,..... f-l.L - ~-i ---1 ~ I ~ I I w I

I

~ ~~ + -.J ~Calculated

f- g CC ~ I

3: I 0 CC w

+ ..... / +", Measured

I ~i (f)1

f h D-

1\ ~ r 0

0 0

"" I

ci I I I 90.0 L20.0 15Q.0 ~ 0.0 30.0 so.o

I 1+5 :00 A!~, Oct. 3, 1986 270.0

TIME (MIN) 180.0 210.0 2'10.0

Figure 2. Comparjson of measured and calculated water level at the downstream end, Oct. 3, 1986 storm.

Page 39: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0

0 LI'lj

- I ~

I 0 1 c:::i-i

'" l-LL - 0

...J gl W' > I W I ...J I Ei CO I I- 01 a::: 2 I ~ I I

0 i 5 I + :c 0 !

.-1 co . J W + + ttl -en 1

D-, ,..... ---. + +

+ + o I I Jl . ,,+~ ,...-r ..L. -r +

~ Measured

~ I I I II I ~o.o 30.0 60.0 90.0 120.0 150.0

I I+-Noon, Sept. 26, 1986 TIME (MIN) 180.0 210.0 2'iO.D 270.0

Figu-re 3. Compa-rison of measured and calculated wate-r level at downstream end, Sept. 26, 1986 storm.

Page 40: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

LAWRENCE AVENUE 44

82 CHICAGO RIVER

102 SOUTH FORK

73rd STREET

Fig. 4. Stationing of Hainstream System excluding all branch tunnels.

Page 41: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0 0 g

SYMBOL TIMECMIN)

C) 0.000

~I A 37.LfLfl

+ lLf2.755

0

0 C> N

,..... l-lL .....,

C>

I 0 ~

t-CL W 0

0

-.( Di~ectionof Surge Movement

C>

8

o

~

d I ,h ~ =~ ~ ~ 15 ~ ~ 0.0 20.0 'i0.0 60.0 80.0 10Q.0 120.0 1'i0.0 1S0.D 180.0

'.l:"pstream e~d STATION (NO.)

Figure 5. Instantaneous hydraulic gradelines showing pressurization surge, Octob~r 3. 1986 storm.

Page 42: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0

0 0

'" SYMBOL TIMECMIN)

C9 157.0LJ8

~I A 153.718

+ 163.LJ10

0

0 Q

N

,.., ~ LL '-" Co

I ~ I-eL w 0

0

0. 0 ...

o o Ul

X 167.333

»-- Direction of Surge Movement

DS 52 & DS 53

Y ci I I I I I I I I I

0.0 20.0 '10.0 60.0 80.0 100.0 120.0 1'10.0 160.0 l80.0

14- Upstream end STATr ON (NO.) Figure 6. Instantaneous hydraulic gradelines showing reflected surge, O~t. 3, 1986 storm.

Page 43: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

,.... l-lL

""

0-r ______________________________________________________ ~ ____________________________________________________________________ -,

g

o

~

0

g N

Co

SYMBOL C)

TIMECMIN) 180.823

187.573 ~2~

I~ l-n... lL.I -c: Direction of Surge Movement

0

0 .,,; 2

o g

~I 0.0 20.0 '10.0 60.() 80.0 10<1.0 120.0 1'10.0 160.D l80.0

, ..... UpstreaE end -.: STAT ION (NO : .. )

Figure 7. Instantaneous hydraulic griidelines after the second reflection, Oct. 3, 1986 storm.

Page 44: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0

0 0 ...,

SYMBOL STATION

0 ci I/)

1 C'oI (!) - UPSTREAM END

A 116 - DS 52 & DS 53

+ 2LiLi - DOWNSTREAM END 0

0 ~

-l-LL ......, .... J:~ t-a... lLJ 0

0 Co 0 -

o

~

o rea E!9 E!9 E!9 i' E!9 E!9 e E9 e e e e e e e e e e E9 E9 e e e' ci I I I

c.o 30.0 60.0 so.o 120.0 15G.0 180.0 210.0 2'iO.D

TIME (MIN) Figure 8. Water depth at three selected stations with reservoir, no inflow restriction,

Oct. 3, 1986 storm.

270.0

Page 45: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

--(f) LL 0 LL 0 (f) 0 z « (f) :::)

0 I I---~ 0 .....J LL Z

.....J

~ 0 I-

70 I I I I I

--60 r- -

50 I- -

40 I- -

30 I-- -

20 I- -

10 I- -

O~ __ ~I~ __ ~I~ __ ~I~ __ ~J ____ ~l ____ ~ o 30 60 90 120 150

TIME (MINUTES)

Fig. 9. Total inflow rate, maximum storm partially controlled.

180

Page 46: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

r-.. f-LL "" J: t-tL w 0

o~ ______________________________________________________________ ~

~ I SYMBOL TIMECMIN)

o

~

0

6 Q C\I

Q

6 Lf)

0

'" 0 -

o g

(2) 60.000

t:::.

+ X

101.3113 106.135 110.505

~ I~ eo. ? e e e , e e e , e e E9 , e E9 E9 T e E9 e ? E9 e E9 , e E9 § 0.0 20.0 '10.0 60.0 80.0 100.0 120.0 l'iO.O 160.0

I4-Upstream end STATION (NO.) Fig. ]0. Instantaneous .hydraulic gradelines, reservoir initially empty.

l80.0

Page 47: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

~ CALUMET TUNNEL

226

CALUMET TREATMENT PLANT

~I~ 145 119 118 55

I+t It117

Ul 1-' !l> '-0 Q

~ ~ 1 1-' ~

H t:lj f:Ij

120 '.56 Ul tJ:j :;;:: J::I:j !:lj

18EA TUNNEL &. MT. GREE1'WOOD It 1

34 27 1

1+1 33 ::s 1-3 . Q :::tl t:lj J::I:j Z :::E 0 0

28 t::!

~ l\)

Fig. 11. Existing Calumet System configuration for mOdeling purposes.

Page 48: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

r-273

CALUMET TUNNEL 252 205

CALUMET TREATMENT PLANT

I

25t~ > tf.l t%j

H

1-3

~ ?13. 1:-1

206

THORNTON RESERVOIR

~ 145 119:·1;1.8 55

I I

14~ f~ 11;1~

120

I I-'

56

E2 t-t H t%j t-lj

(/)

~ :::0

~ 18EA TUNNEL & MT. GREENWOOD til

34- 27. 1 I

3;t~

28

o

~ ~ ::E: o o t:;I

::tt:: N

Fig. 12. Future Calumet System configuration for modeling purpose.

Page 49: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

140 ~----~----~~----~------~-----.-----. ....--.. I­W W IL 120 o en ~

o 100 IL o (f)

Z 80 o ....J ....J

~ -- 60 w ~ ~ o 40 > w C) « 20 a: o I-(f)

I" .' :> ,.

j :, l

,.' ,f'

",-.'

If····

.S::::: ........... . . --.'.~ ... .",. ')

(

........ ---.. ~ .. --.--"-.--­_ .............

-.-..... ~

...... OCT. 3 STORM

- - SEPT. 26 STORM

STATIC STATE

o ~----~------~------~----~------~------~ o 50 100 150 200 250 300

DOWNSTREAM END DEPTH (FEET)

Fig. 13. Statically and dynamically determined correlation between volume and depth at downstream end, Mainstreanl System.

Page 50: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

100r-----.-----.------r-----.--~~~--~

.-I­Z UJ ()

90

80

a: 70 UJ a.. -UJ

~ 60 a: o I-00

~ 50 ::> ....J

§? 40

30

I I I

I

I , I , ,

I I

. I .: , .... \ \ f.

. . .

I I

I

. . . . . . .

I

. . .

I /

. . . . . . . .

" '" '"

. . .

. . · · ·

. . . . . . . .

...... OCT. 3 STORM

- - SEPT. 26 STORM

- STATIC STATE /

20~--~~-----L----~------~----~----~ o 50 100 150 200 250 300

DOWNSTREAM END DEPTH (FEET)

Fig. 14. Statically and dynamically determined correlation between storage volume and depth at downstream end, Calumet System.

Page 51: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

\

7711111111111111111111111111111111111111111111111111"

;: DYNAMIC fREE_SURfACE _U ..... I..L.1j.J.J.'LL1. 11/ 1/ I /I /I /I /I~ I L I~ I 1/ I /I /I

_

.l£l££££l~ _------- _--------X££lUI

• fLO~SIAlIC fREE-SURfACE SURGE /111117111 IIIJlII7 11/1111/11 111/111 1I1/l11f lillI/III

QU.~it.ti~C comVa,ison of ~at.' su: face .:o~ile. bet~een statiC condition and dyuan"c cond,t,on.

Page 52: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

150

..---.. I-W W lL

0 en 125 ::J 0 lL. 0 (f) z 0 -' 100 -' ~ -w QJ « cr:: 0 I- 75 (f)

0

~ j--.:= (f)

50

6 c#""

0 (.j.

LO 60

6 0

0 6 0

6 0 0

6 0°

6 0 6 0

o OCT. 3 STORM

6 SEPT. 26 STORM

- PERFECT FIT

50 75 100 125 150

ACTUAL STORAGE (MILLIONS OF CUBIC FEET)

Fig. 16. Comparison of actual storage and static storage­l1ainstream System.

Page 53: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

...--.. I­W W IL

o (() :J

150~--------~--------~----------~--------~

o 125 IL o (f) z o ...J ...J

~ 100 --w C) « a: o I­(f)

o w ~ ~ I­(f) W

75 o OCT. 3 STORM

6, SEPT. 26 STORM

- PERFECT FIT

50 ~--------~--------~--------~--------~ 50 75 100 125 150

ACTUAL STORAGE (MILLIONS OF CUBIC FEET)

Fig. 17. Comparison of actual storage and estimated storage based on depth at two points - l1ainstream System.

Page 54: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

25

...-... t-UJ UJ LL

0 20 en => 0 LL 0 (f) 15 z 0 -l -l

~ ---UJ 10 (.!} « a: 0 t-(f)

0 5

\d: t-:= (f)

0

o OCT. 3 STORM

6 SEPT. 26 STORM

- PERFECT FIT

8

8

8

8 8

8 8 8

0 6. 0 8

O 8

0 8

08 8 8 8 ~.

0

0 5 10 15 20

ACTUAL STORAGE (MILLIONS OF CUBIC FEET)

Fig. 18. Comparison of actual storage and static stora8e -Calumet System.

25

Page 55: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

25 .-.., I-W W u.. 0 r.::o 20 :::> 0 u.. 0 (f) z

15 0 .....J .....J

~ .........

w <!J 10 « a: 0 I-(f)

0 w 5 ~ ~ I-(f) w

0 0

o. 0 o .

o Z':::. 6.

6. 6. .' 6.

. 6. 6.

6.

0 OCT. 3 STORM

6. SEPT. 26 STORM

- PERFECT FIT

5 10 15 20 25

ACTUAL STORAGE (MILLIONS OF CUBIC FEET)

Fig. 19. Comparison of actual storage and estimated storase based on depth at two points - Calumet System.

Page 56: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

/,DROPSHAFT COVER

CONNECTING PIPE Os

DROPSHAFT

He MAIN TUNNEL .1', " ' ..

H ,.

,.

"

ft N·. ·"FLOW , .. ~ ~ ~

I· L

·1

Fig. 20. A sketch of Dropshaft-Drift Tube System for geyser analysis.

Page 57: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

O~ ________ -L ________ ~ ________ ~ ________ ~ ________ ~ ________ ~ ________ ~ ________ ~ ______ ~

~ ~

0 0 0 t"

0

0

'" N

r-.. ~ LL

~ °1 :r: g t-- N

(L lLJ 0

0 0

~

o

~

~I uo.oo

SYMBOL STATION

(!) 1 - DEPTH AT TU~TI{EL

A 11 - PRESSURE AT DS BOTTOH

+ 15 - DEPTH A1: DS

10.00 20.00 30.00 '10.00 50.00 60.00 7(1.00 80.Gu

TIME (SEC) Fig •. 2 1. Time variation of water depth in dropshaft due to slm~ rise in tunnel pressure,

without resonance.

90.00

Page 58: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

r--..

l-LL '-./

I r-0.--lLJ 0

o I

o i If) ,

~ I SYMBOL STATION

0

0 0 ("')

0

0 lO 0J

Co

0 0 0J

0

<=> U")

o o ~

01 o Ll"o.oo

C) 1 - DEPTH AT TUNNEL

6. 11 - PRESSURE AT DS BOTTOM

15 - DEPTH AT DS /""-.

10.00 20.00 30.00 ~O.OO 50.00 60.00 70.00 80.00

TIME (SEC) Fig. 22. Time variation of water depth in dropshaft due to rapid rise in tunnel pressure,

without resonance.

30.00

Page 59: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0

0 11) ,.,

0 0 0 M

0 0 II> C'\I

/"..

l-LL "" Q

I 8 t-- C'\I

0...-w 0

0 Q 11) -

o

8

61 UO.oo

./

SYMBOL STATION

(!) 1 - DEPTH AT TU1lNEL

fj, 11 - PRESSURE AT DS BOTTOM

+ 15 - DEPTH OF DS

10.00 20.00 30.00 '10.00 50.00 60.00 70.00 80.00

TIME (SEC) Fig. 23. Time variation of water depth indropshaft due to slow rise in tunnel pressure,

with resonance.

90.00

Page 60: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

8 CHICAGO RIVER BRANCH TUNNEL 2 ~ __ -I

90 89 83

109 SOUTH FORK BRANCH TUNNEL

119 118 110

171 73rd BRANCH TUNNEL

PUMPING STATION 172 185

Fig. 24. Hain stream System excluding the 13A, Nashville and Lawrence Ave. branch tunnels.

Page 61: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

g~~--~--~--~~--~--~~--1 o ~

0 Q lJ)

(>J

:r

0 ~

..... '" Co /'-.. 0 0

/'-.. (>J

en l.L u '-/

Q

:;:;: 0

0 lJ)

-...l /V/\ l.L. :z: .)-l

~ 0 0

a:: 0

I-0 I-

0 0 lJ)

§~I---------.---------.--------,,--------'---------.--------'--------~---------r--~--~ 60.0 30.0 60.0 90.0 L20.0 150.0 180.0 210.0 2'-10.0 270.0

~8:00 PH, Oct. 18, 1985 TIME (MIN) Fig. 25. Total inflow hydrograph for short term solutions, Storm A.

Page 62: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

r-... l-LL

6 I I o I I " I SYMBOL STATION ~ o o Ii') N

0

0 .:=. N

C)

6.

1 UPSTREAM END

171 DOWNSTREAM END

~ ~l .J ~ ~

~ h M ~ ~I~ u... w j J 0

0

<=> 0 -

o o Ii')

o I i G €) ~~ ~OO? ~ E9 E9 ~ ~ ~ ~ ~ G o I I

0.0 30.0 60.0 80.0 l20.0 1500

TIME (MIN) 180.0 210.0 2'10.0

Fig. 26. Time variation of water depth at upstream and downstream ends, short-term solution, Storm A.

270.0

Page 63: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

o _ ! _____ ~ _l _____ ~ _______ .!.._. __ _

/'..

r-

~ I I I

~l

J o 0=> 0J

,

LL I '-./ "" I § r- , CL u.J o

O....J a D

oj 5'i1

I

I

SYMBOL STATION

C)

h.

1 UPSTREAl1 END

93 DS .53

~ ~

I

I I

J ~ I

J~ ~1 ~ I\J v i

I I • ~ "ID)~ J /vl vV

l o I Fe e3I E9G GOO? G e3 e3I G G G E9 G @

6 I I I I I I I I

0.0 30.0 60.0 90_0 l20.0 15Q.0 180.0 210.0 2'-10.0 270.0

TIME (MIN) Fig. 27. Time variation of water depth at DS-53 and the upstream end, short-term solution, Storm A.

Page 64: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

~-4------'-----~

T § 0"

:><

-.l cr:: f­a f-§

63,180 cfs

I I I I I

-

-

-

-

3150 cfs

~~O_-O------~~_O-------oo~_O-------~T_Q------I~-r_O------l~,.rO------1OO,.r0-----2-wT.o------~--TI.-D------m~.o TIME (MIN)

Fig. 28. Total inflow hydrograph for short-term solution, Storm B.

Page 65: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0

'=' ':.:: M

I

I

il

g~ '"\,

r--.. ~

LL '-../

"" I ~ !- -~ W 0

0

"" S

o o lJ"!

1 ___L_J _ _ ____ 1 ___ _

SYMBOL STATION

Q)

A

1 171

UPSTREAl1 END

DO'HNSTREAl1 END

~

, I~

W

n J

i ,

~ I I

6 ~OO(9@6;666e:e:ee::eE3Q ~ @ @ @ @ E9, E!l 9 E!l E9 q2 E!l E!l E!l '5l E!l E!l

0.0 30.0 60.0 90.0 120.0 15(1.0 180.0 210.0 2'10.0 270.0

TIME CMIN)

Fig. 29. Time variation of water depth at upstream and downstream ends, short-term solution, Storm B.

Page 66: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

I~)

.. ~

>(

~ u

30 0 -1 IL Z

-1 a:: I-a l-

g-

63,180 cfs -, " I

I

" '"

8 )"'

g

S

g-

2300 cfs

§;--------r-------r------~------~------_,------~------~------~------~ 60.(1 so.o 120.0 180.0 2'iO.0 300.0 360.0 'i2O.0 'i8O.D

TIME (MIN)

Fig. 30. Total inflow hydrograph for short-term solution, Storm C.

S'10.0

Page 67: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

o I ~ i

SYMBOL STRTION

0

6 Ul 1 - UPSTREA,'1 END N (l)

!::,. 171 - DOWNSTREAH END

0

0 Q

N

r-.. f--LL '-'" Q

I ~ I-0..... w 0

0

0 3

o o II)

o ~I!1lli!!llllle'lfl2X'X')6f)(')(')(')(t) 6 E9 (')(') E9 (')(') C)(j9(') (') CH9 (') E9 E9 (') (') I o I I

0.0 60.0 120.0 180.0 2'10.0 300.0

TIME (MIN)

/~MM""1>"""M

360.0 '120.0 '180.0 5'-10.0

Fig. 31. Time variation of water depth at upstream and downstream ends, short-term solution, Storm C.

Page 68: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

I o I i o o ...,

SYMBOL STATION

~l 0

0 Q

~

r-... l-LL '-" Q

I g t-- -0....... I.J.J 0

0 0 0 -

I

01 17l

0 ci

0.0 60.0

C)

fl

Fig. 32.

1 - UPSTREAH END

93 - DS-53

120.0 180.0 2'-10.0

TIME 300.0 360.0 '-120.0 '-180.0

(MIN) Time variation of water depth at DS-53 and upstream end, short-term solution, Storm C.

1

5'-10.0

Page 69: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

40 ~I ----~~------~------~------r_----_,r_----_,r_----_.------_.------_.

-CI) u. ()

u. o CI) o 30 z « CI)

:J o I I--~ o 20 .....J U. Z

.....J

;:; o I-

10 I~ ____ ~ ______ ~ ____ ~ ______ ~ ____ ~ ______ ~ ____ ~ ______ -L ____ ~

o 60 120 180 240 18:00 PM. Oct. 18, 1985

TIME (MINUTES)

Fig. 33. Total inflow hydrograph, long-term solution, Storm A, reservoir initially empty.

Page 70: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

o~ __________ ~ __________ ~ ________ ~~ ________ ~ __________ ~ __________ ~

~

SYMBOL STATION

0 0 I/)

1 N (!) UPSTREAM END

!::. 93 DS.53

+ 171 DOWNSTRE~~ OUTLET TO RESERVOIR

0

0

"" N

"......

l-LL

"" "" :r: § t-~ W 0

0 Co 0 -

o

~

6 I If. I bfl, ~~E9E9E9E9E9E9Eger eee el e E9? e E9EgeE9E9E9~E9 C9 6 E9 E9C'P"l.'"9?eeeee~ 0.0 30.0 60.0 90.0 120.0 150.0 180.0 210.0 2'iO.D

TIME (MIN) Fig.·34. Time variation of water depth at three stations. long-term solution. Storm A, reservoir

initially empty.

270.0

Page 71: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

o g~~--~~--~~--~--~~

~

~l / \ ~ :r

/ \ I I

~ 8 1

/ \ I 0

r-... ,...;

en I..L U '-./

&:> > 0 o u: ---1 LL z: I--l

.-1 g cc c:: 1-0 l-

I

§l

§ I I I I I I I I I I 00.0 30.0 60.0 30.0 l20.0 150.0 180.0 210.0 2'i0.O 270.0

r- 8:00 PM, Oct. 18, 1985 TIME (MIN)

Fig. 35. Total inflow hydrograph, long-term solution, Storm A, reservoir initially partially full.

Page 72: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0

0 0

"" SYMBOL STATION

0 0 IJ)

1 N (!) UPSTREAM END

1:::,. 93 DS.53

+ 171 DOWNSTREAM END

6-1 "" r'_

r-.

l-LL '-./ Co

I g t-O--W 0

0

"" 0

o

~

6 I I j,ee E9E9 E99E9FooeH9:geee?e:H:99 E9 9 ~ ~e e e e f e C) C) 9 C) E9 0 P 0 0 0.0 30.0 60.0 90.0 L20.0 150.0 180.0 210.0 2..,0.0

TIME (MIN) Fig. 36. Time variation of water depth at three key station, long-term solution, Stor~ A,

reservoir initially partially full.

,

J

270.0

Page 73: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

<> ><

(() !.L U

)< 0 .1 LL Z

.1 u:: I·· 0 I··

Ii - ... __ .. ~ __ .. J . ___ ... __ L __ ._ .---L -.-.. - ._j J __ .

63,180 cfs

~--

~l ,n

§

g

§ 17,800 cfs

§ -----.---.----.---.----,---,---,,--~.---~ (>0.0 30.0 60.0 90.0 120 0 ISG 0 160.0 2]O,Q 2~0.D 270.0

T J Mr~: (M J N'

Fig. 37. Total inflow hydrograph, long-term solution, Storm B and C, reservoir initially empty.

Page 74: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0

0 0 ,,",

0

0 III (".J

0

0 0 ",

r--. ~ LL '-/ 0

I § I-eL. W 0

0

0

2:

o o III

SYMBOL STATION

C) 1 - UPSTREAl1 END

.6 93 - DS-53

+ 171 - DOHNSTREAl·1 END

~ I ~Eft~66 6 ~ E!H9 E!:H9 ~ 6 e ~ @ (,1H9 f (9 (9 (9 (9 (9~ (9 i~ 0 9 0 C)(!) (!) I

0.0 30.0 60.0 30.0 [20.0 150.0 180.0 210.0 2'-10.0 270 0

TIME (~lIN)

Fig. 38. Time variation of water depth at three key stations, long-term solution, Storm Band C, reservoir initially empty.

Page 75: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0

<::> 0 ".,

~l

0

0 0 N

i"'-

f-LL '-" 0

I ~ l-lL w 0

0

"" S!

o D Lfl

SYMBOL TIMECMIN)

C9 60.000

A 105.616

+ lY5.866

X 205.551

SURGE MOVING UPSTREAl1

"

POSITIVE AND NEGATIVE SURGES ALTERNATIVELY MOVING DOWN­STREAH AND UPSTREAl1

6 I IS ~~ e 6 ? 0) 6 6 ? 6 6 6 ? 6 C) 6 f 6 6 e 9 6 e 6 ? 9 e cl 0.0 20.0 '10.0 60.0 80.0 10(1.0

/4- UPSTREA11 END . STATI [l~J (NO.) Fig. 39. Instantaneous hydraulic gradelines, long-term solution,

120.0 1'10.0 160.0 180.0

Storm Band C, reservoir initially empty.

Page 76: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0

0 0 ...,

SYMBOL STATION

0 0 If) 1 - UPSTREAM N (!)

93 . END l:,. - DS-53

+ 171 _ 0

0 Co N

r--.. f-LL '-/ "" :r: ~ ... r-0-W 0

0

Co :::

gl

o I ~'Q$D~E9~~ I I -I"",+- ~ o I I I I I I

0.0 30.0 60.0 90.0 120.0 150.0 180.0 210.0 2'10.0 270.0

TIME (MIN) Fig. 40. Time variation of water depth at three key stations, long-term structural solution, Storm C,

reservoir initially' empty.

Page 77: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

"""' I-

o 1

8 i t,., I

I

~~ ,~ I

J C: C> <""'J

~ l '-" Q

~ § CL lLJ 0

i

o I .-1 ,::, I

~ I

o o If)

SYMBOL

C)

A +

STATION

1 ~ UPSTREAM END

33- DS-53

171 - DmmSTREAH OUTLET

"

6 I ~Efl~(!)6e(96~ 0.0 i 30.0 60.0 90.0 [20.0 150.0 180.0 210.0 2'-10.0

TIME (MIN) Fig. ·41. Time variation of water depth at three key stations, long-term solution based on inflow

control and surge structure, Storm C, reservoir initially empty.

1

J

270.0

Page 78: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

g "

,.

0 I I

x g.J o ' .: I

en ! " 0

~ sJ lJ..J " f-en lJ..J r:: f-dj u ' cr: lJ..J

~ ~ o· ....J LL Z

.....J '" a: ~ f­o f-

8b::::~------;;r,----:~~~~-----;; .; 0.0 10.0 20.0 30.0 "10.0 54.0 60.0 70.0 60.D SO.O 100.0

TIME (MIN)

Fig. 42. Total inflow bydrograpb for Calumet System due to September 26, 1986, storm.

..., i i I

-!

I

110.0

Page 79: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

,...... !­!.!...

~.

~ __________ ~ ______ ~ ________ -L ________ ~ ________ L-______ ~ ________ -L ________ ~ ______ ~L-______ -L ________ ~

~ I

o 8 11

o.~ C I

I:; i

5V~~::' ....

8 6,

+

STRTION

1 - UPSTREA..""1 END 119 226

19 R-I JUNCTION DOWNSTREAM END

I I

I

l I

I ,W .. IJ~~I,I.J.~I.~~~~~I..'" I

V" '" r-m,e_,

~

i­e.. o

15

I

~~ ~ r,

~,

s -l

o~; ; ; ~ ~ i ~~ ~ ~ £ ~: : : : : ; :::99 0/ e r I o I I I Iii I

00 • 10.0 20.0 JO.O ~O.O 50.0 60.0 70.0 80.0 SO.O 100.0 II: C

TIME (MIN)

Figure 43. Time variation of 1flater depth at three key stations.

Page 80: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

--- I

o g

0

~ ..c A-m '"' ()() 0

'"' 0 " "0 .,; :z :>. ... ...... ..c

::c 5 ....... ,-j

W 4-1 :E '"' 0 ...... Q)

:li ...- I> 0

,-j

m -1-1 0

Eo-<

~ 0 . :r

""" """ 00

• .-1 ~

~ 0 ..,

.- r---- .-----,----- ,-----I---~--.__-----t_;j ~. 01))"0

t, o I X (S.:JJ) l.:H:.II--I~;dOUO wmu MOl.:LL no

Page 81: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

,. ~ i---'-----------------'--------------'-------'-------'---------'-

o I g~

>~ 0 I

...... en l.:.. u

I

I i

i '"' I c... gl L!...i •

~ '1.

~ ~I , EJ-u :::: L:.J

r- ~ ~ ~ o·

t:: JI.

:~v/' , ,,,'. ~. J 1 ••

o , .0.0 . ~ 1 " •• . " , .... I 50.0

I ~o.o TIME (MIN) I ~~ , ~ 1 20.0 d I 10.0 oO.C

Fig. 45. Total inflow bydrograpb, short term solution, maximum design flow.

....;

-,

! : c

Page 82: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

~ ~----~~~--~~~~--~~-

'" ~ 5 n

0

0> T,;

"" f-l:... '-' ~

::: ~ ~

:'-" , 0

0 ~ ",

o o ,.,

5 y l~; a CJ LSi AT! ON

CJ - UPSTREA.lvf END

L 28 - END HT.G tI2 56 - END SAG RELIEF SEHER

X 120 - END 19 R-I

<) 226 - DOWNSTREAH END

~ ~ 't .z P :b tlf~ 0,0 I ~ 9 !:I=!lp~ D l1! d II¥ 'P .p -d 10,0 20.0 30.0 ~o.o 5Q.0 60.0 70.0 ' 60.0

TIME (MIN) Fig. 46. Time variation of water depth at five key stations,

solution, maximum design flow.

3<1.0 100.0 110,0

short term

Page 83: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

5 ~ ---1 ______ --------1

'"

::-

~ ~

x ~ ---!

r-. rJ) " U V'

Q.... ~ lLJ I-r.n '. , L

I-

U a: lJJ

~ §-

I

~ J z

~ ~ E: ~ . 0 r-

§ .,; 0.0 15.0 JO .0 'is ,0 60.0 75.0 50.0 10Z.0 120.0 135.0 j 50. 0 :55. !)

TIME (HI N)

Fig. 47. Total inflow hydrograph, maximum design flow A.

Page 84: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

o ! _I L ____ ~__ __~

~ SYMBOL STATION

c

~ C!l 1 - UPSTREAM END

6 27 - FIRST JlJNCTION

+ 53 - NEAR SECOND JUNCTION 0

~ X 119 - THIRD JUNCTION

~ 203 - NEAR FOURTH JUNCTION

'"' "i" 273 - Dm-mSTREA11 END f-lL. '-" .. :r: ~ r-Cl... l!...I '0

0

:!

c g

~ i F ~ I ~ 'I f ~: e ~ 1 1 1 1 I

0.0 15.0 30.0 '15.0 80.0 75.0 80.0 105.0 120.0 135.0 150.0 :65.0

TIME (MIN)

Fig. 48. Time variation of water depth at six key stations, maximum design flow.

Page 85: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

8 1

;;i

is lG

8 Fi

~ ~ I J: ~ l 'L J 'J.1 :::::l

8 ::!

8 Vl

___ ~ L

SYMBOL STRTION

C) 206

I

J

I ~ I

8 Iii iii iii I I

'" 0.015.0 30.0 'is.O 60.0 75.0 30.0 105.0 120.0 135.0 150.0 l~S.O

TIME (MIN)

Fig. 49. Time variation of water depth at reservoir, maximum design flow.

Page 86: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

24

39

45

BROOKFIELD

38

44

61

77

25

RIVERSIDE

Fig. 50. Des Plaines South System configuration for modeling purposE!.

Page 87: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

42 64 41

BROADVIEW 65

92 106 93

107 RIVERSIDE

113 128 112

BROOKFIELD 129

145

Fig. 51. Des Plaines South-l1iddlE' System configuration for modeling purpose.

Page 88: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

158 136 135

BROADVIEW 159

186 187

201 RIVERSIDE

207 222 206

BROOKFIELD 223

239

Fig. 52. Des Plaines complete system configuration for modeling purpose.

Page 89: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

~ ;

L _____ ~ ~ _ ___~ ______ 1_ _ __ L

~I 1

, i I

o I t'J 0'" LL :;{ I 8 I ::s= I 0 ....JJ ~ 8 . Z ~

....J CC L-

0 f-- g

S

g I

~

tsl

tsI

o~I---------'--------.---------r--------'---------r--------'---------r--------'---------Y-----

---il------~

0.0 15.0 30.0 "5.0 60.0 75.0 30.0 lQ5.0 120.0 135.0 150.0 ISS

TIME (MIN)

Fig. 53. Total controlled inflow hydrograph, South Desplain System.

Page 90: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

,..... f­LL

g I gl

~I

0 0

'" "'

V' g

I ~ r-0-w o

8 g

8 :::!

SYMBOL STRTION

(!) 1 - UPSTREAM END

6. 77 - DOHNSTREAH END

II

I I

I

I

I ~

5 b 9 • 9 ••• 9 • 9 •••• , ••••• , ................ 9 •••••••• 9 • I 0;; I I I I I I I I I

0.0 15.0 30.0 '15.0 60.0 75.0 SO.O 105.0 120.0 135.0 150.0 165.0

TIME (MIN)

Fig. 54. Time variation of water depth, South Des Plaines System.

Page 91: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

--.-~-.--.------------------

-

0

0 ~ ,

SYMBOL HMECMIN)

C) 0,000

~l t:,. 30.576

+ 57.366

X 77.50Y

<> 86.96L

0--1 4' lL 7.829 15 " I

r-,

I-~

C>

~ Z 'l' 0 H E-l <r:: :> ~ ,..:I c:c ~ ~

I

o

~ I

c:cl'~~--__ r---r-~~~~--~--~--~~~ i~ 6_00 12.00 18.00 2'1.00 30.00 36.00 '12.00 '18.00 5'1.00

I

STATION (NO.)

Fig. 55. Instantaneous hydraulic gradelines, South Des Plaines System.

Page 92: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

. '-r--- -----r------

<> <> ~

. s

<> Q) \I) ...... !:! Ul

>. CI)

Q) .-I '0

co '0 <> ..... ~ ~

I .c: ...... ;:l 0

CI)

<>

~ .c: p.. CO

'"' 00 0

0 " '"' 0 :z '0 en ....... >.

L: .c: .....,

:3 0

W .-I E ~ ....... C

0 l- ..... I!!

.-I CO ...... 0

E-<

~ \C5 0 co Ir)

00 ..... r...

0

!Ii

<> g

- ---------TI---------.I---------,Ir---------rl----------.--------~ 000' I 000' 009' OOh' ooz·

h 01X (S~J) ~Ol~NI lY10l

Page 93: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

o I

:1 0

g

,..... l-lL. '-" Co

:r: 8 I-0-W 0

0

~

o o

'"

5YMBOL STATION

C) 1 - UPSTREAM END

6. 1% - DOWNSTRE~~ END

o ps-e e C) ? e 1:9 e e q e e 1:9 1:9 1:9 ~ eex:;e e e e ~ e e e e e e ~ e e e e e e e e e e e e e e e e e o I I I I

0.0 15.0 30.0 'is.O 60.0 75.0 SO.O 105.0 120.0 l35.0 150.0

TIME (MIN)

Fig. 57. Time variation of water depth at the ends of main tunnel, South-Middle System.

165.0

Page 94: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

01

~

o

~

o

Ii

" I-lJ.... ......,

SYMBOL STATION

C)

6

93 - END OF RIVERSIDE BRANCH 100 - MIDDLE OF RIVERSIDE BRANCH

:r: g ..... e.... w o

o §i

o I;j

.I-HU*~~::~:::::;:::::;:~J I I I I I I 0.0 15.0 30.0 '15.0 60.0 75.0 SO.O 105.0 120.0 135.0 150.0 165.0

TIME (MIN)

Fig. 58. Time variation of water depth in Riverside Branch, South-Middle System.

Page 95: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0

0 ;;-

SYMBOL TIME{MIN)

C) 0.000

~I II 2~.381

+ 50.778

X 72.392

~ ~8.Lj12

~-{ 1- 13~.O~3

i

,..... l-lL ....., ~

0 CD

Z -0 H Eo-< I~· 4 H :> 0 r>::I • o 8

'" I

o

f I

g I I I I I I I I I I '1' 0.0 12.0 2'i.0 36.0 'is.0 60.0 72.0 B~.O 55.D l08.0

STATION (NO:)

Fig. 59. Instantaneous hydraulic gradelines.

Page 96: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

::;: ,"

~-1 JD \

:r

0 ..-< 0

X\ ~

'" (Ji LL U 'V

:::s 15 0":

: "~ I- ~

0 I-

0

ill

sr I I I I I I I I ~ I I 00.0 10.0 20.0 30.0 ~O.O 50.0 60.0 70.0 eo.o 90.0 100.0 110.0

TIME (MIN)

Fig. 60. Total inflow hydrograph - Complete Desplain System.

Page 97: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

~+I----~----~ ____ ~ ____ ~ ____ ~ ____ ~~ ____ ~ ____ ~ ____ ~ ____ L-__ ~

0

~,

~

~

.,..... l-LL 'V'~

I~ I-0.... lI..J 0

~ 63

o

!Ii

SYMBOL STATION

C)

1),

+

136 UPSTRE&~ OF BROADVIEW BRANCH 187 L~STREAM END O~ RIVERSIDE BRANCH 207 UPSTREA11 END OF BROOKFIELD BRANCH

o t !I III e e iii ill ill ill i it ~ 1J i i ! ! 91 E!l 6 6 6 6 1 .,; I I I I I

0.0 sa.o 60.0 70.0 eo.D so.o

TIME (MIN)

Fig. 61. Time variation of water depth at upstream ends of branch tunnels -complete Des Plaines System.

100.0 110.0

Page 98: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

~~------------------------------------------------------------------------------

,..... I-­lL.

o

~

o

~

"'" ~ ~ z' C

H

~ ::> f;t:I 0 ,..:i . f;t:I I'l

7

o

~

~I

~o.o

SYMBOL C)

l::.

+ X ~

.".

22.0

TIMECMIN) 0.000

Li6.323 56.351 65.357 71.157 81.517

'N.O 66.0 88.0 llQ.O 132.0 15~.O 176.0 196. C STATION (NO.)

Fig. 62. Instantaneous hydraulic gradelines.

Page 99: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

1

La Grange Park 10

11 19

Fig. 63. 13A tunnel model system configuration.

Page 100: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

~

I-LL '-./

:z 0 1--1

I-cc: > W -1 W

o-r--------~----------~---------L--------~~--------J---------~

o o 0J

o o LJ) ..---i

o o o .-t

0

a IJl

0

0

0

0 IJl

I

0

a 0 ..---i

I

0

0 IJl ......

I

a a 0 0J

I

o.

SYMBOL STATION

75 DOWNSTREAM END

20. ~O. 60. 80. 100.

TIME (MIN) Fig. 6 ~ Time variation of water surface elevation at downstream end,

existing peak flow.

120.

Page 101: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

~

1-LL '-.../

Z CJ 1---1

1-cr > W .----J W

o~--

______ ~ __________ L-________ -L ________ ~ __________ L-________ ~

o o 0J

o o lJ1 ..--t

o o o .-1

0

0 lfl·

0

0

0

0 lfl

I

0

0 0 ..--t

I

0

0 lfl .-t

I

0

0 0 0J

I

SYMBOL STATION

67 DS.61

O. 20. YO. 60. 80. 100.

TIME (MIN) Fig. 65. Time variation of water surface elevation at DS.61, existing

peak flow.

120.

Page 102: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0 I I I I I

0 0 ::r GJ

~

en 0- -LL 0

0

U GJ '-.-/

I- 0- -W 0 -.-l 0

a:J I- .--<

~ C)

0- -L 0

0 CC LIl

W

~ a:::: I- 0- -(j)

CJ

::z 0

:::s: 0J .--<

V 0 0

0_ -L 0

0 C) m a:::: LL

0_ -:3 0 0 0

-.-l (0

LL l-=:) 0- -0 0

C)

M

O~---------'I---------'I----------'-I-------~I~----__ -'Ir-______ ~

C) O. 20. '-10. 60. 80. 100. 120.

TIME (MIN) Fig. 66. Overflow hydrograph from J3A tunnel, existing peak flow.

Page 103: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

~

I-LL '-../

Z 0 I---l

~ CC > W ..--J W

".

C)~---------l--------~--------~L---------L---------~--------1

o o ('\j

o o I.f1 ...-\

o o o .-;

0

0 t.n

0

0

C) 0 I.()

I

0

a a ...-\

I

0

0 I.() .-; . , a a C) ('\j

I

SYMBOL STATION

75 DOWNSTREAM END

O. 20. YO. 60. 80. 100. 120.

TIME (MIN) Fig. 67. Time variation of water surface elevation at downstream end,

future peak flow.

Page 104: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

/""'-.

~ LL '-.../

z: CJ 1----1

J---0= > W ~ W

C)~--------~----------~---------L--------~----------~------__ ~ o o 0J

o

o o o

C)

a Ln

0

0

C) 0 Ln

I

0

a a .-t

I

0

0 Ln .---.

I

a a C) 0J

I

SYMBOL STATION

67 DS· ... 61

O. 20. YO. 60. 80. 100.

TIME (MIN) Fig. 68. Time variation of water surface elevation at DS.61, future

peak flow.

120.

Page 105: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

a I I I I I

a a ::r 0J

~

en 0_ -'(I

LL 0 0

U --' 0J

'--./

f- a-W a ------.J a

m f- ..---I

=:J 0

0- -L a

a CC III

W ..--.

CC f- a- -en 0 z 0

::s: N ..---I

0 0

0- -L a

a C) 01

CC LL

0_ -:3 0 0 0

------.J (0

LL f-==:J 0_ -0 a

a n

0 I I I 1 T

a 0. 20. YO, 60, 80. 100, 120,

TIME (MIN) Fig. 69. Overflow hydro graph from 13A tunnel, future peak flow.

Page 106: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

~

I-LL--'-/

Z C) I--l

I----a:::: > w -1 W

o-+----------~--------~----------~--------~L----------k--------~ o o ('\J

o C)

Ln ~

o o o .-.

0

0 Ln

0

0

0

0 Ln

I

0

0 C) ~

I

0

0 If) ..-1

I

C)

C)

0 ('\J

I

SYMBOL STATION

75 DOWNSTREA11 END

O. 20. ~O. 60. 80. 100.

TIME (MIN) Fig. 7~ Time variation of water surface elevation at downstream

end, dropshaft design capacity inflow.

120.

Page 107: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0

0 0 0J

."

0 'I a

Ln ~

0

0 0 .-.

~ a f- a LL

l.()

'-./

:z C)

0 I---l

I--- 0

cr > w -' 0

W 0 l.() I

0

a a ~

I

0

0 l.() ....... I

a a 0 0J

I

SYMBOL STATION

(') 67 (DS.6 I)

o. 20. l.!o. 60. 80. 100.

TIME (MIN) Fig. 7 I. Time variation of \>later surface elevation of DS .61,

dropshaft design capacity inflow.

120:

Page 108: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

0

0 0 :r 0J

/"-

en 0-

LL 0 0

U ..-I

0J '-../

I- 0-

W 0 --.J 0

CD I- ....-l

:=J 0

0-

L 0 0

CC Ln

W ..-.

CC I- 0-en 0 z 0

:::3=: N ....-l

0 0

0_

L 0 0

0 OJ

CC LL

0-

3:: 0 CJ 0

--.J (0

LL l-:=) ~-0 0

0 {"l

0

0 o.

I I I

\ I I I I I I 20. ~o. 60. 80. 100.

TIME (MIN)

Fig. 72. Overflow hydrograph from 13A tunnel, dropshaft design capacity inflow.

-

-

-

-

-

-

-

120.

Page 109: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS

3~--~~~----~~-----.-------.-------.

--. I-W W IL

IL 0 (f) 0

Hm 200' Z 2 -« (f) :::> 0 I I----I l-e) Z W .....J

.....J 1

w '" z

z :::> Hm I- -

l-lL a: 0

0 0 1 2 3 4 5

AIR CONTENT (PERCENT)

','

Fig. 73. Conditions for dropshaft-drift tube resonance.

Page 110: HYDRAULIC TRANSIENT MODELING OF TARP SYSTEMS