Menu

HF003
Stream discharge and bedload accumulation in gauged watersheds at the South Umpqua Experimental Forest, Coyote Creek, 1963 to 1981 and 2001 to present

CREATOR(S): Julia A. Jones, Jack S. Rothacher
PRINCIPAL INVESTIGATOR(S): Julia A. Jones
ORIGINATOR(S): Jack S. Rothacher
OTHER RESEARCHER(S): Amy Rusk, Mikeal Jones, Timothy D. Perry, Debra S. Gray, Joseph H. Blanchard
DATA SET CONTACT PERSON: Donald L. Henshaw
METHOD CONTACT: Greg Downing
FORMER INVESTIGATOR: R. Dennis Harr, Richard L. Fredriksen, Craig Creel
DATA SET CREDIT:
All work was carried out by the U.S. Forest Service Pacific Northwest Research Station, Watershed Project, Corvallis, Oregon, from 1963 until 1985. Beginning in 2001 the U. S. Forest Service, Umpqua National Forest, Tiller Ranger District works in conjunction with the PNW Research Station in Corvallis to collect and manage this research data.
MOST RECENT METADATA REVIEW DATE:
20 Apr 2018
KEYWORDS:
hydrology, silviculture, disturbance, sedimentation, hydrologic processes, stream discharge, streamflow, long term monitoring, accumulation, timber harvest, water, sediments, forest ecosystems, watersheds, long term studies
PURPOSE:
Examine the effects on streamflow based on differing silvicultural techniques used in the harvesting of three small watersheds in conjunction with a control watershed in the South Umpqua Experimental Forest. Additionally in an effort to relate forest environments to harvesting techniques and subsequent forest regeneration in southwestern Oregon, the U.S. Forest Service monitored and compared these variables on the three adjacent, harvested experimental watersheds.
METHODS:
Experimental Design - HF003:
Description:

Three adjacent watersheds in the South Umpqua Experimental Forest on Coyote Creek were harvested in summer 1971 after 7 years of pre-treatment stream discharge collection. Data collection was discontinued in 1981 but resumed in 2000. Watershed 1 was was logged as preparation for creating a shelterwood stand, watershed 2 was patch clearcut in 20 small units from 1.6 to 3.3 acres, watershed 3 was cut as one large clearcut, and watershed 4 was left undisturbed as a control.

Citation:

Harr, R. Dennis; Fredriksen, Richard L.; Rothacher, Jack. 1979. Changes in streamflow following timber harvest in southwestern Oregon. Res. Pap. PNW-249. Portland, OR: U.S. Department of Agriculture, Forest Service, Pacific Northwest Forest and Range Experiment Station. 22 p.

Field Methods - HF003:
Description:

Stream discharge is measured on four small gauged watersheds equipped with sharp-crested, 120 degree v-notch weirs. The records of stage are converted to stream discharge by applying a v-notch flume specific rating curve, which is the same for each of the four watersheds (ln y = lna + b ln x, where y = discharge in cubic feet per second, x= gage height in feet, ln a = 1.4884000 and b=2.4489999). Historically, sites have been visited on a 3-week basis and "check sheets" guide the data collection and maintenance activities for the visit. The instrumentation used to measure and record stream stage has changed through the years in response to changes in data collection technology and data management considerations. Leopold-Stevens A-35 (A-71) chart recorders were the primary collection mechanism from the beginning of record through WY 1985, however, Fischer-Porter punched tape recorders were used in lieu of charts from 1967 to 1975. Stage height measurement was switched to Model 2 Stevens Instruments Position Analog Transmitter (PAT) recorders controlled by a data logger shortly after resuming measurement (~2003). Charts are still maintained to provide a visual backup record on two of the four watersheds (WS 3 and 4) with large enough stilling wells to house both the PAT and the Stephens A-71 chart recorder. The discharge measurement is re-initialized every visit to a reference measurement of stream height taken by a hook gage located in an additional stilling well.

Sediment basin surveys are conducted annually since 2000 to determine annual accumulation of bedload. Basin surveys are designed to build basin profiles that are used to determine a change in average bottom elevation between annual surveys. The basins are cleaned annually and resurveyed to provide a base elevation for the following year. Original survey data are summarized in an attachment (1966-1985). Currently, volumetric measurements made with 5-gallon bucket counts and have been used as the basis for calculation since 2002. Historically, a level and leveling rod were used to measure elevation on a point grid and calculations made from the difference in the empty and full basin surveys. From Craig Creel regarding change to bucket counts from a regular survey: We tried to duplicate the historical survey methods, but the transit endpoints were not monumented so we created new ones based on the old notes. One problem with the elevational surveys was the limited number of survey points due to the small size of the basin. Slope points that are usually not included in the calculations because of the difficulty of surveying the exact point when the basin is empty were included just to have a reasonable number of points used in the calculations rater than just a few when the slope is not included (The basins have a large area of sloping sides.). This was one of the reasons we decided to change methods

Instrumentation: Model 2 Stevens Instruments Position Analog Transmitter (PAT) recorder controlled by a data logger (Campbell Scientific CR10X or equivalent); Stevens Type A (A-35 or A-71) recorders; Fischer-Porter punched tape recorders
Processing Procedures - HF003:
Description: Beginning with WY 1964 through WY 1985, all A-35 charts from the Stevens recorder were digitized at the Coweeta Hydrological Lab. However, from WY 1967 through WY 1975, punched tape output was used as the raw record instead of the A-35 charts. This resulted in 15 minute data output during this period. A-35 chart digitizing resumed after WY 1975. Beginning with WY 2001, the process was moved to the Corvallis FSL using a Summagraphics MM1812 digitizer. Consistent digitizing practices have been maintained for all chart data. Campbell scientific data loggers replaced chart digitizing by 2003 as the primary source of streamflow data, and the charts are still collected on CC03 and CC04 and maintained as a backup when electronic data collection fails.
Instrumentation: SummaGraphics 1812 digitizer is able to record up to 40 linear points per mm at highest precision. In practice the digitizer was able to produce raw data points of stage height within .003 ft.
SITE DESCRIPTION:
The watersheds originally supported a mixed conifer forest containing approximately 50,000 board feet per acre (440 m 3 /ha). Douglas-fir (Pseudotsuga menziesii (Mirb.) Franco), grand fir (Abies grandis (Dougl.) Lindl.), incense-cedar (Libocedrus decurrens Torr.), and sugar pine (Pinus Zambertiana Dougl.) predominated in the old growth. Occasional ponderosa pines (Pinus ponderosa Laws.) and western hemlocks (Tsuga heterophylla (Raf.) Sarg.) were also present. Occupying adjacent drainages, the four watersheds comprise 171, 169, 123, and 120 acres (69.2, 68.2, 49.8 and 48.6 ha). These Coyote Creek watersheds are referred to as GSCC01 , GSCC02, GSCC03 and GSCC04 (control). Three of these watersheds were harvested during the summer of 1971, but different methods were used on each. A preparatory cut for creating a shelterwood stand was applied in one watershed (CC01), clearcutting in the other two. Slash treatment varied, but no broadcast burning was done anywhere on the study area. Twenty small units from 1.6 to 3.3 acres (0.65 to 1.34 ha) in size were clearcut on CC02; 10 were tractor-yarded and 10 were high-lead yarded. Slash was machine-piled and burned on all the tractor-yarded units. CC03 was clearcut as one large 123-acre (49.8-ha) unit. Both high-lead and tractor yarding were used.
TAXONOMIC SYSTEM:
None
GEOGRAPHIC EXTENT:
The four Coyote Creek Experimental watersheds are located about 55 km southeast of Roseburg, Oregon, at the head of Coyote Creek, a small tributary of Buckeye Creek which flows into the South Umpqua River (T. 29 S, R. 1 E) in the southwestern Cascades of Oregon.
ELEVATION_MINIMUM (meters):
730
ELEVATION_MAXIMUM (meters):
1065
MEASUREMENT FREQUENCY:
5 minutes
PROGRESS DESCRIPTION:
Active
UPDATE FREQUENCY DESCRIPTION:
annually
CURRENTNESS REFERENCE:
Ground condition