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Chapter 11--Rosgen Geomorphic Channel Design

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<strong>Chapter</strong> <strong>11</strong><br />

Base-level change—A key part of channel stability<br />

analysis. Degree of channel incision (lowering of local<br />

base level) is determined by the ratio of the lowest<br />

bank height divided by maximum bankfull depth,<br />

called the bank height ratio. A stream may not be<br />

entrenched (vertically constrained), but may be partially<br />

incised, leading to entrenchment. A grade-control<br />

structure requirement is often associated with partially<br />

incised channels (<strong>Rosgen</strong> 1997a).<br />

Direct disturbance and riparian vegetation—The direct<br />

disturbance of stream channels must be offset by<br />

correcting dimension, pattern, profile, and often channel<br />

materials. Levees adjacent to both banks should<br />

be set back allowing room for a flood plain. Riparian<br />

vegetation change is not only a major cause of instability<br />

and loss of function, but is a key solution in restoration<br />

and natural channel design. Riparian vegetation<br />

reestablishment should contain the correct overstory<br />

and understory species to be compatible for a self-sustaining,<br />

long-term solution.<br />

Biological assessments—Biological assessments that<br />

describe fish species, food chains, diversity with broad<br />

categories of ecoregions, and stream types (habitat<br />

units) are currently collected with the assessment level<br />

for identifying biological potential. Limiting factor<br />

analysis provides information that identifies specific<br />

problems that may be corrected by changed management<br />

and/or restoration.<br />

It is readily apparent that this procedure involves extensive<br />

field observations and an extensive data base<br />

followed by a thorough and detailed analysis. All of<br />

this must be completed prior to restoration planning,<br />

as it forms much of the foundation for what follows.<br />

It is important to understand the various causes of instability<br />

responsible for loss of physical and biological<br />

function and corresponding loss of value. Recommendations<br />

that follow are critically linked to land uses,<br />

disturbance regime, and other problem sources. The<br />

flowchart (fig. <strong>11</strong>–10) depicts the assessment criteria<br />

of channel stability.<br />

<strong>Rosgen</strong> <strong>Geomorphic</strong> <strong>Channel</strong> <strong>Design</strong><br />

<strong>11</strong>–26 (210–VI–NEH, August 2007)<br />

Part 654<br />

National Engineering Handbook<br />

(d) Phase IV—Passive recommendations<br />

for restoration<br />

A first priority in restoration is to seek a natural recovery<br />

solution based on changes in the variables causing<br />

the instability and/or loss of physical and biological<br />

function. Changes in land use management can influence<br />

riparian vegetation composition, density and<br />

vigor, flow modifications (diversions, storage, and<br />

reservoir release schedule modifications based on the<br />

operational hydrology), flood control measures, road<br />

closures/stabilization, hillslope erosional processes,<br />

and other process influences of river stability. Often, a<br />

change in management strategies can be very effective<br />

in securing stability and function. This often has to be<br />

determined based on the recovery potential of various<br />

stream types and the short- and long-term goals associated<br />

with the stated objectives (including costs). The<br />

alternative of self-stabilization is always a key consideration<br />

in any stability assessment. The time-trend<br />

aerial photography from phase III may help to provide<br />

insight into stream recovery potential following disturbance.<br />

Successional stages of channel adjustment (fig. <strong>11</strong>–15)<br />

can also assist at looking at natural recovery potential.<br />

It is very important to ensure that objectives are met<br />

through effectiveness monitoring required to provide<br />

the documentation on the nature, magnitude, rate, and<br />

consequences of natural recovery. If natural recovery<br />

potential is poor and/or does not meet specific objectives,<br />

phase V would be appropriate (<strong>Rosgen</strong> geomorphic<br />

channel design methodology).<br />

(e) Phase V—The stream restoration<br />

and natural channel design using the<br />

<strong>Rosgen</strong> geomorphic channel design<br />

methodology<br />

Phase V involves combining the results of the previous<br />

phases. A good design can only follow a good assessment.<br />

It is preferred not to patch symptoms, but rather<br />

provide solutions to restoration that will offset the<br />

cause of the problem and allow for the river to be selfmaintaining.<br />

The practitioner must be very familiar<br />

with the processes involved in hydrology, hydraulics,<br />

sedimentology, geomorphology, soil science, aquatic<br />

habitat, and riparian vegetation. Due to the inherent<br />

complexity, it is usually necessary to obtain technical

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