Stream-Profile Analyses Using a Step-Backwater Model for ... - USGS
Stream-Profile Analyses Using a Step-Backwater Model for ... - USGS
Stream-Profile Analyses Using a Step-Backwater Model for ... - USGS
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6 <strong>Stream</strong>-<strong>Profile</strong> <strong>Analyses</strong> <strong>Using</strong> a <strong>Step</strong>-<strong>Backwater</strong> <strong>Model</strong> <strong>for</strong> Selected Reaches in the Chippewa Creek Basin in Ohio<br />
Table 1. Original design characteristics of the Soil Conservation Service flood-retention structures.<br />
[From U.S. Department of Agriculture, 1956]<br />
Flood-retention<br />
structure<br />
Tributary to<br />
Chippewa Creek<br />
Storm recurrence<br />
interval <strong>for</strong><br />
flood-retention<br />
structure<br />
(years)<br />
Year<br />
of dam<br />
completion<br />
Drainage area<br />
above dam<br />
(square miles)<br />
Conservation<br />
pool<br />
storage capacity<br />
(acre-feet)<br />
Flood storage<br />
capacity up to the<br />
emergency crest<br />
(acre-feet)<br />
II–A Buck Creek 25 1969 2.95 77 278<br />
III–A Hubbard Creek 50 1980 5.88 124 676<br />
IV–A Fall Creek 25 1973 1.51 16 120<br />
V–C East Branch Steele Ditch 1 25 1971 3.73 None 432<br />
V–D West Branch Steele Ditch 1 25 1971 1.75 30 156<br />
VII–C Little Chippewa Creek 50 1974 14.42 None 2,225<br />
VIII–C River Styx 2 5.7 inches 1976 3.86 None 673<br />
VIII–D Holmes Brook 3 50 1976 2.02 None 427<br />
Totals 36.12 247 4,987<br />
1 East and West Branch Steele Ditch <strong>for</strong>m Steele Ditch, a tributary to Chippewa Creek.<br />
2 This dam designed to control a storm runoff of 5.7 inches in 6 hours.<br />
3 Holmes Brook is a tributary to River Styx.<br />
Table 2. Hydraulic model limits <strong>for</strong> selected streams in the Chippewa Creek basin, Medina, Wayne, and Summit Counties, Ohio.<br />
<strong>Stream</strong> Upstream limit Downstream limit<br />
The Inlet 1 About 1,200 feet above<br />
Wedgewood Road /State Route 162<br />
About 750 feet below<br />
Chippewa Road<br />
Reach length<br />
(miles)<br />
Chippewa Creek 2 Chippewa Lake Mouth 19.1<br />
Little Chippewa Creek Steiner Road Mouth 3.2<br />
River Styx Flood Control Structure VII–C Mouth 7.9<br />
1 The Inlet is the head of Chippewa Creek.<br />
2 Westfield Ditch was modeled as an overflow channel to Chippewa Creek.<br />
Study Methods<br />
Data Collection<br />
Field visits were made to the Chippewa Creek basin to<br />
determine applicable stream-channel roughness coefficients<br />
(Manning’s n), cross-section elevations, and geometries of<br />
hydraulic structures. Cross sections and geometries were surveyed<br />
at all structures in each reach. If the distance between<br />
structures was more than 1 mi, an open-channel cross section<br />
was surveyed by the <strong>USGS</strong> at a convenient location near the<br />
halfway point. By use of a Geographic In<strong>for</strong>mation System,<br />
a Triangular Irregular Network (TIN) was developed from<br />
digital 2-ft contour interval mapping provided by Medina,<br />
Wayne, Stark, and Summit Counties to supplement surveyed<br />
cross-sectional data. In-channel bottom elevation data <strong>for</strong><br />
TIN-derived cross sections were estimated by interpolating<br />
values between surveyed cross sections. The in-channel<br />
bottom width <strong>for</strong> each TIN-derived cross section was estimated<br />
from the “AS-BUILT” plans provided by the MWCD<br />
(U.S. Department of Agriculture, 1980) <strong>for</strong> each stream. The<br />
combination of TIN-derived cross sections with interpolated<br />
in-channel elevations will be referred to as “synthetic” sections<br />
in this report. For this investigation, 246 cross sections<br />
were surveyed in the field (table 3) and 484 synthetic sections<br />
were developed. Geometries of 56 culverts and bridges and<br />
4 low head dams also were obtained from field surveys.<br />
The initial starting water-surface elevation <strong>for</strong> each<br />
model was determined from a normal-depth calculation in the<br />
HEC-RAS model. The initial slope was determined from the<br />
minimum channel elevations of surveyed cross sections near<br />
the mouth of each stream studied. All models were assumed to<br />
be independent of the downstream water-surface conditions.<br />
<strong>Backwater</strong> from the receiving stream was not considered in<br />
the beginning of each model. There<strong>for</strong>e, the water surface of<br />
each model will most likely be lower than the actual water sur-<br />
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