Highway 80 Gage
Historical Peaks
Bridges
Weirs
HEC-2 Computer Model
The Golder Evaluation
CONSIDERATIONS AND COMPUTATIONS FOR
FLOOD CONTROL LAKE
IN JACKSON MISSISSIPPI
For conceptual purposes,
while studying the feasibility of using a lake through Jackson for Flood control our
initial calculations were made using an average Pearl River cross section.
And the Chezy-Manning Hydraulic Equation:
Q = AV
V= C (rs)1/2
r = A/p
s = h/l
Where:
Q = Flow rate (ft3/sec)
A = Cross sectional area (ft2)
V = Velocity (ft/sec)
r = Hydraulic radius (ft)
p = Wetted perimeter (ft)
s = Slope of water surface (ft/ft)
l = Distance (ft)
h = Drop in water level (ft)
C is found using the kutter formula
C = 41.6 + 1.1811/n + 0.000281/s
1 + (41.6 + 0.00281/s) n/(r)1/2
Where:
n = Manning roughness coefficient
This was much less
cumbersome than using the HEC-2 program with its many cross sections and data points. This
way we could get a feel for what it would take by simply changing a few numbers. This
would get us in the ball park of what it would take and later we could use a more accepted
computer model.
Present Condition
The first step was to take historical flood
levels vs flow rates and generate a pre-downtown levee/structure curve and a post
levee/structure curve.

When plotting the Pearl River
Jackson Gage data of pre 1963 annual flows and post 1969 annual peak flows, one must go
back to the period of 1874 - 1935 in order to have any significant amount of flood data
which could compare to the 1979 and 1983 floods. By using all of the available yearly peak
flow information, excluding the period in which the levees were constructed, and assuming
that the information is somewhat accurate, it can clearly be seen that there is a
difference in magnitude of the gage readings taken before 1963 compared to those taken
after 1969 (approximately 3 feet at this location). It should be noted that the gauge
readings were taken downstream of the cutoff channel. All that may be concluded from this
information due to the long span of time it covers is that the combination of bridges,
levees, landfills and other encroachments (see map on following page) seem to have an
increase in water levels for this location for the higher magnitude floods.

| Year |
Date |
Gage
Height (ft-HGVD) |
Discharge
(cfs) |
Notes |
Year |
Date |
Gage
Height (ft-HGVD) |
Discharge
(cfs) |
Notes |
|
|
|
|
|
|
|
|
|
|
| 1874 |
4-25-74 |
37.00 |
80000 |
1 |
1947 |
1-22-47 |
30.66 |
26000 |
|
| 1881 |
12-05-80 |
36.50 |
70000 |
1 |
1948 |
3-11-48 |
30.63 |
25600 |
|
| 1900 |
4-24-00 |
36.70 |
35000 |
|
1949 |
1-12-49 |
33.11 |
38300 |
|
| 1901 |
01 |
|
24000 |
|
1950 |
1-14-50 |
33.90 |
44700 |
|
| 1902 |
3-31-02 |
37.50 |
85000 |
|
1951 |
4-04-51 |
34.36 |
49100 |
|
| 1903 |
2-14-03 |
33.70 |
43600 |
|
1952 |
3-16-52 |
17.51 |
6600 |
|
| 1904 |
4-11-04 |
11.10 |
5295 |
|
1953 |
5-09-53 |
31.65 |
28500 |
|
| 1905 |
2-17-05 |
29.20 |
24880 |
|
1954 |
5-12-54 |
23.25 |
10600 |
|
| 1906 |
3-29-06 |
29.80 |
26000 |
|
1955 |
4-20-55 |
31.50 |
27500 |
|
| 1907 |
10-13-06 |
30.10 |
26600 |
|
1956 |
4-14-56 |
31.78 |
29300 |
|
| 1908 |
2-23-08 |
29.08 |
26000 |
|
1957 |
4-11-57 |
30.32 |
22100 |
|
| 1909 |
5-30-09 |
35.30 |
58300 |
|
1958 |
5-08-58 |
34.23 |
38900 |
|
| 1910 |
4-20-10 |
16.40 |
9020 |
|
1959 |
2-20-59 |
26.52 |
13600 |
|
| 1911 |
4-16-11 |
22.60 |
14600 |
|
1960 |
3-11-60 |
30.29 |
22600 |
|
| 1912 |
4-23-12 |
31.70 |
29600 |
|
1961 |
3-01-61 |
35.00 |
46000 |
|
| 1913 |
3-18-13 |
29.00 |
24600 |
|
1962 |
12-21-62 |
37.24 |
66100 |
2 * |
| 1914 |
4-09-14 |
31.10 |
29900 |
|
1963 |
3-19-63 |
17.74 |
6440 |
2 ** |
| 1915 |
2-09-15 |
26.70 |
20200 |
|
1964 |
3-23-64 |
31.00 |
24000 |
2 |
| 1916 |
1-09-16 |
26.70 |
20200 |
|
1965 |
2-17-65 |
32.02 |
28800 |
2 |
| 1917 |
4-11-17 |
26.50 |
19800 |
|
1966 |
2-18-66 |
30.99 |
26700 |
2 |
| 1918 |
5-04-18 |
22.90 |
15300 |
|
1967 |
2-25-67 |
20.16 |
8130 |
2 |
| 1919 |
3-19-19 |
27.60 |
21800 |
|
1968 |
12-23-67 |
31.43 |
29900 |
2 |
| 1920 |
12-14-19 |
30.50 |
28100 |
|
1969 |
4-20-69 |
34.55 |
44800 |
2 |
| 1921 |
4-21-21 |
32.90 |
37800 |
|
1970 |
5-03-70 |
27.43 |
18300 |
2 |
| 1922 |
3-11-22 |
28.80 |
24200 |
|
1971 |
5-15-71 |
32.67 |
32100 |
2 |
| 1923 |
2-16-23 |
30.70 |
28700 |
|
1972 |
1-17-72 |
32.56 |
31600 |
2 |
| 1924 |
3-08-24 |
26.80 |
20400 |
|
1973 |
4-19-73 |
32.99 |
33400 |
2 |
| 1925 |
1-25-25 |
28.80 |
24200 |
|
1974 |
4-18-74 |
34.36 |
40300 |
2 |
| 1926 |
3-17-26 |
27.00 |
20700 |
|
1975 |
3-20-75 |
32.43 |
34400 |
2 |
| 1927 |
2-24-27 |
30.00 |
26800 |
|
1976 |
4-03-76 |
35.74 |
50400 |
2 |
| 1928 |
4-30-28 |
29.80 |
26300 |
|
1977 |
4-09-77 |
35.57 |
48900 |
2 |
| 1929 |
3-24-29 |
32.30 |
30600 |
|
1978 |
5-14-78 |
31.80 |
27400 |
2 |
| 1930 |
5-28-30 |
31.90 |
29400 |
|
1979 |
4-17-79 |
43.28 |
128000 |
2,3,4 |
| 1931 |
8-05-31 |
26.40 |
15100 |
|
1980 |
4-13-80 |
35.50 |
50900 |
|
| 1932 |
2-28-32 |
29.10 |
21300 |
|
1981 |
4-05-81 |
30.10 |
24600 |
|
| 1933 |
12-19-32 |
35.20 |
60000 |
|
1982 |
12-02-82 |
36.00 |
46600 |
|
| 1934 |
3-13-34 |
28.00 |
18600 |
|
1983 |
5-23-83 |
39.50 |
78600 |
|
| 1935 |
3-12-35 |
35.18 |
56700 |
|
1984 |
3-06-84 |
28.40 |
20800 |
|
| 1936 |
2-12-36 |
32.46 |
34400 |
|
1985 |
2-07-85 |
29.00 |
23800 |
|
| 1937 |
1-29-37 |
30.00 |
22800 |
|
1986 |
11-29-86 |
29.40 |
25300 |
|
| 1938 |
4-09-38 |
32.07 |
32100 |
|
1987 |
2-28-87 |
32.60 |
39100 |
|
| 1939 |
2-15-39 |
28.93 |
19200 |
|
1988 |
4-03-88 |
27.70 |
19700 |
|
| 1940 |
7-18-40 |
31.94 |
30100 |
|
1989 |
1-17-89 |
30.20 |
24000 |
|
| 1941 |
12-29-41 |
25.17 |
12700 |
|
1990 |
1-25-90 |
33.70 |
38900 |
|
| 1942 |
3-17-42 |
19.41 |
7720 |
|
1991 |
5-05-91 |
35.00 |
45500 |
|
| 1943 |
3-30-43 |
28.43 |
19200 |
|
|
|
|
|
|
| 1944 |
4-04-44 |
34.03 |
46700 |
|
|
|
|
|
|
| 1945 |
3-01-45 |
32.58 |
36900 |
|
|
|
|
|
|
| 1946 |
2-17-46 |
34.44 |
49600 |
|
|
|
|
|
|
1 - Historic peaks outside period of record
2 - Flow regulated since 27 Sep61 by Ross Barnett Reservoir, 15 miles upstream
3 - Estimated discharge of 145,000 cfs used in frequency study to account for flood
control regulation at Ross Barnett Dam, 15 miles upstream of gage
4 - Highest peak since 1874
* - Reservoir constructed
** - Levees constructed
Using the Chezy equation,
an average cross section, historical slopes, and flood data friction factors were derived
to get this cross section to fit the pre-levee/structure curve at various flow rates.
Main Body of Lake
Now a much narrower more efficient cross section (or
lake) was derived that would handle the 1979 flood at the safe flood levels assuming the
water levels south of the lake would remain the same for either situation.

The cleared and graded lake with 2000 foot wide
dredged flow course now has friction factors similar to or better than the original river
channel. Various channel depths were used until through iteration the derived water level
and hydraulic gradient could be achieved.
From an engineering stand point it could be
considered that we are designing a flow course that would have the ability to handle
128,000 cubic feet per second with a rise of about three feet over a length of 11 miles.
Bridges
The next question is what to do at the bridges? Most
of the Pearl River bridges in Jackson have a span of at least 1000 feet. The Highway 80
bridge for example has a span of 1170 feet.

If a 1000 feet wide flow course was dredged down to
the top of the pile caps over a l000 foot length, the resulting cross section would have
the same hydraulic gradient as the rest of the lake.
In the event that any of the bridges are not
constructed in a manner that would lend itself to this depth of dredging, side pilings
could be driven with a concrete band poured around them and the existing piling tying them
all together in order to obtain the proper safety factors. It would also be possible not
to dredge as deep directly under the bridge. Limestone could then be added to prevent
washing. The area under the bridge would act as a small weir and would not cause a
significant change in the water level.
The following three pages show the calculations using the Chezy
equations for the original river channel, the lake itself, and the dredged channels that
could be used under the bridges.
|
water level
|
272
|
ft elev
|
@R.M.294
|
|
|
channel
|
river bottom
|
flat woods
|
|
|
|
av.bottom (elevation)
|
246
|
265
|
274
|
|
32
|
ft equiv. gage reading
|
|
rise (ft)
|
12.00
|
12.00
|
12.00
|
|
0.70
|
ft rise per river mile
|
|
run (ft)
|
90800
|
63500
|
63500
|
|
1.00
|
ft rise per reach mile(somewhat
|
|
height (ft)
|
26.0
|
7.0
|
-2.0
|
|
|
straight line down floodplain) |
|
width (ft)
|
200
|
3800
|
12000
|
|
264.4
|
ft water surface-RM284.5
|
|
n (friction coef.)
|
0.03
|
0.2
|
0.2
|
|
276.4
|
ft water surface-RM301.7
|
|
velocity (ft/sec)
|
4.72
|
0.45
|
0.00
|
|
|
|
|
flowrate (cubic ft/sec)
|
24535
|
11981
|
0
|
|
|
|
|
total flow (cubic ft/sec)
|
|
36515
|
36515
|
|
|
|
|
|
|
|
|
|
|
|
The above calculations are for an average cross-section of the Pearl River in
Jackson as it existed before the levees, bridges, or any other structures were built. For
calculation purposes the cross-section is located at River Mile 294 which is roughly at
the half way point of the upper lake. Different water levels and their resulting flowrates
can be compared to the historical Jackson gage readings to make sure we are in the ball
park with our friction factors and cross-sectional shape. The extrapolated water levels
are based on reach distance rather than river miles.
|
|
|
|
Average
|
water level
|
274
|
ft elev
|
@R.M.294
|
|
|
channel
|
river bottom
|
flat woods
|
|
|
|
av.bottom (elevation)
|
246
|
265
|
274
|
|
34
|
ft equiv. gage reading
|
|
rise (ft)
|
12.00
|
12.00
|
12.00
|
|
0.70
|
ft rise per river mile
|
|
run (ft)
|
90800
|
63500
|
63500
|
|
1.00
|
ft rise per reach mile(somewhat
|
|
height (ft)
|
28.0
|
9.0
|
0.0
|
|
|
straight line down floodplane)
|
|
width (ft)
|
200
|
3800
|
12000
|
|
266.4
|
ft water surface-RM284.5
|
|
n (friction coef.)
|
0.03
|
0.2
|
0.2
|
|
278.4
|
ft water surface-RM301.7
|
|
velocity (ft/sec)
|
4.95
|
0.56
|
0.00
|
|
|
|
|
flowrate (cubic ft/sec)
|
27709
|
19315
|
0
|
|
|
|
|
total flow (cubic ft/sec)
|
|
47024
|
47024
|
|
|
|
|
|
|
|
|
|
|
|
The average water level is increased in two ft. increments and will be placed
on a curve that shows the historical data
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Average
|
water level
|
276
|
ft elev
|
@R.M.294
|
|
|
channel
|
river bottom
|
flat woods
|
|
|
|
av.bottom (elevation)
|
246
|
265
|
274
|
|
36
|
ft equiv. gage reading
|
|
rise (ft)
|
12.00
|
12.00
|
12.00
|
|
0.70
|
ft rise per river mile
|
|
run (ft)
|
90800
|
63500
|
63500
|
|
1.00
|
ft rise per reach mile(somewhat
|
|
height (ft)
|
30.0< | |