USE OF WETTED-PERIMETER IN DEFINING MINIMUM ENVIRONMENTAL FLOWS

Citation
Cj. Gippel et Mj. Stewardson, USE OF WETTED-PERIMETER IN DEFINING MINIMUM ENVIRONMENTAL FLOWS, Regulated rivers, 14(1), 1998, pp. 53-67
Citations number
33
Categorie Soggetti
Environmental Sciences","Water Resources
Journal title
ISSN journal
08869375
Volume
14
Issue
1
Year of publication
1998
Pages
53 - 67
Database
ISI
SICI code
0886-9375(1998)14:1<53:UOWIDM>2.0.ZU;2-7
Abstract
In regulated rivers, the relationship between wetted perimeter and dis charge is sometimes used as an expedient technique for determining the minimum flow allowable for environmental purposes. The critical minim um discharge is supposed to correspond to the point where there is a b reak in the shape of the curve (usually a logarithmic or power functio n). Below this discharge, wetted perimeter declines rapidly. This crit ical point on the curve is almost universally, but incorrectly, termed an 'inflection' point, and is usually determined subjectively by eye from a graph. The appearance of a break in the shape of the curve is s trongly dependent on the relative scaling of the axes of the graph. Th is subjectivity can be overcome by defining the break in shape using m athematical techniques. The important break in the shape of the curve can be systematically defined by the point where the slope equals 1, o r where the curvature is maximized. The technique can be applied to ot her habitat-discharge relationships, provided the habitat variable inc reases with discharge. These techniques were applied to two regulated headwater streams located in the Melbourne catchment area. Channel sur vey data were used to model the relationship between discharge and wet ted perimeter, flowing water perimeter and blackfish habitat area. A l ogarithmic function could be fitted to the wetted perimeter data for S tarvation Creek, but the relationship for Armstrong Creek was linear. Both streams showed logarithmic relationships between discharge and fl owing water perimeter. For these streams, the wetted perimeter relatio nships did not suggest an optimum environmental flow, nor did they sug gest a flow level that would maintain the macroinvertebrate community in its unregulated state if it was applied for a long period of time. Fish habitat area does not necessarily increase with discharge, so the method of curve analysis suggested here for wetted perimeter may not be applicable to some fish habitat area data. Flowing water perimeter is preferable over wetted perimeter as a variable to define habitat su itable for macroinvertebrates. (C) 1998 John Wiley & Sans, Ltd.