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Last modified
7/14/2009 5:01:47 PM
Creation date
5/20/2009 5:10:24 PM
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UCREFRP
UCREFRP Catalog Number
8256
Author
Holly, F. M. and R. Ettema
Title
Sediment Imbalance in Rivers
USFW Year
n.d.
USFW - Doc Type
Simulation Possibilities and Problems
Copyright Material
YES
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<br />r <br /> <br />f: .. <br /> <br />;1 <br />iI, <br />~.: <br />;~ <br /> <br />416 BIOLOGICAL REPoRT 19 <br /> <br />':f. <br />Ji <br />-,J <br />if <br /> <br />changes on a river and its ecosystem, and generally <br />in a very short time (months to years). But the <br />response of the river and its ecosystem to these <br />perturbations is not necessarily coITespondingly <br />short. Several decades, perhaps even centuries, <br />may be required before the river returns to a new <br />(or former) equilibrium channel and planform ge- <br />ometry. Ironically, such natural response times <br />often span at least the typical professional career <br />of a river engineer. Yet this seemingly slow re- <br />sponse may, in just one generation, exterminate a <br />species that has otherwise survived from the age <br />of the dinosaurs. <br />Nature's deliberate but definite response to <br />man's rapid (and equally definite) intervention <br />may deprive the river engineer of an immediate- <br />feedback mechanism for evaluating the effective- <br />ness (and indirect habitat effects) of engineering <br />works. Design evaluations thus have relied on <br />physical scale-model studies for local, rather short- <br />term effects. Yet the scaling of physical models can <br />be inaccurate, especially when extended lengths of <br />river or periods of time are modeled. For this <br />reason, and because of the inordinate physical size <br />of laboratory space required, it rarely has been <br />practical to use physical models for those situ- <br />ations. <br />Computational simulation of extended lengths <br />of rivers and periods of time began in the 1960's. <br />At that time fixed-bed computational modelling <br />(that is, numerical simulation of flood propagation <br />and backwater effects in immobile-bed channels) <br />began to achieve a certain engineering maturity, <br />and the next logical step was to apply the same <br />techniques to mobile-bed simulation. However, <br />whereas fIXed-bed modelling evolved into a reli- <br />able, mature engineering tool in the space of about <br />10 years, mobile-bed modelling is still in its in- <br />fancy, groping for the statUB of its fIXed-bed pro- <br />genitor. <br />The problem in mobile-bed computational mod- <br />elling is one of applying effective numerical tech- <br />niques to frustratingly limited, crude schematiza- <br />tions of complex water-sediment processes, with <br />the goal of mAking reliable long-term predictions <br />of a river's response to changes imposed upon it. <br />That some progress has been made toward this <br />goal is a tribute more to the skill, intuition, and <br />experience of numerical modelers than to any in- <br />herent reliability of the modelling techniques em- <br />ployed.- <br />In the remainder of this paper we provide a brief <br />overview of mobile-bed computational modelling, <br /> <br /> <br />i <br />I <br />~ <br />II <br />'" <br />, <br />~ <br /> <br />I <br /> <br />~ <br />I' <br />'I <br /> <br /> <br />discuss challenges and opportunities for the fu- <br />ture, and present an example application to the <br />Missouri River. Our purpose is to provide general <br />background on the capabilities and limitations of <br />such modelling in support of river-development <br />decisions. <br /> <br />Sediment Non-equilibrium <br /> <br />An early recognition of the notion of the mecha- <br />nisms by which an alluvial river is always trying <br />to achieve an equilibrium was presented by Lane <br />(1957) and depicted in a classic diagram, a recent <br />version of which is shown in Fig. 1. The diagram <br />reflects the essential role of shear stress. exerted <br />on a river bed by flowing water and relates the <br />sediment transport to the flow hydraulics. On the <br />water side of the scale, bed shear stress increases <br />as the channel slope and water discharge increase. <br />On the sediment side of the scale, the amount of <br />sediment transported increases with the shear <br />stress, and finer sediment is more easily trans- <br />ported than coarser sediment. Thus excessive or <br />insufficient shear (with regard to equilibrium con- <br />ditions) results in degradation (scour) or aggrada- <br />tion (deposition) toward a new equilibrium, or bal- <br />ance. This can result from adjustments of sediment <br />load, sediment size, channel slope (as in planform <br />meandering), or channel cross section (not explic- <br />itly represented in the diagram). Of course even <br />natural rivers are seldom in a state of true equilib- <br />rium, but rather are constantly adjusting. The <br />balances of Fig. 1 reflect both natural and per- <br />turbed adjustment tendencies. <br />The qualitative understanding of the processes <br />represented in Fig. 1 has entered the river-engi- <br />neering lexicon through the term "hungry water," <br />refemng to the inevitable bed scour and degrada- <br />tion immediately downstream of dams that trap <br />sediments, releasing clear water with its potential <br />for unmitigated scour. <br />Figure 1 is thought-provoking and summarizes <br />the essential features of dynamic river equilibrium. <br />However, there are complexities and subtleties in <br />the way equilibrium can be obtained. For example, <br />hydraulic sorting, that is, the preferential trans- <br />port of finer material in a mixture, can result in a <br />coarSening of the bed; indeed, this is the essential <br />process by which the sediment-size adjustments of <br />Fig. 1 occur. But accumulation of a relatively small <br />amount of coarse, nonmoving material in an inter- <br />locking pattern on the bed can suppress virtually <br />
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