
U.S. Geological Survey
Effects of Hypothetical Management Scenarios on Simulated Water Temperatures in the Tualatin River, Oregon, 1998
By John C. Risley
USGS Water-Resources Investigations Report 00-4071, 110 pages,
74 figures, 22 tables
Report availability
SIGNIFICANT FINDINGS
Water temperature is one of the most important factors determining
the health of fish and other aquatic organisms. If water temperatures
warm beyond a critical threshold, particularly during the sensitive
life stages of fish, survival can markedly decrease. In 1996, the State
of Oregon adopted a revised maximum water temperature standard of
17.8oC (degrees Celsius) (64oF [degrees
Fahrenheit]) for most waterways, including the Tualatin River in
northwestern Oregon. To assess water temperature conditions in the
Tualatin River, a recent cooperative study between the U.S. Geological
Survey and the Unified Sewerage Agency of Washington County, Oregon,
used two dynamic-flow heat-transport models, DAFLOW-BLTM (river mile
[RM] 63.9-RM 38.4) and CE-QUAL-W2 (RM 3 8.4-RM 3.4). After the models
were calibrated with data collected during the 1994 low-flow season,
they were used to simulate various hypothetical water-management
scenarios. Results from the first 10 scenarios were published in an
earlier report. This report presents the results of an additional 16
scenarios for both 1994 and 1995 conditions. In all 16 scenarios, the
State's temperature standard (17.8oC) was exceeded in much
of the lower reaches of the Tualatin River during the warmer months in
both years.
- The effect of diverting 1.33 ft3/s (cubic feet per
second) of Rock Creek Wastewater-Treatment plant (WWTP) effluent for
irrigation was evaluated. Temperatures downstream of that facility (RM
38.1) for most months decreased about 0.05oC or
less. Farther downstream, near RM 10, the effect was almost
negligible. The effect of the diversion is slightly more apparent in
the 1994 simulation than in the 1995 simulation. In a similar follow-up
scenario, a constant flow of 1.33 ft3/s was withdrawn from
the river at RM 37.3 and an additional constant flow of 2.0
ft3/s was released from Henry Hagg Lake to compensate. The
effect of this diversion/augmentation on the river system was also
fairly minimal for both 1994 and 1995. Temperatures generally decreased
from RM 60.0 to RM 3.4 by about 0.05 to 0.1oC. For most
months, the overall cooling resulting from this scenario was slightly
greater than the cooling resulting from the former scenario.
- In another set of scenarios, the effect of piping and then releasing
Rock Creek WWTP effluent at two upstream locations (RM 43.8 and RM
55.2) was evaluated. A constant flow of 5 Mgal/d (million gallons per
day) was released at each upstream location, in addition to a constant
release of either 10, 20, or 30 Mgal/d of effluent at RM
38.1. Temperatures increased between RM 55.2 and RM 38.1 by about 1.0oC
or less, but were still within compliance with the water-quality
standard. Downstream of RM 38.1 the river temperature decreased
(generally 0.6oC or less) if the release from Rock Creek WWTP was only
10 Mgal/d. If the release from Rock Creek WWTP was 20 or 30 Mgal/d,
temperatures downstream of RM 38.1 generally increased. However, the
magnitude of the increase was generally less than 1.0oC.
- The temperature effect resulting from constant 25, 45, or 65
Mgal/d effluent releases from the Rock Creek (RM 38.1) and Durham (RM
9.3) WWTPs was evaluated. Temperatures throughout the reach downstream
of Rock Creek WWTP and, to a lesser extent downstream of Durham WWTP,
increased proportionately. The magnitude of the increases was as much
as 0.6, 1.5, and 2.2oC for the three scenarios, respectively.
- In another scenario, a cooler water-temperature data set,
representing more shaded "natural" background conditions, was used as
input to the model upper boundary at Gaston (RM 63.9). Water
temperatures decreased substantially between RM 63.9 and the confluence
with Scoggins Creek (RM 60.0) by as much as 4.0ooC. In a follow-up scenario, the same model upper
boundary condition was used in conjunction with the "natural"
background conditions scenario from an earlier study. Water
temperatures again decreased substantially between RM 63.9 and the
confluence with Scoggins Creek (RM 60.0). However, between Scoggins
Creek and the Dairy Creek confluence (RM 44.8), water temperatures
gradually increased because the unnaturally cool water released from
Henry Hagg Lake was not present. However, almost all of the reach above
Rood Bridge (RM 38.4) was still in compliance with the water-quality
standard. Below RM 38.4 temperatures increased (1.0oC or
less) for July and August and decreased for other months.
- The effect of setting the temperature of effluent released at RM
38.1 and RM 9.3 equal to the temperature of the river was
evaluated. Temperatures downstream of RM 38.1 decreased by as much as
2.4oC. The reduction then tapered off to 0.5oC
upstream of RM 9.3. Downstream of RM 9.3, temperatures decreased by as
much as 1.2oC.
- Another scenario was used to evaluate the effect of releasing a
purchased allotment of Scoggins Dam flow (up to, but not exceeding 10
Mgal/d) at RM 38.1 instead of into Scoggins Creek. Observed Scoggins
Dam temperature data were used for the allotted flow. Temperatures
increased for all months except October from RM 60.0 to RM 38.1 by as
much as 0.6oC. However, downstream of RM 38.1, temperatures
decreased from as much as 0.7oC for all months except
October. However, the effect of the supplemental release became less
pronounced farther downstream.
- The effect of constant effluent releases of 20, 25, 45, and 65
Mgal/d at two WWTPs (RM 38.1 and RM 9.3) was evaluated. The 1994 and
1995 measured effluent temperature data from the WWTPs were used,
except that the temperatures were not permitted to be greater than
17.8oC. For most months, the temperature in the reach
downstream of both WWTPs decreased in all four scenarios. From RM 38.1
to RM 9.3, the temperature decrease was less than
1.0oC. Downstream of the Durham WWTP (RM 9.3), temperatures
decreased almost by 2.0oC.
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supplies last) from:
U.S. Geological Survey, 10615 S.E. Cherry Blossom Drive, Portland,
OR 97216 (ph: 503-251-3201, e-mail info-or@usgs.gov)
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