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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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