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...for using USGS Auto Port Selection Algorithm - only set up for Version 3.7-4.1/README.txt
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README.txt 11-December-2014 | ||
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Example Applications with Modified version 3.7/4.2 blending algorithm by USGS | ||
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This package contains four example applications of CE-QUAL-W2 models, meant to | ||
illustrate the features of the modified blending algorithm. | ||
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-------------------------------------------------------------------------------- | ||
Example #1: det_normal_uro-float_400fmin | ||
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This is a model of Detroit Lake, OR, USA, for a "normal" water year, using a combination | ||
of hypothetical outlets, where one of them is a floating outlet with a 400 cfs | ||
minimum flow (float_400fmin). | ||
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This scenario uses 4 outlets: | ||
1: floating weir, priority 1, 2.3 m depth, minimum 400 cfs, maximum 5600 cfs | ||
2: spillway, priority -1 (nonblended) | ||
3: lower power outlet, priority 1, maximum 5600 cfs | ||
4: regulating outlet, priority -1 (nonblended), maximum 5600 cfs | ||
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Outlets 2 and 4 represent outlets used to "spill" excess flow that the other | ||
outlets cannot handle. Those flows are preset in the outflow file, but the | ||
temperature effects of those releases are accounted for by including them in the | ||
blending group but giving them priorities of -1, which tells the model to | ||
account for that heat but not adjust the flows through those two outlets. The | ||
model estimates the temperatures released by those flows through the priority -1 | ||
outlets, then adjusts the temperature target for the blended releases accordingly. | ||
In this case, we have two outlets of the same priority balancing flows from a | ||
fixed elevation (outlet #3) and from a floating outlet (#1). It's not the most | ||
exciting example, but it's a good example to illustrate the "nonblended" outflows | ||
that are still accounted for in the temperature blending calculations. | ||
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The temperature target is in the file dynsplit_selective1.npt. It was set up to | ||
try to eject lots of heat through mid-summer, then concentrate on colder water | ||
releases based on a no-dams assessment of temperatures later in the year. | ||
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Note that when the maximum flow of an outlet is exceeded, even for a non-blended | ||
outlet (priority -1), the maximum flow criterion is honored and excess releases | ||
are shifted to other outlets. | ||
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-------------------------------------------------------------------------------- | ||
Example #2: lop-dex_lopFloat_20ppmin | ||
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This is a model for calendar year 2002 for Lookout Point and Dexter Lakes | ||
(lop-dex) using a floating outlet at Lookout Point (branch 1, outlet 1, 1-m | ||
depth) with a 20% minimum power production constraint at Lookout Point Dam | ||
(20ppmin). | ||
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Branch 1 is Lookout Point Lake, and the dam is given 3 outlets: | ||
1: floating outlet at 1-m depth, priority 2, no minimum or maximum flow constraint | ||
2: power outlet, priority 1, 20% minimum flow constraint | ||
3: regulating outlet, priority 2, maximum head constraint of 51.42 m | ||
TSSHARE is set to OFF, which tells the model to decide which of the two | ||
priority-2 outlets to use in blending with the power outlet. There are times | ||
when the RO (#3) is not available because of the maximum head constraint. In | ||
that case, blending occurs between the power outlet and the floating outlet. | ||
Late in the year, when we need cold-water releases and the lake level is lower, | ||
blending occurs between the power outlet and the RO. In this scenario, at least | ||
20% of the releases at Lookout Point Dam are constrained to go through the power | ||
outlet (minfrac=0.2). | ||
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Branch 2 is Dexter Lake. Two outlets. Nothing special. Spillway is outlet #1 | ||
and has priority 2. Power outlet is #2 and has priority 1. | ||
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Temperature targets are in dynsplit_selective1.npt for Lookout Point and | ||
dynsplit_selective2.npt for Dexter. They happen to be the same. | ||
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-------------------------------------------------------------------------------- | ||
Example #3: det_multigate_example3 | ||
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This example is a hypothetical case based on the Detroit Lake example, in which | ||
a multiple-gate tower of 8 outlets is used to blend releases to meet a release | ||
temperature target. The outlets are all fixed-elevation and arranged from 476 m | ||
to 385 m so that each is 13 meters apart, vertically. | ||
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The intention is to blend releases from the lowest and the highest available | ||
outlets. Therefore, priorities are set so that the deepest outlet has a priority | ||
of 1, and the other outlets, from shallowest to deepest, have priorities from 2 | ||
to 8. In this way, the deepest outlet will be blended with the one that is | ||
nearest to the surface. Each outlet is given a minimum head constraint of 2 m, | ||
so that the outlet cannot be used if it is too near the water surface. No other | ||
flow or head constraints are specified. | ||
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Note that the results from this scenario would be similar to those resulting from | ||
setting all of the outlet priorities to the same number. In that case, the model | ||
would first fulfill any minimum flow constraints (none here), then blend between | ||
the lowest and highest available outlets. That is pretty much what is done in | ||
this example, only through the explicit setting of priorities. | ||
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-------------------------------------------------------------------------------- | ||
Example #4: det_multigate_example4 | ||
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This example is similar to example #3, except that some other constraints are | ||
added and a different way of dealing with priorities is used. | ||
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In this example, outlet #6 is given a priority of 1 and all of the other outlets | ||
are given a priority of 2. TSSHARE is set to OFF, meaning that the model is | ||
supposed to choose one of the priority-2 outlets to blend releases with the | ||
single priority 1 outlet. The choice is made after fulfilling any other minimum | ||
flow constraints, and all of the priority 2 outlets are tested to see which one | ||
is best used for meeting the target release temperature. | ||
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In this example, the priority 1 outlet is given a minimum flow constraint, | ||
specifying that at least 20% of the total release should go through that outlet. | ||
No other outlets have minimum or maximum flow constraints. However, the lowest | ||
two outlets have maximum head constraints, such that they cannot be used if they | ||
are deeper than 60 meters. All outlets were given a minimum head constraint, | ||
such that they cannot be used unless there is at least 2 meters of depth at the | ||
centerline elevation of the outlet. | ||
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So, the result is that outlet #6 is blended with an upper outlet during summer | ||
when the goal is to export warmer water from the lake, and then blended with a | ||
lower outlet when the goal is to export cold water late in the season, subject | ||
to the lowest outlets not being more than 60 meters deep. | ||
-------------------------------------------------------------------------------- | ||
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For more information, contact: | ||
Stewart Rounds | ||
U.S. Geological Survey | ||
Oregon Water Science Center | ||
2130 SW 5th Avenue | ||
Portland, OR 97201 | ||
503-251-3280 | ||
[email protected] | ||
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or | ||
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Norman Buccola | ||
U.S. Geological Survey | ||
Oregon Water Science Center | ||
2130 SW 5th Avenue | ||
Portland, OR 97201 | ||
503-251-3245 | ||
[email protected] |
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Constituent, hydrodynamic, and derived constituent names, formats, multipliers, and array viewer controls | ||
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....................HNAME................... FMTH HMULT HMIN HMAX HPLTC # | ||
Timestep violations [NVIOL] (I10) 1.0 -1.0 1.0 OFF 1 | ||
Horizontal velocity [U], m/s (f10.3) 1.0 -.1000 0.25 OFF 2 | ||
Vertical velocity [W], m/s (f10.3) 1.0 -.1E-6 -0.01 OFF 3 | ||
Temperature [T1], <o/>C (f10.3) 1.0 -2.0 -30.0 ON 4 | ||
Density [RHO], kg/m^3 (f10.3) 1.0 997.0 1005.0 OFF 5 | ||
Vertical eddy viscosity [AZ], m^2/s (f10.3) 1.0 -1E-08 0.01 OFF 6 | ||
Velocity shear stress [SHEAR], 1/s^2 (f10.3) 1.0 -1E-08 0.01 OFF 7 | ||
Internal shear [ST], m^3/s^2 (f10.3) 1.0 -1E-08 0.01 OFF 8 | ||
Bottom shear [SB], m^3/s^2 (f10.3) 1.0 -1E-08 0.01 OFF 9 | ||
Longitudinal momentum [ADMX], m^3/s^2 (f10.3) 1.0 -1E-08 0.01 OFF 10 | ||
Longitudinal momentum [DM], m^3/s^2 (f10.3) 1.0 -1E-08 0.01 OFF 11 | ||
Horizontal density gradient [HDG], m^3/s^2 (f10.3) 1.0 -1E-08 0.01 OFF 12 | ||
Vertical momentum [ADMZ], m^3/s^2 (f10.3) 1.0 -1E-08 0.01 OFF 13 | ||
Horizontal pressure gradient [HPG], m^3/s^2 (f10.3) 1.0 -1E-08 10.0 OFF 14 | ||
Gravity term channel slope [GRAV], m^3/s^2 (f10.3) 1.0 0.0 0.0 OFF 15 | ||
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....................CNAME.................... FMTC CMULT CMIN CMAX CPLTC # | ||
TDS g/m3 or Salinity kg/m3 (F10.3) 1.0000 -1.0000 200.000 OFF 1 | ||
Water age, days (F10.3) 1.0000 -1.0000 1000.00 OFF 2 | ||
Large Suspended solids,g/m^3, #1 (F10.3) 1.0000 -1.0000 15.0000 OFF 3 | ||
Small Suspended solids,g/m^3, #3 (F10.3) 1.0000 -1.0000 15.0000 OFF 4 | ||
Phosphate, g/m^3 (F10.3) 1.0000 -1.0000 -50.000 OFF 5 | ||
Ammonium, g/m^3 (F10.3) 1.0000 -0.1000 -300.00 OFF 6 | ||
Nitrate-Nitrite, g/m^3 (F10.3) 1.0000 -0.1000 -5.0000 OFF 7 | ||
Dissolved silica, g/m^3 (F10.3) 1.0000 -1.0000 10.0000 OFF 8 | ||
Particulate silica, g/m^3 (F10.3) 1.0000 -0.2000 15.0000 OFF 9 | ||
Total iron, g/m^3 (F10.3) 1.0000 -0.1000 2.00000 OFF 10 | ||
Labile DOM, g/m^3 (F10.3) 1.0000 -0.1000 -3.0000 OFF 11 | ||
Refractory DOM, g/m^3 (F10.3) 1.0000 -0.1000 4.00000 OFF 12 | ||
Labile POM, g/m^3 (F10.3) 1.0000 -0.1000 3.00000 OFF 13 | ||
Refractory POM, g/m^3 (F10.3) 1.0000 -0.1000 4.00000 OFF 14 | ||
Dissolved oxygen, g/m^3 (F10.3) 1.0000 -2.0000 15.0000 OFF 15 | ||
Inorganic carbon, g/m^3 (F10.3) 1.0000 -1.0000 10.0000 OFF 16 | ||
Alkalinity, g/m^3 (F10.3) 1.0000 -1.0000 200.000 OFF 17 | ||
Zooplankton, g/m^3 (F10.3) 1.0000 -0.0100 3.00000 OFF 18 | ||
LDOM P, mg/m^3 (g10.3) 1000.0 0.0 1.0 OFF 19 | ||
RDOM P, mg/m^3 (g10.3) 1000.0 0.0 1.0 OFF 20 | ||
LPOM P, mg/m^3 (g10.3) 1000.0 0.0 1.0 OFF 21 | ||
RPOM P, mg/m^3 (g10.3) 1000.0 0.0 1.0 OFF 22 | ||
LDOM N, mg/m^3 (g10.3) 1000.0 0.0 1.0 OFF 23 | ||
RDOM N, mg/m^3 (g10.3) 1000.0 0.0 1.0 OFF 24 | ||
LPOM N, mg/m^3 (g10.3) 1000.0 0.0 1.0 OFF 25 | ||
RPOM N, mg/m^3 (g10.3) 1000.0 0.0 1.0 OFF 26 | ||
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....................CDNAME................... FMTCD CDMULT CDMIN CDMAX CDPLTC # | ||
Dissolved organic carbon, g/m^3 (F10.3) 1.0 -1.0 25.0 OFF 1 | ||
Particulate organic carbon, g/m^3 (F10.3) 1.0 -1.0 50.0 OFF 2 | ||
Total organic carbon, g/m^3 (F10.3) 1.0 -1.0 25.0 OFF 3 | ||
Dissolved organic nitrogen, g/m^3 (F10.3) 1.0 -1.0 25.0 OFF 4 | ||
Particulate organic nitrogen, g/m^3 (F10.3) 1.0 -1.0 25.0 OFF 5 | ||
Total organic nitrogen, g/m^3 (F10.3) 1.0 -1.0 50.0 OFF 6 | ||
Total Kheldahl Nitrogen, g/m^3 (F10.3) 1.0 -1.0 15.0 OFF 7 | ||
Total nitrogen, g/m^3 (F10.3) 1.0 -1.0 15.0 OFF 8 | ||
Dissolved organic phosphorus, mg/m^3 (F10.3) 1000.0 -1.0 25.0 OFF 9 | ||
Particulate organic phosphorus, mg/m^3 (F10.3) 1000.0 -1.0 -1.0 OFF 10 | ||
Total organic phosphorus, mg/m^3 (F10.3) 1000.0 -1.0 5.0 OFF 11 | ||
Total phosphorus, mg/m^3 (F10.3) 1000.0 -1.0 20.0 OFF 12 | ||
Algal production, g/m^2/day (F10.3) 1.0 -1.0 5.0 OFF 13 | ||
Chlorophyll a, mg/m^3 (F10.3) 1.0 -5.0 145.0 OFF 14 | ||
Total algae, g/m^3 (F10.3) 1.0 -1.0 60.0 OFF 15 | ||
Oxygen % Gas Saturation (F10.3) 1.0 -1.0 50.0 OFF 16 | ||
Total suspended Solids, g/m^3 (F10.3) 1.0 -1.0 5.0 OFF 17 | ||
Total Inorganic Suspended Solids,g/m^3 (F10.3) 1.0 -1.0 20.0 OFF 18 | ||
Carbonaceous Ultimate BOD, g/m^3 (F10.3) 1.0 5.0 9.0 OFF 19 | ||
pH (F10.3) 1.0 -1.0 10.0 OFF 20 | ||
CO2 (F10.3) 1.0 -1.0 10.0 OFF 21 | ||
HCO3 (F10.3) 1.0 -1.0 10.0 OFF 22 | ||
CO3 (F10.3) 0.0 0.0 0.0 OFF 23 |
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