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AD-A121 948 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE COUNTY ILLINOIS i/I HYDRAULIC MODEL I..(U) ARMY ENGINEER WATERWAYS EXPERIMENT STATION YICKSBURG MS HYDRA. R R COPELAND UNCLASSIFIED SEP 82 IES/TR/HL-82-23 F/G 12/2, N
80

AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

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Page 1: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

AD-A121 948 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE COUNTY ILLINOIS i/IHYDRAULIC MODEL I..(U) ARMY ENGINEER WATERWAYSEXPERIMENT STATION YICKSBURG MS HYDRA. R R COPELAND

UNCLASSIFIED SEP 82 IES/TR/HL-82-23 F/G 12/2, N

Page 2: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

TECHICALREPORT HL-82-23

McGEE CREEK PUMPING, STATION SIPHONPIKE COUNTY, ILLINOIS

Hydraulic Model Investigation

by

Ronald R. CopelandHydraulics Laboratory

U. S. Army Engineer Waterways Experiment StationP. 0. Box 631. Vicksburg, Miss. 39180

September 1982Final Report

Approved For Public Release; Distribution UnlimitedA

* - 7

PreeJ for~w U.S ryEgierDsrct t oiSt Lois o.630

82 1201 00

Page 3: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

* Destroy this report when no longer needed. Do not returnit to the originator.

The findings in this report are not to be construed as on officialDepartment of the Army position unliess so deignoted.

by other authorized documents.

The contents of this report are not to be used foradvertising, publication, or promotional purposes.Citation of trade names does not constitute anofficial endorsement or approval of the use of

such commercial products.

Page 4: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

iTUnclassified

SECURITY CLASSIFICATION OF THIS PAGE (Wn Date Entere-- "__ _

READ INSUCTIONSREPORT DOCUMENTATION PAGE BEFORE COMPLETING FOR.REPORT NUMBER 2. GOVT ACCESSIN NO, . RECIPIENT'S CATALOG NUMBER

Technical Report HL-82-23 .D 'q / 5"

4. TITLE (Anld Sublid.) S. TYPE OF REPORT & PERIOD COVERED

McGEE CREEK PUMPING STATION SIPHON, PIKE COUNTY, Final reportILLINOIS; Hydraulic Model Investigation

S. PERFORMING ORG. REPORT NUMBER

7. AUTHOR(e) 8. CONTRACT OR GRANT NUMBER(e)

Ronald R. Copeland

9. PERFORMING ORGANIZATION NAME AND ADORE" S0. PROGRAM ELEME. PROJECT. TASK

U. S. Army Engineer Waterways Experiment Station ARE P ORK UNIT. NME

Hydraulics Laboratory

P. 0. Box 631, Vicksburg, Miss. 3918011. CONTROLLING OFFICE NAME AND ADDRESS 12. REPORT DATE

U.S. Army Engineer District, St. Louis September 1982210 Tucker Blvd, North IS. NUMBER Of PAGES

St. Louis, Mo. 63101 73

W4 MONITORING AGENCY NAME & AODRE *I diffeent -,a. C.,,oll, Office) IS. SECURITY CLASS. (ofa .port)

Unclassified

IS.. DECLA IFICATION/DOWNGRAOINGSCHEDULE

IS. OISTRIBUTION STATEMENT (of hi RePort)

Approved for public release; distribution unlimited.

17. DISTRIBUTION STATEMENT (of Ii. edbeic entered In lock 2. If uffrent hom Repor)

IS. SUPPLEMENTARY NOTES

Available from National Technical Information Service, 5285 Port Royal Road,Springfield, Va. 22151.

IS. KEY WORDS (Cntiwa. on overse side

nl 4cay and Idionilfy by block nmbw)

Hydraulic modelsMcGee Creek Pumping StationPumping stationsSiphons

MASISRAcT (coman -m soverem -- N n.ase aid l~Fy"I by block nuibo)I"A l:4.36-scale hydraulic model of the proposed McGee Creek pumping sta- /

tion siphon was used to develop a design with adequate hydraulic performance.

The saxophone outlet design was modified to ensure maintenance of the primingseal. Priming times and head losses were measured in the model. Modificationsto decrease priming times were tested, including a reduced cross-sectional area

at the crown, and air escape vents. The recommended design siphon operated

satisfactorily for the entire range of expected tailwaters and discharges ,4

t Nm Unclassified

SICURITY CLASSIFICATION OF ThIS PAIAGE (Mm Doat Entere.)

S, , ww.

Page 5: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

UnclassifiedMuucum CLANNFICATI OF THIS PASS(Nm shom Da

r

Unclassified* SUCUmiT CLASMIPCATI OF THIS PAeGWIW. DO& BDame.

w 0 w IV 0 IV V V V V

Page 6: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

PREFACE

The model investigation of the McGee Creek puamping station siphon

* reported herein was authorized by the U. S. Army Engineer District, St.

Louis (LRS), on 13 January 1981.

This investigation was conducted during the period January 1981 to

January 1982 in the Hydraulics Laboratory of the U. S. Army Engineer

* Waterways Experiment Station (WES), under the direction of Mr. H. B.

*Simmons, Chief of the Hydraulics Laboratory, and Hr. J. L. Grace, Jr.,

* Chief of the Hydraulics Structures Division, and under the general

* supervision of Mr. N. R. Oswalt, Chief of the Spillways and Channels

Branch. The project engineer for the model study was Hr. R. R.

Copeland, assisted by Hr. E. L. Jefferson. Hr. E. B. Williams is

acknowledged for his work in constructing the model. This report was

* prepared by Hr. Copeland.

During the course of the study, Messrs. James Luther, Walter

Wagner, and Ben Venturella of LHS; Emil Cook and Mark Wagner from the

* consulting firm of Crawford, Murphy and Tilly, Inc.; Joe McCormick,

Larry Eckenrod, Larry Cook, and Roddis C. Randall of the Lower His-

sissippi Valley Division; and John S. Robertson of the Office, Chief of

* Engineers, visited WES to discuss the program of model tests, observe

the model in operation, and correlate test results with concurrent de-

sign work. -

Commanders and Directors of WES during the conduct of this in-

* vestigation and the preparation and publication of this report were

COL Nelson P. Conover, CE, and COL Tilford C. Creel, CE. Technical

Director was Hr. F. R. Brown.

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CONTENTS

Page

PREFACE. .. ............. .................

CONVERSION FACTORS, U. S. CUSTOMARY TO METRIC (SI) UNITS OFMEASUREMENT. .. ............. ............. 3

PART I: INTRODUCTION .. ...... ................ 5

The Prototype........................5Purpose of the Model Study...................6

*PART II: THE MODEL .. ............. .......... 8

Description. .. ............ ............ 8Interpretation of Model Results .. ....... ....... 10

*PART III: TEST RESULTS. .. ............. ....... 13

Method of Operation. .. ............. ...... 13Original Design Siphon. ...... ............. 14Experimental Outlet Designs .. ...... ........... 15Recoimmended Outlet Design. .. ............ .... 17Head on the Saxophone Outlet .. ............. .. 20Operating Head Losses. .. .............. .... 20Priming Characteristics. .. ............. .... 22Air Escape Vents .. .............. ....... 24Effect of Reducing Cross-Sectional Area at Siphon Crown . .. 27Pressure Regulation with Air Vent .. ...... ....... 31Velocity Distributions Upstream from Outlet .. .... .... 32

PART IV: CONCLUSIONS .. .............. ....... 33

REFERENCES. ....... ................ ..... 35

TABLES 1-6

* PHOTOS 1-6

PLATES 1-25

2

Page 8: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

CONVERSION FACTORS, U. S. CUSTOMARY TO METRIC (SI)UNITS OF MEASUREMENT

U. S. customary units of measurement used in this report can be con-

verted to metric (SI) units as follows:

Multiply BY To Obtain

acres 0.4047 hectares

cubic feet per second 0.02831685 cubic metres per second

Fahrenheit degrees * Celsius degrees orKelvins

feet 0.3048 metres

feet of water 0.03048 kilograms per squarecentimetre

feet per second 0.3048 metres per second

inches 25.4 millimetres

miles (U. S. statute) 1.609344 kilometres

*To obtain Celsius (C) temperature readings from Fahrenheit (F) read-ings, use the following formula: C = (5/9)(F -32). To obtain Kelvin(K) readings, use: K =(5/9)(F -32) + 273.15.

3

AP _V - 1P 9 W W W 9 9 9 a

.~~~~ .. .o . . . . .

Page 9: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

IA CHICAO

PEORIA

SSEWOMINGTO4

$PROJECT AREACASOUT

MEREDOSIA I YILLINOIS EXISTING LEVEE MORGAN COUNTY

ALTON *VANOALIAMISSO&R, EAST ST LOUIS

ST. LOUIS MT. CARMEL

MEREDOSIAmo ESTER TC 4 .. ISLAND

CAIRM

SCALE

VICINITY MAP 499 -N-

BROWN COUNTY. McGEE CREEK DRAINAGEA

PROPOSED McGEE CREEK EREDOSIA

QCHAMBERSBURGfXIS TING GRAVITY DRAIN

EXISTING DITCHES-ST(CTREOB

SFRCTR MTOE CREE

PROJECT LOCATION

FigreDOI 1. Latinma

SCL

If 200 0~ 200 4000FT

Page 10: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

McGEE CREE PUMPING STATION SIPHON

PIKE COUNTY, ILLINOIS

Hydraulic Model Investigation

PART I: INTRODUCTION

The Prototype

1. The proposed McGee Creek pumping station is to be located in

*west central Illinois, in the northeast corner of Pike County. The site. l* is located on the vest bank of the Illinois River about 1 mile* west of

*Meredosia, Illinois, and about 52 miles west of Springfield, Illinois

(Figure 1). The pumping station is part of a flood-control project

that will provide protection to approximately 12,200 acres of predomi-

nantly agricultural lands in the McGee Creek Drainage and Levee

District.

2. An existing pumping station and gravity-flow structure cur-* rently provide limited flood protection to the McGee Creek Drainage and

Levee District. These structures cannot maintain a sufficiently low

groundwater elevation during the growing season due to seepage through

the Illinois River levee and rainfall runoff. Overbank flood damages

* begin at el 422.7,** and high water-table damages to crops begin at

el 420.7. The existing pumping station has a capacity of 196 cfs and

has maintained a mean annual flood elevation of 424.2 over a 40-year pe-

riod of record. The gravity-flow drain is essentially useless, except.

during winter months when water levels in the ditches are allowed to W

rise above those maintained during the growing season. The existing

station will be demolished after completion of the new pumping station.

3. The proposed pumping station will have three vertical

*A table of factors for converting U. S. customary units of measure-ment to metric (SI) units is presented on page 3.

* ** All elevations (el) cited herein are in feet referred to the Na-tional Geodetic Vertical Datum (NGVD).

5

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IF-4

propeller-type mixed or axial flow pumps operating with siphonic re-

covery. Design discharge for each pump at high operating heads is

107 cfs; at a low operating head, the expected discharge for each pump

is 133 cfs. Minimum priming discharge is 89 cfs. Discharges will vary

depending on the operating head and the pump characteristics. The first

* pump will be started when the water level in the sump reaches el 419.5,* the second at el 420.5, and the third at el 421.5. Pumps will be shut

off with sump water surfaces at el 420,5, 419.5, and 418.0. The pro-2

posed pumping station would maintain a mean annual flood elevation of

420.9. The mean number of pumping days required annually would be re-

duced from 153 to 67, and the mean number of days requiring full pumping

capacity would be reduced from 95 to 23 days annually.

4. Three 48-in. -diam steel discharge pipes will convey flow from

* the pumping station, over the levee, and into the outlet structure and

Illinois River. The inside of the pipes will be coated with coal-tar

epoxy enamel. An air vent will be located at the crown or summit of the

* siphon. The vent will be opened to relieve positive pressures that ac-

company pump start-up and then will be closed to initiate priming. Whenthe pumping operation is completed, the air vent will be opened to break

the siphon and prevent backflow. At the outlet, in order to provide a

* priming seal, the discharge pipe will be turned upward like the bell of

* a saxophone--hence the name saxophone outlet. Elevation of the outlet

determines the maximum negative pressure that will occur in the primed

siphon. Negative pressures in excess of 28 ft of water may cause cavi- -

tation or result in excess leakage at pipe joints. The adverse slope of

the saxophone outlet will direct flow upward. Energy of the efflux: will

be dissipated on a concrete capstone and riprap-bedded outlet channel.

Tailwaters in the outlet channel will range between el 419.0 and 449.5.

Purpose of the Model Study

5. Design guidance for pumping station siphons is generally lack-

ing. Pumping station siphons differ from siphon spillways (which are

* capable of rapid increases in discharge and for which there is

6--

[7 2 U U U U U U

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.. . . .. "

considerable design guidance) in that discharge of pumping station

siphons is limited by the relatively constant capacity of the pump.

This makes it essential that the siphon prime with the minimum discharge

capacity of the pump and that "washout" be prevented with the maximum

discharge capacity of the pump prior to priming. Also, friction losses

are typically more important in pumping station siphons and form losses

are more important in siphon spillways. Problems with priming pumping

station siphons may be due to insufficient air entrainment, inability to

transport the entrained air out of the siphon, and/or washout of the

" priming seal.

6. The original siphon design was analyzed by engineers of the

Hydraulic Structures Division at the U. S. Army Engineer Waterways Ex-

periment Station (WES). Preliminary calculations (with an unsubmerged

outlet and the maximum discharge expected at the start of priming) indi-

cated that the hydrostatic head provided by the saxophone outlet would

be insufficient to resist the momentum forces of the supercritical flow

coming down the riverward leg of the discharge pipe. Therefore, a hy- -.

draulic jump could not form in the discharge pipe and there would be no

priming seal. Without siphonic head recovery, the pumps proposed for

the McGee Creek pumping station would be unable to deliver the design

discharge. The model investigation was therefore recommended and con-

ducted to study the hydraulic characteristics of the siphon and to de-

velop a satisfactory design of siphon that will ensure maintenance of

the priming seal and adequate priming characteristics.

7-

- - ---.-- °

""-2

.. 4

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- . .. . - . - - - - -4-a.I -7i.

PART II: THE MODEL

Description

7. The McGee Creek pumping station siphon was modeled at an un-

distorted linear scale of 1:4.36. The entire 397-ft-long siphon was

simulated from the prototype pump location to the saxophone outlet. The

-model was constructed of transparent plastic pipe so that hydraulic flow

;. conditions could be observed. Air vents located on the siphon crown

. were also simulated. The saxophone outlet discharged into a tailbay of

sufficient height to allow testing with the full range of expected

tailwaters. The tailbay had a large window so that flow conditions in

the saxophone outlet could be observed. Flow through the model was

recirculated by centrifugal pumps. Discharge was measured with a

paddle-wheel flowmeter and displayed electronically. Flow rates were

controlled by an automatic valve. An overall view of the model is shown

in Figure 2. .

Figure 2. 1:4.36-scale model of pumping station siphon

8. Hydrostatic pressures were measured at 48 locations in the

model with piezometers and at one location with an electronic pressure

cell mounted flush with the bottom of the pipe. Locations of the piezom-

eters are shown in Plate 1; the piezometer board and control panel are

shown in Figure 3. At each piezometer station, two taps were made in

the pipe. On the landward (upstream) portion of the siphon, these taps

were placed on each side of the pipe at middepth. On the riverward

(downstream) portion of the siphon, the taps were placed 45 deg from the

vertical center line in the bottom quadrants of the pipe. The two

8

0 - S • 0 9 0 9 I w w V S W

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-. ....... .. .. . . 2

Figure 3. Model piezometer board and control panel

piezometer taps at each station were connected so that the reading repre-

sented an average pressure. The electronic pressure cell was located at -

sta 0+63 which was far enough downstream from the prototype pump loca-

tion to avoid any significant flow disturbances that were introduced by

the 90-deg flow curvature entering the siphon. The pressure cell was

used to measure instantaneous pressure fluctuations due to hydraulic

forces that would be expected to occur at the prototype pump location.

In the model investigation of the Pointe Coupee pumping station siphon

conducted by WES (Copeland 1982), it was determined that pressure

9

* .O -9 9 9 9 9 9 9 9 9 3 3

Page 15: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

fluctuations due to vibration of the model's pumps and the model itself

had a much higher frequency than the pressure fluctuations due to hy-

draulic forces. The high-frequency fluctuations were filtered electron- --

ically so that only the frequency fluctuations related to hydraulic

forces were recorded. The piezometers were used to measure the average

* hydrostatic pressure and the electronic pressure cell was used to mea-

sure instantaneous pressure fluctuations.

9. Air flowed into the siphon through one of the air vents at

the siphon crown and airflow was measured with a hot-wire anemometer.

The air vent diameters were geometrically similar to those in the proto-

type. The air vent was extended sufficiently to ensure uniform velocity

distribution at the point of velocity measurement.

Interpretation of Model Results

10. The principle of dynamic similarity, which requires that the

ratios of forces be the same in the model and prototype, is the basis ....

for the design of models and the interpretation of results. The hydrau-

lic performance of a siphon is affected by inertial forces (forces re-

sulting from changes in the magnitude or direction of the velocity),

.. gravitational forces, viscous forces, and surface tension. It was not

practical, in this case, to conduct a model investigation in which all

of the forces influencing flow were scaled correctly. However, during

certain operating conditions when fundamental flow characteristics are

the same in the model and prototype systems, the differences in force

• "ratios are negligible or can be accounted for by calculating adjustments

to the model results. For other operating conditions, these forces are

not negligible and only qualitative model results are possible. Qualita-

tive model investigations are useful in evaluating the merits of one de-

sign against another. Hydraulic conditions of primary interest in this

model study are influenced predominantly by gravitational and inertial

forces; therefore, the model was constructed and operated based on theFroudian criteria.

11. When the siphon is flowing full (after being primed), the

forces influencing hydraulic performance are gravity, viscosity, and

76

10

-

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inertia. It is the gravitational and inertial forces that predominate

" at the outlet where flow is discharged into the outlet channel and the

viscous and inertial forces that predominate in the pipe itself. It

has been established by several investigators involved in siphon model --

studies (Gibson, Aspey, and Tattersall 1931; Whittington and Ali 1972)

and is generally accepted (Naylor 1935; CBIP 1956; Babb, Amoracho, and

: Dean 1967; Head 1975) that if the Reynolds number of flow in the model

* exceeds 1.8 x 105, then in cases where friction is negligible, the

viscous scale effects will be negligible. When friction losses are not

negligible, adjustments to the model or to the model results can be made

to account for scale effects due to friction. Thus, if the model is

constructed large enough so that the Reynold's number of flow exceeds

1.8 X 10 then viscous effects are insignificant and the Froudian cri-

teria may be applied. The Reynolds number of flow ranged between1.8 x 105 and 7.9 x 10 in the McGee Creek siphon model tests.

12. When the siphon is flowing partially full (with the air vent

at the crown open or during priming), hydraulic performance is influenced

by the forces of gravity, viscosity, inertia, and surface tension. The

process of air entrainment by the hydraulic jump has been shown to be

primarily a function of the Froude number and pipe slope (Kalinske and

" Robertson 1943; Kent 1953; Renner 1975; Wilhelms et al. 1981). When the

pipe downstream from the hydraulic jump is horizontal or is sloping up- - -

ward, most of the air entrained by the jump is removed from the pipe

(Falvey 1980). However, when the pipe slopes downward, the process of'

air transport downstream from the jump becomes important. This process

- is highly influenced by surface tension and viscosity. The entrained

air bubbles will have approximately the same still water rise velocity

in the model and prototype (Ervine and Elsawy 1975), giving a nonscaling

of air transport. Several investigators have observed significant scale

effects in the air transport in siphon models (Naylor 1935; CBIP 1956;

Babb, Amorocho, and Dean 1967; Ervine and Elsawy 1975; Thatcher andS

Battson 1975; Copeland 1982).

13. Due to the scale effect in modeling air transport in siphons,

priming times will be longer in the model and the ability to maintain

11

* 9 0 "9 S U 9 9 3 3 6 6 6 6 6 • "

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* the priming seal at pump start-up may be overestimated. With respect to

* priming time, if adequate priming action exists in the model, then it is-

* safe to conclude that the prototype priming action will be at least as

* good and probably better. With respect to maintaining the priming seal,

* the model scale effect will have an opposite impact. If more air is en-

trained in the prototype, then the weight of the water and air column,

which holds the hydraulic jump in the siphon, will be reduced. If this

weight is reduced significantly the priming seal will wash out of the

* siphon. Model scale effects related to washout are not as critical in

* this case as might be imagined because the pipe slopes upward in the2- saxophone outlet downstream from the hydraulic jump; and air entrainment* is primarily a function of the Froude number of flow. It remains prudent

to provide a safety factor in designing for washout when the design is

based on model results. Scale effects associated with siphon modelingI

are reduced as the size of the model is increased. To date, research

* has not established an appropriate scale to adequately model siphon

* priming or washout, and model results must be interpreted with care.

14. The general relations expressed in terms of the model scale

or length ratio are as follows: -

Dimension Ratio Scale Relations

Length Lr L 1:4.36

r

Time Tr L" 1:2.09 .r

Prssuare P L 521:4.6r

Frequency F r= L1 1 1:0.479

Values for water discharges, velocity, hydraulic grade line, and pres-

sure fluctuation can be transferred quantitatively from model to proto-

type by means of the scale relations above; values for priming timne and

* air discharge can only be transferred qualitatively. Unless otherwise

noted, all results reported herein will be in prototype units.

12

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PART III: TEST RESULTS

Method of Operation

15. Discharges simulated in the model ranged between 44 and

202 cfs; tailvaters ranged between el 419.0 and el 449.5. To study2priming characteristics, the discharge was set with an air vent at thesiphon crown opened. Priming was initiated by closing the air vent.

The priming operation was timed with a stopwatch. The siphon was con-

sidered to be primed when all the air was removed from the downward

sloping portion of the siphon. Discharge was checked at the end of each

test; no significant changes were noted. Several priming operations

were simulated where the discharge increased as the head decreased.

Head-discharge relationships for these simulations were taken from the

possible pump characteristic curve shown in Plate 2. For these simula-

tions, discharge was increased by manually operating the regulating

valve on the model so that the simulated discharge corresponded approxi-

mately to the head measured from the piezometer board and expected for

the pump characteristic curve. These simulations were not intended to

reproduce actual prototype priming times but were intended to develop a

comparison between priming times with constant and varying discharges.

- . To study the capability of the siphon to maintain a priming seal, thesaxophone outlet and upstream pipe below the outlet elevation were

filled with water by allowing a very small flow in the siphon. It is

important that the outlet be filled with water before any significant

flow comes through the siphon, because if the outlet is empty the super-2critical flow coming down from the crown may have sufficient momentum toflow out of the saxophone outlet without forming a hydraulic jump and

% priming seal. Once the outlet was full of water, discharge could be in-

creased to simulate possible prototype priming discharges. Washout

tests were run with the air vent at the siphon crown opened. Discharge

was increased in steps until the priming seal was washed out of thesiphon.

132

...........7

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77-4

Original Design Siphon

16. The original design siphon consisted of a 397-ft-long, 4-ft-

diam pipe that extended from the pumping station, over and down the levee

slope, to the outlet channel and the Illinois River. Three air vents

were located at the siphon crown. At the outlet, the pipe turned upward

at a 45-deg angle to form the saxophone outlet. The outlet was set at

el 427.5 to limit the negative pressure in the siphon crown to 28 ft of

water. Negative pressures in excess of 28 ft of water would probably

cause cavitation. The type 1 (original) design siphon is shown in:i Figure 4.

40, I I I I I I I I I J"""0

~460

4I-

NOE PIP"DIAMTERONSTNT- FT 2.)

Fgr4.TEL 452. 8 MITERED- r(FIGURE 9)

"EL 426.7420 - EL 421.8-0 EL 421.5 -

NOTE: PIPE DIAMETER CONSTANT 4 FT

40 40 Wo 120 180 200 240 290 320 39o 400DISTANCE FROM PUMP," FT .. ,-;-

"" ~Figure 4. Type I (original) design siphon".i;.- '

17. It was determined in the model that the priming seal wouldwash out of the type 1 (original) design siphon at discharges greater '

than 102 cfs when the tailwater was below the outlet. Maximum discharges(pump capacity) expected before the start of priming ranged between

89 and 140 cfs depending on the sump water-surface elevation and the par-

ticular performance curve of the pumps finally acquired for the pumping

station. In order to ensure maintenance of the priming seal for the max-f..

imum anticipated priming discharge, the hydrostatic head on the outlet

was increased. This could have been accomplished by raising the outlet

14

IF _W_-,- -9 9

Page 20: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

B"

elevation or by lowering the horizontal portion of the pipe upstream

from the outlet. Raising the outlet elevation would decrease the amount

of siphonic recovery that could be realized at low tailwaters for normal

(primed) operations; therefore, lowering the horizontal portion of the

outlet pipe was the preferred solution.

Experimental Outlet Designs

18. The effect of raising the elevation of the outlet on washout

of the priming seal was determined in the model. Although this was not

the preferred solution to the washout problem, model revisions were rela-

tively simple and the results could be used to estimate how much the

horizontal pipe should be lowered. The elevation of the type 1 design

outlet was increased by 1, 2, and 4 ft in the model investigation. With

the outlet raised 1 ft to el 428.5, washout occurred with discharges

greater than 133 cfs. With the outlet at el 429.5 washout occurred at

discharges greater than 155 cfs. When the outlet was raised 4 ft to

el 431.5, washout did not occur with a discharge of 220 cfs, which is

the maximum discharge that could be simulated in the model. The progres-

sion of the hydraulic jump toward washout with increasing discharge as

determined in these tests is shown in Plate 3.

19. The effect of raising the outlet elevation a specific dis-

tance will not be the same as lowering the horizontal section of pipe

upstream from the outlet the same distance. Lowering the pipe will in-

crease the flow momentum upstream from the hydraulic jump so that a

greater hydrostatic head will be required at the outlet to contain the

same discharge. Results of the tests with increased outlet elevations,

therefore, provided only a general idea of what to expect if the pipe

was lowered.

20. The horizontal pipe upstream from the outlet was lowered 2 ft -

to el 419.5 in the type 2 design siphon (Figure 5). Center line of the

outlet remained at the same station as in the type 1 design siphon so

that the length of the horizontal pipe was shortened, but the total

length of the siphon remained the same. The new elevation for the

horizontal section of the pipe was based on the subject model tests with

W

15

S~ ~ 9 0 -v W------------------------------------------------------------------- ---....-. •

Page 21: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

460

,C,

Z 45DEG -,U.40 MITERED -:.:

EN

) FLOW,. // EL 452.8 \%BN-7 (FIGURE 9)

LUw EL 426.0 EL 426.7420 -:.¢2

NOTE: PIPE DIAMETER CONSTANT 4 FT EL 419.8 EL 419.5

0 40 80 120 160 200 240 280 320 360 400 440DISTANCE FROM PUMP, FT

Figure 5. Type 2 design siphon

the raised outlet elevations and on determinations by engineers from the

St. Louis District that soils and structural considerations limited low-

ering the pipe to el 419.5. It was determined by model testing that dis-

charges greater than 133 cfs would wash out of the type 2 design siphon.

This value is slightly less than the required design value of 140 cfs.

21. In order to increase the hydrostatic head provided by the

outlet, a 90-deg saxophone outlet was used in the type 3 design siphon.

• :With this modification, the center line of the outlet remained at the

same station as in the type 2 design siphon, which resulted in a longer

portion of horizontal pipe. In the model, the priming seal did not wash

out of the type 3 design siphon at a discharge of 220 cfs (maximum that

could be simulated in model). The type 3 design siphon eliminated the

washout problem but resulted in increases in head losses. At the pump,

heads with the type 3 design siphon were 0.6 ft greater with a discharge

*- of 107 cfs and 1.3 ft greater with a discharge of 133 cfs than the heads

"" measured with the type 1 design siphon.

22. Hydraulic conditions were more severe in the model tailbay

with the 90-deg outlet than with the 45-deg outlet when the tailwater was

below the outlet. The jet trajectory was considerably shorter with the

90-deg outlet and there was more turbulence and surface wave action. In

addition, there is a greater thrust on the pipe with a 90-deg saxophone

16

-- " 0 -0 a a 1 1P a P 0 0 ".. .. . . .. . .-....". ,-. " "7- 7 7 " - --7-7 -7 - - - 7 -7 . .... ..- -= ....7 . . . ..= .. .

Page 22: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

* outlet and flow from the outlet falls on the pipe and pipe supports up-

stream from the outlet. Engineers from the St. Louis District determined

that these adverse conditions could be accounted for in the structural

* design.

23. In the type 4 design siphon, the 90-deg outlet elevation was

*lowered 1 ft to el 426.5. This modification would decrease the head at

the pump for tailwaters below el 426.5 but would have no significant ef-

fect when the outlet was submerged. At low tailwaters, the head at the

pump with the type 4 design siphon was 0.6 ft less than that observed

with the type 3 design siphon with discharges of 107 and 133 cfs.

Recommended Outlet Design

24. A 60-deg saxophone outlet at el 427.5 was used in the type 5

* design siphon. This design was capable of mnaintaining the priming seal

* and resulted in a smaller total head on the pump for the operating range

of discharges than either the type 3 or 4 design siphons. The ability

of the various designs tested to hold the hydraulic jump and maintain

* the priming seal is shown in Figure 6. Increasing the distance between

the outlet elevation and the horizontal pipe provided a larger hydro-

*static head which held the hydraulic jump at a greater distance from the

outlet. This effect is demonstrated by comparing the type 1 and the

type 2 design siphons which both had 45-deg outlets with the type 3 and 4

the type 4 design siphons which both had 90-deg outlets. The distance

* between the outlet and the pipe was more important than the angle of the

saxophone in determining the position of the hydraulic jump as can be

seen by comparing the type 2, 3, and 5 design siphons. However, the

angle of the saxophone appears to be the most significant factor in de-

* termining the ability to maintain the priming seal. The steeper outlets

* were aided by flow dropping back onto the outlet. This feature made it

unnecessary to fill the saxophone outlet and upstream pipe below the out-

let elevation because the backflow caused the priming seal to form even

when the pipe was empty. The model facility did not have sufficient dis-

charge capacity to determine actual washout discharges for the 60- and

* ii I7-1 4P 19 . V 0 . 0 40,

Page 23: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

380

370STTO

u 350

340 PRIMING SEAL WASHOUT.z

:0 TYP 1,-.

P 330-TYE2,3520 -

ANGLE EL OUTLET EL PIPE (

- 310 - TYPE 1 457 427.5 423.5340 TYPE 2 450 427.5 421.530 -_ o TYPE 3 9 427.5 421.5

" TYPE 4 900 426.5 421.5cca 290 TYPE 5 600 427.5 421.5

28040 50 60 70 80 90 100 110 120 130 140 150 160 170 180 190 200 210 220

DISCHARGE, CFS

Figure 6. Progression of hydraulic jump toward outlet

with increasing priming discharge

90-deg outlets. Total heads on the pump for the various designs with

the tailwater below the outlet are compared in Figure 7. With the mini-

mum operating discharge of 107 cfs, the type 5 design siphon provided

about the same total head on the pump as the type 4 design siphon and

about 0.6 ft less than the type 3 design siphon. With a normal low head

operating discharge of 133 cfs, the type 5 design siphon provided about

0.6 ft less than the type 4 design siphon and about 1.2 ft less than the

type 3 design siphon. The type 5 design siphon provided the best combi-

nation of low head losses and ability to maintain the priming seal of

the designs tested in the model."0

25. The amount of siphonic recovery (decrease in head elevation

at the pump due to siphonic action) is limited to a maximum allowable

negative pressure of 28 ft of water to prevent cavitation that could

occur in the siphon when the pressure reaches the vapor pressure of

water. The maximum negative pressure will occur at the point on the si-

phon with the highest elevation. The average maximum negative heads at

the crown for the various siphon designs are compared in Figure 8. With

18

.. . . - . U - - -

Page 24: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

442

o TYPE 1o TYPE 3

440- TYPE 4

* TYPE 5

438

z TYPE 4U. 436z TYPE 3

> 434-1"'l wTYPES I & 5

X 432

430- V

428 ,-"0 50 100 150 200 250

DISCHARGE. CFS -V.

Figure 7. Total head elevation at pump withtailwater below outlet

r4

• TYPE 4

p 28-

z<

26

o TYPE24 ITYP3TYPE4 I

o TYPE 5

< 22 I I I i " -.0 50 100 150 200 250

DISCHARGE. CFS

Figure 8. Average maximum negative head at siphon crownwith tailwater below outlet and siphon primed

V 0 0 0 a 4 0 1111 S .

Page 25: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

* the type 5 design siphon and the minimum operating discharge of 107 cfs,

the average maximum negative pressure was 27.4 ft of water. The actual

maximum negative pressure will be somewhat lower than the average value -@-

due to the nonuniformity of the velocity and pressure distributions at

the crown.*

Head on the Saxophone Outlet

26. The effective hydrostatic head at the saxophone outlet for

normal (primed) operating conditions with free discharge was determined

for the various outlet designs by extrapolating the pressure profile

from upstream of the outlet (Plates 4-7). The effective head includes

head losses due to the double mitered bend in the saxophone outlet.

This procedure was used because the velocity and pressure distributions

are distorted in the saxophone outlet, and the effective hydrostatic

head on the system cannot be readily determined by the piezometers. The

effective head on the 90-deg outlets wis higher because of higher bendlosses and because the effective tailwater created by the direction of

the jet trajectory was greater. The effective heads on the 60- and

45-deg outlets were similar. The additional bend loss that would nor-

mally be expected with a greater flow angle change was apparently offset

by the longer interior mitered section used in the 60-deg outlet. The

saxophone outlet designs tested are shown in Figure 9 and the effective

hydrostatic heads are shown in Figure 10.

Operating Head Losses

27. The model was used to estimate the total head that the -,,up .

* would be operating against at the beginning of priming, at tailwaters be-

low the outlet elevation of 427.5, and at tailwater elevations of 435.0,

442.0, and 449.5. The hydrostatic head and pressure fluctuation at vari-

ous locations along the siphon were measured using piezometers. These

data were plotted and the profile extrapolated to sta 0+00, which is the

location of the prototype pump (Plates 8-12). The head determined in

the model was reduced to account for frictional differences in the model

20

p p - Ip Op 0 Ip a Ip Ip p p Ip ap1

Page 26: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

TYPE I

E~~~~E 427.5. TP 2E 4.

400

EL 3.5.

TYP 3.5YPFiur 90. MITphoeotestse

0LL

0

0X

TYPE 3u2.0 900 MITER

I-W

00 1.5-

w .o 450 MITER

0.50 DISCHARGE, CFS 20

Figure 10. Effective hydrostatic head on saxophone outlets

Page 27: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

1 - *1and prototype. The model was assumed to be a smooth pipe with Darcy-

Weisbach friction factors between 0.016 and 0.012. The prototype fric-

tion factors ranged between 0.012 and 0.013 and were determined for a

k value of 0.0003 ft as recommended in HDC Sheet 224-1/1 (USA, CE 1968)Sfor steel pipes with tar coating. Results of the procedure used to ad-

just for frictional differences are shown in Table 1. Calculations for

the adjusted heads and hydraulic grade line elevations at the pump for

various discharges are shown in Tables 2-6; results are plotted in

Plates 13-17.

28. The primary function of this model investigation was to study

the siphon's priming characteristics and washout potential, a phenomenon

governed primarily by gravity forces. When the siphon is primed, vis-

cous forces become more important. In order to use the model to esti-

mate head losses in the siphon, it was necessary to make adjustments tothe data to account for incorrectly scaled roughness elements. The as- -.

sumptions required to make the necessary adjustments render the results

only as reliable as normal hydraulic calculations used to determine head

losses in a closed conduit.

Priming Characteristics

29. Hydraulic characteristics in the siphon during priming are

shown in a series of photographs (Photos 1-6) for a constant discharge

of 120 cfs. In Photo 1 the air vent at the siphon crown is open and the

hydraulic jump (not visible due to outlet flume) is stationary just up-

stream from the outlet. Initially, the air vent is opened in order to

relieve the positive pressure that accompanies pump start-up. When the

air vent is closed, the priming process begins. The hydraulic jump en-

trains air that must be transported down the pipe by the flow. Ini-

tially, air removal is rapid and the hydraulic jump moves quickly up the

4 siphon (Photos 2 and 3). As the distance required for air transport in-

creases, the air removal rate decreases. Large air pockets form down-

stream from the jump (Photo 4) and move upstream, eventually blowing

through the hydraulic jump. When this happens, the hydraulic jump moves

22

* S S S S S S S S S U U S S U

Page 28: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

slightly downstream so that the general upward progress of the jump is

characterized by pulsations. As the hydraulic jump nears the siphon

crown, only a small percentage of the air entrained by the jump is ac-tually transported out of the siphon (Photo 5). Air bubbles entrained

by the hydraulic jump eventually rise to the top of the siphon and form

small air pockets. These air pockets will continue to move downstream

* as long as the drag forces provided by the flow are large enough to over- -

come their buoyant forces. The final stages of priming are characterized

* by a steady train of small air pockets moving upstream and air bubbles

being gradually transported downstream out of the siphon. The primed

siphon is shown in Photo 6. Due to the hydraulic characteristics of the

priming process, the siphonic recovery is rapid during initial phases of

* priming and much slower during the final stages of priming.

30. Priming times were measured in the type 5 design siphon with

constant discharges and a range of tailwaters. Results of these tests

* indicated that tailwater had an insignificant effect on priming time

* when the discharge was constant. It was also apparent that when the dis-

charge was less than about 110 cfs, priming times increased signifi-

cantly with small decreases in discharge. Priming times determined in

these tests are shown in Figure 11 and are presented in prototype units;

however, duration of the priming phase determined by model tests is

greater than would be expected in the prototype. The prototype siphon

will prime faster because, during priming, the discharge will be in-

creasing as the head on the pump decreases; whereas in the model tests,

* the discharge was held constant. This effect will be significant at low

tailwaters but much less significant at high tailwaters where the air

removal and siphonic recovery rates are slower. In addition, the

priming times determined in the model study may be greater than in the

prototype because the air entraining and air transport capabilities of

* the model may be somewhat less than the prototype due to scale effects.

Thus, the model test results cannot be transferred quantitatively to the

prototype and must be interpreted with care.

23 '190 V No *fS 40 10 1P V W W

Page 29: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

120

110

100

90-z TAILWATER EL 449.5

so TAILWATER EL 438.570 -a TAILWATER BELOW OUTLET70 EL 427.5

~60

S50

. 3:- - '.: 7CL 40

30

20

10

80 100 120 140 160 180 200

DISCHARGE, CFS

Figure 11. Priming times for constant discharges,variable tailwaters, type 5 design siphon

Air Escape Vents

31. The effect of an air escape vent on priming characteristics

was determined in the model. An air escape vent could L~e 4ocate@ ,e the

downstream (riverward) leg of the siphon to assist priming with high

, tailwaters. Its purpose is to shorten the distance required for trans-

port of entrained air and to reduce the upstream movement of air pockets

* that have buoyant forces greater than the drag forces provided by the

- flow. Elevation of the air escape vent must be below the hydraulic

grade line in the siphon conduit or it will act as a siphon breaker. In

addition, if the hydraulic jump is located below the vent station at the

start of priming, the vent must be closed until the hydraulic jump has

* moved upstream past the vent station. Operation of the air escape vent --

" which is operated during priming is illustrated in Figure 12. Effec-

tiveness of the air escape vent is a function of its location on the

24

a V

,. .

[ < . " > ' : ' - ' '- . : -: °. - : ' -. . " . ... .".•-

Page 30: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

AIR ESCAPE VENT CLOSED AT START OF PRIMINGBECAUSE HGL IS BELOW VENT ELEVATION.

AFTER T MINUTES. HGL IS GREATER THANVENT ELEVATION AND AIR ESCAPE VENT IS OPENED

AIR ,HYDRAULIC GRADE LINE (HGL) T MINUTES1 ESCAPE /AFTER START OF PRIMING--

VENT (INCREASE IN SLOPE DUE TO INCREASE

HIHYDRAULIC JUPLAISLOCATION AFTER "G. A,,T STR OF PRIMING

REDUCED HEAD ELEVATIONAFTER T MINUTES RESULTS "IN INCREASED DISCHARGE kHYDRAULIC JUMP LOCATION " '

CAPABILITY FROM PUMP AT START OF PRIMING

Figure 12. Operation of air escape vent

siphon. If the vent is at a higher location on the siphon, air will be

removed faster and priming times will be reduced; however, the tailwater

must be higher for the vent to function. The frequency of high tail-

water is an important consideration in deciding whether an air escape

vent should be provided or not. Air escape vents at representative ele-

vations of 435.0 and 442.0 were tested in the model with a range of. ,. ,i.

tailwaters.

32. Effects of the air escape vents on priming times for con-

stant discharges were compared in the model with a tailwater elevation

of 445.0. The vents significantly reduced priming times at the lower

discharges which are representative of expected priming discharges

*: (Figure 13). The vent at el 442.0 was more effective than the vent at

el 435.0; operating both vents did not result in a significant improve-

ment in priming conditions. In these tests, priming was considered com-

plete when all the air was removed from the siphon.

33. The amount of time required for complete priming at low

discharges may be excessive; but under certain conditions, significant

partial priming or siphonic recovery may occur rapidly. The model was

used to determine siphonic recovery at various times after the start

of priming for a constant discharge of 89 cfs. This discharge is the

minimum priming discharge acceptable in the pumping station's design

25

25 . ... .

Page 31: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

• r:. 3o2rrIr-'-rrT

130

120-

110

100 -o AIR VENTS CLOSED

' AIR VENT AT EL 43590 - AIR VENT AT EL 442 2

z o BOTH VENTSj80 -W,

ui NO AIR VENT2 70

'60 AIR VENT AT EL 435z

gi:50

40 -BOTH VENTS

30 AIR VENT AT EL 442

20

10

so 100 120 140 160 IB 200080 100 12 DISCHARGE. CFS

Figure 13. Priming times for constant discharges

with air escape vents at tailwater el 445.0

specifications. When the tailwater was below the outlet (el 427.5),

significant partial recovery occurred rapidly; but full recovery could

not be achieved in the model (Plate 18). At a tailwater elevation of" .:-. ..

438.5, siphonic recovery was determined with and without an air escape

vent at el 435.0 (Plate 19). Without the vent, recovery was rapid at

first but slowed down considerably after a head recovery of about 9 ft.

With the air vent, about 15 ft of head was recovered before the recovery

rate slowed down. The air vent at el 442.0 could not function at this .

tailwater elevation. At tailwater elevations of 445.0 and 449.5, si-

phonic recovery was determined without an air escape vent and with vents

* at el 435.0 and 442.0 (Plate 20). At these higher tailwaters the rate

of siphonic recovery is slow without the air vents and considerably

faster with the vents. Complete siphonic recovery was achieved faster

26

10 .- A . . ".

Page 32: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

with the vent at el 442.0 than at el 435.0. Model results suggest that

significant partial siphonic recovery may be achieved in a relatively

short time without the use of air escape vents at low tailwaters; but at

higher tailwaters, air escape vents are required if rapid recovery is

desired.

34. Actual priming operations with varying discharge were simu-

* lated in the model with a high and a low tailwater. As the siphon

primes, the head on the pump is reduced and the discharge increases.

Variation of discharge with head is dependent on the particular per-

formance curve of a specific pump. Since this curve will remain unknown

* until the contract is awarded, a pump performance curve was estimated

*(Plate 2) and used to demonstrate the effect of increasing discharge on

* priming time. Results are shown in Figure 14. With a low tailwater,

discharge increases rapidly from 98 to 158 cfs and priming is accom-

plished in about 7 min. With the high tailwater, discharge increases

from 98 to 110 cfs at a slower rate, and about 50 min is required for

priming. With an air escape vent at el 435.0, priming time was reduced

to about 19 min. With the vent at el 442.0, about 9 min was required

for priming. Air escape vents provided significant improvement in

priming times with high tailwaters and varying discharges.

35. Surging of flow occurred in the vents during the early stages

of priming and adequate measures should be taken to prevent saturation

and scour of the embankment by flows that spill out of the vent. This

could be accomplished by providing protection and drainage around the

vent opening.

Effect of Reducing Cross-Sectional *Area at Siphon Crown

36. The last part of the siphon to flow full during priming is at

the crown and immediately downstream. The air removal rate is much

slower in the last stage of siphon priming because entrained air bub-

bles must travel farther to escape. It was postulated that if the cross-

sectional area of the crown was reduced so that the pipe would flow full,

priming times would be reduced.

27

0 '10 9_ 40 1P 9 U0 0 1P 1P 0 U

Page 33: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

4804

____ ___ _ __ __ _ ___450

_ _ _ _ _ _ 1 _ _ _440

7 6 5 4 3 2 0 "MINUTES AFTER START OF PRIMING

DISCHARGE INCREASES WITH TIME FROM98 TO 158 CFS, TAILWATER BELOW OUTLET

LU

VENT OPENED

S11 109 7 6 5 4 3 2 10W MINUTES AFTER START OF PRIMING

AIR VENT AT EL 442z

VENT OPENED-4 , I i I.LL.I - - S60ii.'.:

:'. I II I I II I I II :I I:I LI1445-19 18 17 16 15 14 13 12 11 10 9 8 7 6 5 4 3 2 1 0 '

MINUTES AFTER START OF PRIMINGAIR VENT AT EL 435

2019 18 17 16 15 14 13 12 11 10 9 8 7 6 5 ,3 2 1 0 " "MINUTES AFTER START OF PRIMING "S2

445 040 39 38 37 36 35 34 33 32 31 30 29 28 27 26 25 24 2322 210 a

MINUTES AFTER START OF PRIMING "

44555 54 63 52 51 50 49 48 47 46 45 44 43 42 41 40

MINUTES AFTER START OF PRIMING

NO AIR VENTDISCHARGE INCREASES WITH TIME FROM to

98 TO 110 CFS, TAILWATER EL 449.5

Figure 14. Hydrostatic head elevations during priming athigh and low tailvaters

28

.- 'S V *~U ~ 94

Page 34: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

37. Two designs were tested in the model (Figure 15) with the type

5 design outlet and compared with the type 1 (original) design crown.

The type 2 design crown consisted of plugging the top 1 ft of the 4-ft-

]. diam pipe along the horizontal crown section and providing a transition

downstream. The type 3 design crown extended the reduced cross-sectional

area an additional 16 ft downstream. Priming times for a range of con-

stant discharges were determined for each crown design with the tail-

water below the outlet. Results are compared in Figure 16. The crown

modifications provided for a decrease in priming times at the lower dis-

charges. The type 2 design crown was successful in forcing the horizn-

tal portion of the siphon crown to flow full during initial stages of ..t

* priming. The type 3 design crown was successful in causing the reduced

*. section to flow full at an earlier phase of priming so that the last

E portion of the siphon to flow full was the transition reach. Thus, the

modifications were successful in forcing the siphon to flow full at the

-00

SECTION A-A TYPE 2

,E; A15. 18" 14.23'

L _-_ _'

Figure 15. Siphon crown modifications

. -29

All9 a---'

Page 35: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

120

110- TYPE 1' .'; TYPE 2

- 100 - &TYPE 3 -

90-

U~70 TYPE24-0 -

3 2

TYPE 320 "

10

0 100 120 140 160 10 200

DISCHARGE, CFS

Figure 16. Effect of crown modifications on priming times

S1 crown early in the priming phase but unsuccessful in reducing priming

times sufficiently to justify incorporation into the final design. Ex-

tending the modified section farther downstream or replacing the 4-ft-

diam pipe with a smaller diameter pipe could effectively reduce priming

times, primarily by increasing velocities and thus increasing air re-

moval rates.

38. Velocities through the modified portions of the siphon were

increased due to the area reduction. This resulted in an increase in

total head losses at the pump for the normal (primed) operating condi-

* tions. At the design discharge of 133 cfs, the increase in head loss

was found to be 0.35 ft with the type 2 design crown and 0.50 ft with

the type 3 design crown. Increases in head losses for other discharges

are shown in Figure 17. Additional cross-sectional area reductions

would result in even greater head losses, which were considered to be

unsatisfactory by the sponsors.

30

~ -S S U ~ - U S S S S• S

Page 36: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

-#

"22 i 0 TYPE 20 TYPE 3

U- I0 0 50 100 150 200 250

DISCHARGE, CFS

Figure 17. Effect of crown modifications on head losses

Pressure Regulation with Air Vent

39. Siphonic head recovery can be limited by allowing small

amounts of atmospheric air to enter through the vents at the top of the

siphon conduit. Consideration has been given to this type of operation

in the conversion of existing pumping station discharge pipes to siphonswhere the elevation between the crown and outlet permits recoveries in

excess of 28 ft. This type of operation could also be used to increase

the head on the pump for operations where the static head on the pump is. reduced below the design limit. This method of operation was demon-

strated in the model with the type 4 design outlet. The model was al- -

lowed to operate for 2 hr (prototype time) and no change in the average

head was observed. Pressure fluctuations increased significantly due to

the unsteady flow conditions created by the air entrainment and removalprocess. Maximum and minimum pressures along the length of the siphon --

for a water discharge of 168 cfs and representative air discharges of7 and 4 cfs are shown in Plates 21 and 22, respectively. Pressure fluc-

*; tuations at the pump are shown in Plate 23. Severity of pressure fluctu-

ations varies with water and air discharges.

31

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Velocity Distributions Upstream from Outlet

40. Velocity distributions were measured just upstream from the

*type 4 design outlet with both the siphon primed and with the air vent

* open. Velocities were measured along the vertical axis of the discharge

* pipe with a pitot tube located 4 ft upstream from the center of the out-

let (Plate 24). Two measurements were made with the siphon primed and

- the tailwater below the outlet. Velocities measured for discharges of

* 107 cfs and 186 cfs (which represent the possible minimum and maximum

* operating discharges, respectively, to be expected with the pump char-2acteristic curves supplied by the St. Louis District) are plotted inPlate 24. These measurements show that flow tends to concentrate at the

top of the pipe when the siphon is primed, indicating a backwater effect.

- Velocity measurements with the air vent open and the tailwater below theIoutlet were made for discharges of 140 cfs and 89 cfs (the expected maxi-mum and minimum priming discharges, respectively, Plate 25). Under

* these conditions, flow was characterized by irregular velocity fluctua-

* tion and considerable air entrainment. Flow concentrated near the bot-

* tom of the pipe when the air vent was open and a hydraulic jump occurred

- just upstream of the position where the velocities were measured. These

* measurements were made in the type 4 design outlet to provide informa-

tion relative to structural design of the outlet, and would not be ex-

pected to be significantly different in the recommended type 5 design

outlet.

32

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PART IV: CONCLUSIONS

41. Pumping station siphons must be designed so that velocities

are sufficient to remove air at the priming discharge and a priming seal

. will remain in place upstream from any open air vents or an unsubmerged

outlet. A priming seal can be maintained with a properly designed saxo-

phone outlet. Water flows down the riverward leg of the siphon until it

reaches the adverse slope of the outlet. The saxophone outlet must have

a sufficient adverse slope and horizontal distance to force a hydraulic

jump in the siphon. The hydraulic jump entrains air which must be

carried out of the siphon by the flow so that the siphon will prime.

This model investigation determined that a 60-deg adverse slope and a

horizontal distance of 6 ft from the end of the horizontal section of

the siphon conduit center line to the outlet center line was sufficientU to maintain the priming seal for the McGee Creek pumping station siphon.

42. Priming characteristics may be studied qualitatively using

physical hydraulic models, realizing that there is a definite scale ef-

fect in modeling a water and air mixture. Priming times in prototypes

will be less than those obtained in models. This provides for a built-in ,

safety factor, because if the model primes it is safe to predict that

the prototype will prime. Conversely, the discharge that will wash out -

the priming seal may be underestimated by a model. It is therefore

prudent to provide a safety factor in the design of saxophone outlets.

Siphon models should be constructed to scales sufficiently large to mini-

mize scale effects. The state of the art does not yet allow determina-

tion of exact model-to-prototype scale effects. Prototype tests of this

structure will be invaluable in this regard.

43. Priming times can be significantly reduced with an air escape

vent when the tailwater is high. Elevation of the air escape vent must

be below the hydraulic grade line in the siphon conduit or it will act

tion on the siphon conduits. If the vent is at a higher location on the

conduit, air will be removed faster and priming times will be reduced;

however, the tailwater must be higher than the vent for the vent to

K • - . -•-•

Page 39: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

o -, .o T ~ - - -- ... -

function. The optimum vent location, therefore, depends on the fre-

quency of high tailvaters.

44. Reducing the cross-sectional area at the crown of the siphon

did not reduce priming times sufficiently to justify incorporation into

the final design. Additional head losses occurred with the reduced

cross sections after the siphon was primed.

45. The amount of siphonic head recovery for any given tailwater

can be reduced by allowing small amounts of atmospheric air to enter

through the vents at the top of the siphon conduit. Pressure fluctua-

tions and head losses in the siphon are much greater with an air pocket

and hydraulic jump in the siphon than with the siphon fully primed.

I V6

IQ"

34

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Page 40: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

REFERENCES

Babb, Alan F., Amorocho, J., and Dean, John. 1967. "Flow Behavior inLarge Siphons," Department of Water Resources, Aqueduct Design Section,--

* State of California and Department of Water Science and Engineering,University of California, Davis, Calif.

Central Board of Irrigation and Power. 1956. "Manual on River Behav-iour, Central, and Training," Publication No. 60, New Delhi, pp 347-348.

Copeland, Ronald R. 1982 (Sep). "Pointe Coupee Pumping Station Siphon,Upper Pointe Coupee Loop Area, Louisiana; Hydraulic Model Investigation,"Technical Report HL-82-21, U. S. Army Engineer Waterways Experiment Sta-tion, CE, Vicksburg, Miss.

Ervine, D. A., and Elsawy, E. M. 1975. "Some Scale Effects in ModelingAir Regulated Siphon Spillways," Proceedings of the Symposium on Designand Operation of Siphons and Siphon Spillways, London, BHRA FluidEngineering.

*" Falvey, Henry T. 1980. "Air Flow in Hydraulic Structures," EngineeringMonograph 41, U. S. Department of Interior, Denver, Colo., pp 48-51.

Gibson, A. H., Aspey, T. H., and Tattersall, F. 1931. "Experiments atSiphon Spillways," Proceedings of the Institution of Civil Engineers,Vol 231, London.

Head, Christopher. 1975 (Mar). "Low-Head Air-Regulated Siphons,".. Journal, Hydraulics Division, American Society of Civil Engineers,

Vol 101, No. HY3, pp 329-345.

Kalinske, A. A., and Robertson, James M. 1943. "Entrainment of Air inFlowing Water: Closed Conduit Flow," American Society of Civil Engi-neers Transactions, Vol 103, pp 1435-1447.

Kent, J. C. 1953. The Entrainment of Air by Water Flowing in CircularConduits with Downgrade Slopes, M.S. Thesis, University of California atBerkeley, Calif.

Naylor, A. H. 1935. Siphon Spillways, Edward Arnold & Company, London.

Renner, J. 1975. "Air Entrainment in Surface Rollers," Proceedings ofthe Symposium on Design and Operation of Siphons and Siphon Spillways,London, BHRA Fluid Engineering.

Thatcher, E. F., and Battson, A. K. 1975. "Delivery Siphons on PumpingPlant for Docks," Proceedings of the Symposium on Design and Operationof Siphons and Siphon Spillways, London, BHRA Fluid Engineering.

U. S. Army, Corps of Engineers. "Hydraulic Design Criteria," preparedfor Office, Chief of Engineers, by U. S. Army Engineer Waterways Experi-ment Station, CE, Vicksburg, Miss., issued serially since 1952.

Whittington, Richard B., and Ali, Kamil H. M. 1972 (Jan). "Siphons:Some Scale-Effects in Models," Journal, '-draulics Division, AmericanSociety of Civil Engineers, Vol 98, No. hil, pp 45-60.

35. ... .

Page 41: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

Wilhelms, Steven C., et al. 1981 (Jul). "Gas Transfer in HydraulicJumps," Technical Report E-81-10, U. S. Army Engineer Waterways Experi-ment Station, CE, Vicksburg, Miss.

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LOCATION OF VELOCITYMEASUREMENTS

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4 FT UPSTREAM FROM CENTER OFDISCHARGE PIPE OUTLET

SIPHON PRIMEDTYPE 4 DESIGN

PLATE 24

Page 78: AD-A121 MCGEE CREEK PUMPING STATION SIPJ4ON PIKE …be dissipated on a concrete capstone and riprap-bedded outlet channel. Tailwaters in the outlet channel will range between el 419.0

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--- [ 4----.-- -.. W -7~~

In accordance with letter from DAEN-RDC, DAEN-ASI dated22 July 1977, Subject: Facsimile Catalog Cards forLaboratory Technical Publications, a facsimile catalog - -

card in Library of Congress MAK format is reproducedbelow.

Copeland, Ronald R.McGee Creek pumping station siphon, Pike County,

Illinois : Hydraulic Model Investigation / by RonaldR. Copeland (Hydraulics Laboratory, U.S. Army EngineerWaterways Experiment Station). -- Vicksburg, Miss.The Station ; Springfield, Va. ; available from NTIS,1982.

36, [12] p., 25 p. of plates : ill. ; 27 cm. -- (Technicalreport ; HL-82-23)Cover title."September 1982."Final report."Prepared for U.S. Army Engineer District, St. Louis."Bibliography: p. 35.

1. Hydraulic models. 2. McGee Creek Pumping Station (lll.)3. Pumping stations. 4. Siphons. I. United States.Army. Corps of Engineers. St. Louis District. II. U.S.Army Engineer Waterways Experiment Station. Hydraulics

Copeland, Ronald R.McGee Creek pumping station siphon, Pike County : ... 1982.

(Card 2)

Laboratory. III. Title IV. Series: Technical report(U.S. Army Engineer Waterways Experiment Station) ; HL-82-23.TA7.W34 no.HL-82-23

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