Hydraulics for Hydrographers Channel Dynamics and Shift Corrections AQUARIUS Time-Series Software™ Aquatic Informatics Inc. Preview Concepts, terms and definitions Fluvial Processes Hydraulic Geometry EcoHydraulics Shift Corrections www.aquaticinformatics.com | 2 Fluvial Processes Mechanics of transport Solution Flotation Suspension Saltation Traction www.aquaticinformatics.com | 3 Suspended Load For a sediment particle to be held in suspension, the settling velocity must be less than or equal to the turbulent velocity As discharge increases, the suspended load increases at a more rapid rate than the discharge. The enhanced concentration is due to erosion of the drainage basin, not of scouring of the channel. www.aquaticinformatics.com | 4 Revised Universal Soil Loss Equation A R K LS P C Where A = soil loss; R is rainfall erosivity; K is soil erodibility; LS is topography (length of slope and slope); P is a conservative practices factor; and C is a cover factor Most sediment originates from the landscape Understanding the landscape upstream of your gauge can help in interpreting Shift Corrections www.aquaticinformatics.com | 5 Stoke’s Law for settling velocity of supended particles Vs 2( p f ) gr 2 9m Where: Vs is settling velocity; ρp is density of the particle; ρf is density of the fluid; g is gravity; r is radius of particle; and m is viscosity www.aquaticinformatics.com | 6 Bed Load: Saltation and Traction Saltation refers to low extended trajectories of sediment particles of particles with less mass than the tractive force. Traction is the movement of larger particles by rolling or sliding www.aquaticinformatics.com | 7 Sixth power law The radius of the largest particle that can be set in motion by a given velocity is: r kv 3 6 Where r is radius; k is a constant that includes gravity and grain density; and v is flow velocity Therefore a small increase in velocity can have a large increase in the size of particle that can be moved www.aquaticinformatics.com | 8 Hydraulic lift and the critical tractive force The steep gradient of velocity near the stream bed lowers the pressure on the top of particles resulting in hydraulic lift The column of water supported by a particle exerts as critical tractive force: Ft gds Where Ft is critical tractive force; is density of water; g is gravity; d is depth of water; and s is the gradient of the stream www.aquaticinformatics.com | 9 Erosion, transport and deposition 10 Erosion velocity (m/s) 1 0.1 Transport Deposition 0.01 0.001 0.001 0.01 0.1 1 10 100 Diameter (mm) www.aquaticinformatics.com | 10 Fluvial Landforms www.aquaticinformatics.com | 11 Dynamic equilibrium 2000 hypsometric integral = 0.45 elevation (m) 1500 1000 500 0 0 10 20 30 40 50 60 70 80 90 100 % of basin area www.aquaticinformatics.com | 12 Hydraulic Geometry Q AV WDV w aQ d cQf b v kQ a c k 1.0 b f m 1.0 m www.aquaticinformatics.com | 13 Hydraulic Geometry Channels with resistant bank-forming material such as cohesive silts have large values for ‘f’ and low values for ‘b’ Whereas channels with weak bank forming material such as sand have low values for ‘f’ and high values for ‘b’ www.aquaticinformatics.com | 14 Hydraulic geometry Velocity (m/s) 10 1 v 0.024 Q 0.1 Depth (m) 100 d 0.781 Q 10 0.303 w 53.542 Q 1 1000 Width (m) 0.595 0.103 100 10 100 1000 Discharge (m3/s) 10000 www.aquaticinformatics.com | 15 Velocity Residuals (m/s) Depth Residuals (m) Width Residuals (m) Hydraulic Geometry 20 10 0 -10 -20 1.0 0.0 -1.0 0.4 0.2 0 -0.2 -0.4 10/3/54 8/28/76 Discharge (m3/s) 7/24/98 www.aquaticinformatics.com | 16 EcoHydraulics Beavers =leaky weirs Vegetation Biofilms Submergent Emergent Riparian and LWD www.aquaticinformatics.com | 17 EcoHydraulics Stage data are more indicative of reach storage than of discharge Beavers regulate flow to control water table (e.g. To expand riparian zone) or to regulate water level (e.g. For protection of lodge entrance from predators) S Qo Qi dt www.aquaticinformatics.com | 18 Beaver Dams Simplistic Hydraulic solutions are invalid Hydrologic solutions include: Estimation of flow from representative gauged basins (e.g. using Empirical modeling toolbox) Interpolation between measurements with adjustments for runoff processes (e.g. using Data Correction Toolbox) Use of rainfall-runoff modeling (e.g. using custom toolboxes) www.aquaticinformatics.com | 19 River ice The effects of river ice are discussed in the lesson “River Ice Processes and Dynamics” www.aquaticinformatics.com | 20 Biofilms Biofilms are thin layers of algae that form under favourable conditions They are ‘slippery’ - affecting the coefficient in the rating equation - use a time-based to the right. If thick enough - the dominant effect may be on PZH, which can be temporarily be handled with a time-based shift to the left. Note: Rock Snot (Didymosphenia geminata) is transferred from watershed to watershed on waders – clean your waders between measurements if you don’t want to be responsible for its spread www.aquaticinformatics.com | 21 Submergent Lotic Vegetation Vegetation that does not break the water surface affects both the PZH and the HeadArea relation Note that the effect varies with stage – because high velocities flatten the weeds. At low velocities the weeds have a greater effect on PZH and the Head-Area relation. Use a time-based knee-bend shift to the left www.aquaticinformatics.com | 22 Emergent Lentic Vegetation In addition to all the effects of submergent vegetation – Emergent vegetation (e.g. lily pads) affect the wetted perimeter fundamentally altering the Hydraulic Radius upon which the rating curve is based. Use a time-based, truss shift to the left. Knowing the timing of emergence is crucial. www.aquaticinformatics.com | 23 Riparian vegetation - overhanging Riparian vegetation competes for sunlight in forests by growing out over the stream channel Overhanging vegetation may only come in contact with the water during high flows Overhanging vegetation affects wetted perimeter, and will result in an abrupt stage change at time of contact Use an upside down knee-bend shift to the left www.aquaticinformatics.com | 24 Riparian Vegetation – floating LWD Sweepers alter the wetted perimeter, PZH, and the Head-Area relation. Use a time-based shift correction – because they are floating - the effect is more or less uniform with respect to stage. If the sweeper is nasty – full of green branches etc. –it may not be possible to accurately estimate discharge using simplistic hydraulic assumptions in which case hydrologic methods may be required www.aquaticinformatics.com | 25 Riparian Vegetation – spanning LWD High water – critical flow Log spanning streambanks Abstraction and obstruction of flow Stream bed Normal rating curve Use a combination of the base rating curve at low-water, hydrologic (coefficient and exponent are unrelated to base rating curve) estimation from first contact to submergence of the log and a new rating curve at high water www.aquaticinformatics.com | 26 Other types of channel dynamics Variable backwater • • Estuaries Confluences Anthropogenic effects - Shopping carts, bicycle frames etc. Evaluate the hydraulic parameters affected and shift according to the type (time-based if the coefficient is affected; stage-based if the exponent is affected; time-based, stage-based if PZH is affected) www.aquaticinformatics.com | 27 Rating Curve Shifts Natural River Channels are seldom static (Aggradation/Degradation/ Fill / Ice / Weed Growth) Even artificial controls are subject to shifts (debris / algae) www.aquaticinformatics.com | 28 Fluvial dynamics velocity (m/s) 10 1 0.1 0.01 0.001 0.001 Transport 0.01 0.1 1 10 100 Diameter (mm) Aggradation or degradation of the banks generally affects the exponent, which calls for a stage-based correction whereas aggradation or degradation of the bed primarily affects PZH, which usually indicates a time-based, stage-based correction www.aquaticinformatics.com | 29 Shifts in AQUARIUS Can be developed in three ways Typing in shift points in the Shift Manager Adjusting points in the Shift Diagram On the rating curve zoom plots Shift dates can be specified in The Shift Manager The Time Series Pane (Shift Period Bars) www.aquaticinformatics.com | 30 Shifting by Time Sometimes Shifts are not static Weed growth, fill, and scour can take place gradually AQUARIUS lets you prorate a shift by leaving the ‘end date’ unspecified. An unspecified ‘end date’ shift will pro-rate into the next shift www.aquaticinformatics.com | 31 Preview In the next lesson: ‘River Ice Processes and Dynamics’ we will look at hydraulic and hydrologic approaches to estimating winter streamflow. www.aquaticinformatics.com | 32 Recommended, on-line, self-guided, learning resources USGS GRSAT training http://wwwrcamnl.wr.usgs.gov/sws/SWTraining/Index.htm World Hydrological Cycle Observing System (WHYCOS) training material http://www.whycos.org/rubrique.php3?id_rubrique=65#hydrom University of Idaho http://www.agls.uidaho.edu/bae450/lessons.htm Humboldt College http://gallatin.humboldt.edu/~brad/nws/lesson1.html Comet Training – need to register – no cost http://www.meted.ucar.edu/hydro/basic/Routing/print_version/05stage_discharge.htm#11 Thank you from the AI Team We hope that you enjoy AQUARIUS! www.aquaticinformatics.com | 34