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1. High-resolution Thermal Infrared and True-color Imagery Mosaics, Longitudinal Stream Temperature Profiles, and Thermal Points of Interest from Airborne Surveys of the Quillayute River Basin, August 2022
This dataset presents high-resolution thermal infrared (TIR) and true-color RGB (red, green, blue) imagery mosaics, longitudinal stream temperature profiles, thermal points of interest, and river centerlines from airborne surveys of the Quillayute, Dickey, Sol Duc, Calawah, South Fork Calawah, Sitkum, and Bogachiel Rivers (203 river kilometers; 126 river miles total). All datasets were produced and initially processed by NV5 Geospatial (NV5). The U.S. Geological Survey (USGS) performed additional processing of the longitudinal stream temperature profiles and thermal points of interest, as described below. TIR and RGB images were acquired by NV5 on August 29-31, 2022, using a FLIR SC6000 LWIR sensor and a Sony Alpha 7R III camera mounted in a fiberglass enclosure to a Bell 206 Long Range helicopter. Images were acquired during afternoon hours to maximize the thermal contrast between the river water and the banks. At a flying altitude of 350-450 m (1,148-1,476 ft) above ground level, the FLIR SC6000 and Sony Alpha 7R III achieved ground sampling distances of less than 50 cm (20 in.) and 10 cm (4 in.), respectively. TIR imagery mosaics (.tif) for individual surveys and a single RGB imagery mosaic (.sid) for the entire study area were developed by NV5, and river centerlines (.shp) were manually digitized by NV5 using the imagery mosaics as guides. Points were then generated by NV5 every 50 m (164 ft) along the centerlines to quantify the longitudinal stream temperature profiles (LTPs; .shp). Summary statistics, in degrees Celsius, were computed by NV5 for each point in the profile by sampling pixel values of water temperature along the centerline in the corresponding TIR mosaic within a 2-m (6.56 ft) radius buffer around each point. The statistical information was used by USGS to identify sampling points that fall on non-water features such as boulders or bridges, and then filter these points from the final dataset. LTPs assist in identifying the water temperature gradient in the river and changes in the gradient due to the potential influence of thermal exchange processes, such as water inflows (tributaries, lateral groundwater flow, hyporheic flow, etc.) or increased heating from a low percentage of effective riparian shading. These profiles are also an important component of models that estimate water temperature based on climate and land use scenarios. Thermal points of interest (POIs; .shp) were manually identified by NV5 and USGS across the channel, riparian zone, and floodplain. Such features include cold-water anomalies that may represent thermal refuges and serve as salmonid habitat. POIs were classified by USGS as one of four types: (1) tributary; (2) lateral groundwater / side channel / small tributary; (3) hyporheic / diffuse groundwater; or (4) point source effluent. Summary statistics were computed by USGS for each POI using a sample of water temperature values from pixels in the corresponding TIR mosaic within a 0.6-m (1.97 ft) radius buffer around each point. The automated sampling of the POIs included pixels that are not purely water, but instead mixed with other in-stream and riparian features, such as boulders, woody debris, and tree canopy. Therefore, the water temperatures reported for POIs where the 0.6-m radius sampling area contains mixed pixels are often skewed. The POI temperatures should thus serve as indicators where thermal heterogeneity requires additional investigation and potentially more precise quantification. All data is projected in UTM 10N and the horizontal datum is NAD83(2011).
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Airborne Thermal Infrared and High-resolution True-color Imagery and Longitudinal Profiles of Stream Temperatures, Upper Donner und Blitzen River Basin, Oregon, August 2020
공공데이터포털
This dataset includes georeferenced, high-resolution, airborne thermal infrared (TIR) and high-resolution true-color imagery, a polyline shapefile of the channel centerline, a polyline shapefile with TIR sample points for longitudinal stream temperature profiles, and a tabular file with longitudinal stream temperature profiles for the Donner und Blitzen River and its tributaries, Oregon. The aerial TIR surveys were conducted with a helicopter by NV5 Geospatial and are published as 17 raster mosaics in GeoTiff format with a resolution of 0.3 meters (m). The TIR mosaics contain corrected surface temperatures in degrees Celsius (C) (multiplied by 10 to create an unsigned integer pixel type). The longitudinal stream temperature profiles have temperatures in degrees C. The TIR dataset encompasses 159 kilometers (km) of the Donner und Blitzen River and its tributaries that extends from near Frenchglen, Oregon into the basin headwaters on Steens Mountain. The TIR surveys were collected during the afternoons (13:00-17:00) of August 13, 14, and 15, 2020. The TIR surveys were calibrated using continuous temperature loggers deployed at 29 in-stream locations distributed longitudinally throughout the survey area. The true-color imagery is published as a single raster mosaic of the entire surveyed upper Donner und Blitzen River basin stream network with a resolution of 0.1 m. Channel centerlines were manually digitized within a geographic information system. Stream temperatures for longitudinal profiles were sampled using both automated and manual methods along the channel centerline from the TIR imagery. The stream temperatures were plotted versus channel distances upstream along the Donner und Blitzen River, starting from the bridge over the river near Page Springs Campground to create longitudinal stream temperature profiles, which may be used to interpret groundwater discharge patterns and to identify potential cold-water refuges.
Airborne Thermal Infrared and High-resolution True-color Imagery and Longitudinal Profiles of Stream Temperatures, Upper Donner und Blitzen River Basin, Oregon, August 2020
공공데이터포털
This dataset includes georeferenced, high-resolution, airborne thermal infrared (TIR) and high-resolution true-color imagery, a polyline shapefile of the channel centerline, a polyline shapefile with TIR sample points for longitudinal stream temperature profiles, and a tabular file with longitudinal stream temperature profiles for the Donner und Blitzen River and its tributaries, Oregon. The aerial TIR surveys were conducted with a helicopter by NV5 Geospatial and are published as 17 raster mosaics in GeoTiff format with a resolution of 0.3 meters (m). The TIR mosaics contain corrected surface temperatures in degrees Celsius (C) (multiplied by 10 to create an unsigned integer pixel type). The longitudinal stream temperature profiles have temperatures in degrees C. The TIR dataset encompasses 159 kilometers of the Donner und Blitzen River and its tributaries that extends from near Frenchglen, Oregon into the basin headwaters on Steens Mountain. The TIR surveys were collected during the afternoons (13:00-17:00) of August 13, 14, and 15, 2020. The TIR surveys were calibrated using continuous temperature loggers deployed at 29 in-stream locations distributed longitudinally throughout the survey area. The true-color imagery is published as a single raster mosaic of the entire surveyed upper Donner und Blitzen River basin stream network with a resolution of 0.1 m. Channel centerlines were manually digitized within a geographic information system. Stream temperatures for longitudinal profiles were sampled using both automated and manual methods along the channel centerline from the TIR imagery. The stream temperatures were plotted versus channel distances upstream along the Donner und Blitzen River, starting from the bridge over the river near Page Springs Campground to create longitudinal stream temperature profiles, which may be used to interpret groundwater discharge patterns and to identify potential cold-water refuges.
Thermal infrared and photogrammetric data collected by drone for hydrogeologic characterization around two US Geological Survey Next Generation Water Observing Systems stream gage locations near Claryville, NY, USA
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The U.S. Geological Survey (USGS) collected low-altitude (typically 200-350 ft above land surface) airborne thermal infrared, and visual imagery data via a multirotor, small unoccupied aircraft system (UAS or ‘drone’) deployed along the river corridor encompassing two U.S. Geological Survey Next Generation Water Observing Systems (NGWOS) stream gage locations near Claryville, NY, USA. One site is the West Branch Neversink River at Claryville, NY (USGS station number 01434498) and the Neversink River at Claryville, NY (USGS station number 01435000). Beginning in summer 2019 these stations serve as groundwater/surface water instrumentation ‘test beds’ for the NGWOS program. Data collected at the sites include water electrical conductivity, level, and temperature in mapped groundwater discharge zones adjacent to the gage houses, soil moisture on the streambank, and a suite of supporting atmospheric data. Unmanned aviation system-based visible-light imagery data were collected from October 8-10, 2019 in .jpg format, and the images were compiled automatically into a larger stitched image (orthomosaic) using Agisoft Metashape (Agisoft LLC, St. Petersburg, Russia) software as described in the ‘processed_data’ subfolders of this data release. Structure from Motion techniques were also applied to the visual imagery to derive time-specific, digital surface models (DSM). In addition to the visible-light data, thermal infrared still images were collected in radiometric .tif format. Thermal data were compiled into orthomosaics and DSMs in a similar manner to visible light imagery.
Thermal infrared and photogrammetric data collected by drone for hydrogeologic characterization around two US Geological Survey Next Generation Water Observing Systems stream gage locations near Claryville, NY, USA
공공데이터포털
The U.S. Geological Survey (USGS) collected low-altitude (typically 200-350 ft above land surface) airborne thermal infrared, and visual imagery data via a multirotor, small unoccupied aircraft system (UAS or ‘drone’) deployed along the river corridor encompassing two U.S. Geological Survey Next Generation Water Observing Systems (NGWOS) stream gage locations near Claryville, NY, USA. One site is the West Branch Neversink River at Claryville, NY (USGS station number 01434498) and the Neversink River at Claryville, NY (USGS station number 01435000). Beginning in summer 2019 these stations serve as groundwater/surface water instrumentation ‘test beds’ for the NGWOS program. Data collected at the sites include water electrical conductivity, level, and temperature in mapped groundwater discharge zones adjacent to the gage houses, soil moisture on the streambank, and a suite of supporting atmospheric data. Unmanned aviation system-based visible-light imagery data were collected from October 8-10, 2019 in .jpg format, and the images were compiled automatically into a larger stitched image (orthomosaic) using Agisoft Metashape (Agisoft LLC, St. Petersburg, Russia) software as described in the ‘processed_data’ subfolders of this data release. Structure from Motion techniques were also applied to the visual imagery to derive time-specific, digital surface models (DSM). In addition to the visible-light data, thermal infrared still images were collected in radiometric .tif format. Thermal data were compiled into orthomosaics and DSMs in a similar manner to visible light imagery.
Water Temperature Dynamics in the Quillayute River Basin, Washington, 2021 - 2023
공공데이터포털
The Quillayute River Basin in northwestern Washington consists of the Quillayute River and the river systems of its major tributaries, the Dickey, Sol Duc, and Bogachiel Rivers. With a drainage area of 629 square miles, the Quillayute River Basin provides important habitat for 23 distinct runs of anadromous steelhead and salmon, representing one of the largest and most productive watersheds on the Washington coast (Nelson, 1982; Hunter, 2006). The Quileute Tribe maintains treaty-protected fisheries at usual and accustomed areas in the Quillayute River Basin; however, these fisheries are currently at risk during the late summer as water temperatures within these areas may exceed the specific thermal tolerances of salmonids and other cold-water aquatic species. To inform the planning and prioritization of projects that aim to improve the availability of cold-water habitat in the Quillayute River Basin, the U.S. Geological Survey (USGS), in cooperation with the Quileute Tribe and Wild Salmon Center, utilized various methods to characterize the late-summer water temperature dynamics of the Quillayute River Basin. These study components and their corresponding objectives included the following: - Thermal infrared surveys to map and profile water surface temperatures and identify thermal points of interest in the Quillayute River and its major tributaries (126 river miles total). - Paired air-stream temperature analysis to evaluate the groundwater influence and thermal sensitivity of 11 sites within the Quillayute River Basin. Repeated longitudinal near-surface and near-bottom water temperature float surveys to locate temperature changes indicative of groundwater discharge and assess the tidal influence on water temperatures along the right edge, left edge, and center of the Quillayute River (20 surveys total) - Models of groundwater-surface water exchange using streambed sediment temperature data at 6 sites in the lower Quillayute River and 13 sites in the Quillayute River oxbow ponds. - Cross-sectional profiles of water temperature and specific conductance to support interpretation of continuous water temperature records collected in the Quillayute River oxbow ponds. The data from these study components are included in the Child Items of this Data Release. In addition to the data presented herein, continuous water temperature data at ten sites representing deep pools in the Quillayute River and Quillayute River oxbow ponds were collected and published on the USGS National Water Information System (USGS, 2024a-e, g-k) as part of this study, along with river stage data at an additional site on the Quillayute River (USGS, 2024f). At each of the ten pool sites water temperature was collected at two to three depths in the water column to assess thermal stratification and the potential effect of tides and groundwater discharge. A forthcoming USGS Scientific Investigations Report will provide interpretation of all data published for this study. References Cited: Hunter, J.W., 2006, Quillayute Watershed Prioritized Salmon Restoration Projects: Quileute Natural Resources, accessed May 29, 2024, at https://quileutenation.org/natural-resources/salmon-restoration/. Nelson, L.M., 1982, Streamflow and sediment transport in the Quillayute River basin, Washington: U.S. Geological Survey Open-File Report 82-627, 33 p. [Also available online at https://pubs.usgs.gov/publication/ofr82627] U.S. Geological Survey (USGS), 2024a, USGS 475408124342701 Quillayute River Oxbow Hockey Pond nr La Push, WA, in USGS water data for the Nation: U.S. Geological Survey National Water Information System database, accessed May 29, 2024, at https://doi.org/10.5066/F7P55KJN. [Site information directly accessible at https://waterdata.usgs.gov/nwis/uv?site_no=475408124342701.] U.S. Geological Survey (USGS), 2024b, USGS 475413124351219 Quillayute R Oxbow Long Pond South nr La Push, WA, in USGS water data for the Nation: U.S. Geological Survey National Water Information
Water Temperature Dynamics in the Quillayute River Basin, Washington, 2021 - 2023
공공데이터포털
The Quillayute River Basin in northwestern Washington consists of the Quillayute River and the river systems of its major tributaries, the Dickey, Sol Duc, and Bogachiel Rivers. With a drainage area of 629 square miles, the Quillayute River Basin provides important habitat for 23 distinct runs of anadromous steelhead and salmon, representing one of the largest and most productive watersheds on the Washington coast (Nelson, 1982; Hunter, 2006). The Quileute Tribe maintains treaty-protected fisheries at usual and accustomed areas in the Quillayute River Basin; however, these fisheries are currently at risk during the late summer as water temperatures within these areas may exceed the specific thermal tolerances of salmonids and other cold-water aquatic species. To inform the planning and prioritization of projects that aim to improve the availability of cold-water habitat in the Quillayute River Basin, the U.S. Geological Survey (USGS), in cooperation with the Quileute Tribe and Wild Salmon Center, utilized various methods to characterize the late-summer water temperature dynamics of the Quillayute River Basin. These study components and their corresponding objectives included the following: - Thermal infrared surveys to map and profile water surface temperatures and identify thermal points of interest in the Quillayute River and its major tributaries (126 river miles total). - Paired air-stream temperature analysis to evaluate the groundwater influence and thermal sensitivity of 11 sites within the Quillayute River Basin. Repeated longitudinal near-surface and near-bottom water temperature float surveys to locate temperature changes indicative of groundwater discharge and assess the tidal influence on water temperatures along the right edge, left edge, and center of the Quillayute River (20 surveys total) - Models of groundwater-surface water exchange using streambed sediment temperature data at 6 sites in the lower Quillayute River and 13 sites in the Quillayute River oxbow ponds. - Cross-sectional profiles of water temperature and specific conductance to support interpretation of continuous water temperature records collected in the Quillayute River oxbow ponds. The data from these study components are included in the Child Items of this Data Release. In addition to the data presented herein, continuous water temperature data at ten sites representing deep pools in the Quillayute River and Quillayute River oxbow ponds were collected and published on the USGS National Water Information System (USGS, 2024a-e, g-k) as part of this study, along with river stage data at an additional site on the Quillayute River (USGS, 2024f). At each of the ten pool sites water temperature was collected at two to three depths in the water column to assess thermal stratification and the potential effect of tides and groundwater discharge. A forthcoming USGS Scientific Investigations Report will provide interpretation of all data published for this study. References Cited: Hunter, J.W., 2006, Quillayute Watershed Prioritized Salmon Restoration Projects: Quileute Natural Resources, accessed May 29, 2024, at https://quileutenation.org/natural-resources/salmon-restoration/. Nelson, L.M., 1982, Streamflow and sediment transport in the Quillayute River basin, Washington: U.S. Geological Survey Open-File Report 82-627, 33 p. [Also available online at https://pubs.usgs.gov/publication/ofr82627] U.S. Geological Survey (USGS), 2024a, USGS 475408124342701 Quillayute River Oxbow Hockey Pond nr La Push, WA, in USGS water data for the Nation: U.S. Geological Survey National Water Information System database, accessed May 29, 2024, at https://doi.org/10.5066/F7P55KJN. [Site information directly accessible at https://waterdata.usgs.gov/nwis/uv?site_no=475408124342701.] U.S. Geological Survey (USGS), 2024b, USGS 475413124351219 Quillayute R Oxbow Long Pond South nr La Push, WA, in USGS water data for the Nation: U.S. Geological Survey National Water Information
Water Temperature Mapping of the Skykomish, Snoqualmie, and Middle Fork Snoqualmie Rivers, Washington—Longitudinal Stream Temperature Profiles, Significant Thermal Features, and Airborne Thermal Infrared and RGB Imagery Mosaics
공공데이터포털
The Skykomish, Snoqualmie, and Middle Fork Snoqualmie River Basins have historically provided critical spawning, rearing, and core habitat for several salmonid species. These salmonid species include natural populations of Chinook salmon (O. tshawytscha), steelhead trout (O. mykiss), and bull trout (Salvelinus confluentus)—listed as “Threatened” under the Endangered Species Act—as well as coho salmon (O. kisutch)—listed as a ”Species of concern”—pink salmon (O. gorbuscha), chum salmon (O. keta), and native char (S. malma) (Solomon and Boles, 2002; Stohr and others, 2011; Svrjcek and others, 2013; Snohomish County Surface Water Management and the Sustainable Lands Strategy Executive Committee [SWM], 2017; U.S. Fish and Wildlife Service, 2022). Because of the thermal constraints on salmonids and other aquatic species, the Washington Department of Ecology maintains temperature criteria for waters designated for aquatic life uses. These standards range between 12 degrees Celsius (°C) and 17.5 °C, referring to the highest permissible 7-day average of the daily maximum temperatures (7-DADMax), and vary depending on the habitat classification and time of year (Washington Department of Ecology, 2020). Over the past two decades, however, summer 7-DADMax water temperatures within the Skykomish, Snoqualmie, and Middle Fork Snoqualmie Rivers have frequently exceeded these temperature criteria, as well as the 23 °C threshold above which temperatures can be lethal to salmonids (Stohr and others, 2011; Svrjcek and others, 2013; Kubo and leDoux, 2016). To inform salmonid restoration efforts within the Skykomish, Snoqualmie, and Middle Fork Snoqualmie Rivers, this study used high-resolution thermal infrared (TIR) and co-acquired true-color red, green, blue (RGB) imagery from airborne surveys conducted in August 2020 and 2021. The imagery mosaics from the airborne TIR and RGB surveys were used to measure the longitudinal stream temperature profiles (LTPs) of the Skykomish, Snoqualmie, and Middle Fork Snoqualmie Rivers and identify the location of significant thermal features (STFs) expressed at the water’s surface, including cold-water anomalies that could represent thermal refuges and serve as salmonid habitat. These surveys were done twice to evaluate the interannual persistence of STFs and the temporal variability of water temperature patterns in the LTPs, because the presence of STFs and the patterns in LTPs have been shown to vary over time in other studies (Dugdale and others, 2013). The study area for the TIR and RGB surveys, from upstream to downstream, was (1) the Middle Fork Snoqualmie River from above the Goldmyer Hot Springs trailhead to the North Fork Snoqualmie River confluence (33 river miles), (2) the mainstem Snoqualmie River from the North Fork Snoqualmie River confluence to Chinook Bend Natural Area in Carnation, Washington (23 river miles), and (3) the Skykomish River from Gold Bar, Washington to its confluence with the Snoqualmie River in Monroe, Washington (26 river miles). Those results are presented with the following items: - TIR and RGB imagery mosaics (.tiff and .sid, respectively) of the Skykomish Snoqualmie, and Middle Fork Snoqualmie Rivers. - LTPs (.shp) produced from the thermal infrared imagery mosaics. - STFs (.shp) identified using the thermal infrared and true-color red, green, blue imagery mosaics. In addition, water temperature float surveys were conducted on the Skykomish and Middle Fork Snoqualmie Rivers, August–September 2020, and a follow-up survey on the Middle Fork Snoqualmie River August 2021, to evaluate this less expensive and low-tech method of producing LTPs. Float survey data was collected by measuring near-surface and near-streambed (henceforth, “near-bottom”) water temperature, conductivity, and GPS position at three-second intervals from an inflatable kayak drifting downstream at ambient river velocity, following the method of Vaccaro and Maloy (2006). By moving downstream at ambient
Water Temperature Mapping of the Skykomish, Snoqualmie, and Middle Fork Snoqualmie Rivers, Washington—Longitudinal Stream Temperature Profiles, Significant Thermal Features, and Airborne Thermal Infrared and RGB Imagery Mosaics
공공데이터포털
The Skykomish, Snoqualmie, and Middle Fork Snoqualmie River Basins have historically provided critical spawning, rearing, and core habitat for several salmonid species. These salmonid species include natural populations of Chinook salmon (O. tshawytscha), steelhead trout (O. mykiss), and bull trout (Salvelinus confluentus)—listed as “Threatened” under the Endangered Species Act—as well as coho salmon (O. kisutch)—listed as a ”Species of concern”—pink salmon (O. gorbuscha), chum salmon (O. keta), and native char (S. malma) (Solomon and Boles, 2002; Stohr and others, 2011; Svrjcek and others, 2013; Snohomish County Surface Water Management and the Sustainable Lands Strategy Executive Committee [SWM], 2017; U.S. Fish and Wildlife Service, 2022). Because of the thermal constraints on salmonids and other aquatic species, the Washington Department of Ecology maintains temperature criteria for waters designated for aquatic life uses. These standards range between 12 degrees Celsius (°C) and 17.5 °C, referring to the highest permissible 7-day average of the daily maximum temperatures (7-DADMax), and vary depending on the habitat classification and time of year (Washington Department of Ecology, 2020). Over the past two decades, however, summer 7-DADMax water temperatures within the Skykomish, Snoqualmie, and Middle Fork Snoqualmie Rivers have frequently exceeded these temperature criteria, as well as the 23 °C threshold above which temperatures can be lethal to salmonids (Stohr and others, 2011; Svrjcek and others, 2013; Kubo and leDoux, 2016). To inform salmonid restoration efforts within the Skykomish, Snoqualmie, and Middle Fork Snoqualmie Rivers, this study used high-resolution thermal infrared (TIR) and co-acquired true-color red, green, blue (RGB) imagery from airborne surveys conducted in August 2020 and 2021. The imagery mosaics from the airborne TIR and RGB surveys were used to measure the longitudinal stream temperature profiles (LTPs) of the Skykomish, Snoqualmie, and Middle Fork Snoqualmie Rivers and identify the location of significant thermal features (STFs) expressed at the water’s surface, including cold-water anomalies that could represent thermal refuges and serve as salmonid habitat. These surveys were done twice to evaluate the interannual persistence of STFs and the temporal variability of water temperature patterns in the LTPs, because the presence of STFs and the patterns in LTPs have been shown to vary over time in other studies (Dugdale and others, 2013). The study area for the TIR and RGB surveys, from upstream to downstream, was (1) the Middle Fork Snoqualmie River from above the Goldmyer Hot Springs trailhead to the North Fork Snoqualmie River confluence (33 river miles), (2) the mainstem Snoqualmie River from the North Fork Snoqualmie River confluence to Chinook Bend Natural Area in Carnation, Washington (23 river miles), and (3) the Skykomish River from Gold Bar, Washington to its confluence with the Snoqualmie River in Monroe, Washington (26 river miles). Those results are presented with the following items: - TIR and RGB imagery mosaics (.tiff and .sid, respectively) of the Skykomish Snoqualmie, and Middle Fork Snoqualmie Rivers. - LTPs (.shp) produced from the thermal infrared imagery mosaics. - STFs (.shp) identified using the thermal infrared and true-color red, green, blue imagery mosaics. In addition, water temperature float surveys were conducted on the Skykomish and Middle Fork Snoqualmie Rivers, August–September 2020, and a follow-up survey on the Middle Fork Snoqualmie River August 2021, to evaluate this less expensive and low-tech method of producing LTPs. Float survey data was collected by measuring near-surface and near-streambed (henceforth, “near-bottom”) water temperature, conductivity, and GPS position at three-second intervals from an inflatable kayak drifting downstream at ambient river velocity, following the method of Vaccaro and Maloy (2006). By moving downstream at ambient
3. Longitudinal Stream Temperature Profiles from Float Surveys of the Quillayute River, August 2021 and 2022
공공데이터포털
This dataset provides a zipfile containing 20 shapefiles with geo-referenced longitudinal water temperature profiles (LTPs; .shp). Profiles were obtained from longitudinal “Lagrangian” drag-probe temperature surveys ("float surveys") of the Quillayute River. Near-streambed and near-surface water temperature and conductivity were measured at three-second intervals and the spatial locations of each measurement was recorded using a GPS from a kayak drifting downstream at ambient stream velocity following the method of Vaccaro and Maloy (2006). The study area consisted of the Quillayute River from its upstream-most point at the confluence of the Sol Duc and Bogachiel Rivers to its outlet at the Pacific Ocean (8 river kilometers). The float surveys were conducted August (Aug.) 10 and 11, 2021, and Aug. 2 and 3, 2022, during different tidal conditions. Three longitudinal profiles were measured near-simultaneously on each survey date, along the left bank, right bank, and thalweg. Each shapefile was named according to the depth of the measurements at near-surface (SRF) or near-streambed (BED), and whether it was along the left bank (L), right bank (R), or thalweg (C). Only twenty profiles are included because data from four surveys was unusable due to sensor malfunction. The missing profiles were from the following dates and sensor locations: Aug. 10, 2021, near-surface left bank; Aug. 10, 2021, near-streambed left bank; Aug. 11, 2021, near-surface right bank; and Aug. 3, 2022, near-streambed left bank. Two of the sensors used in the float surveys had temperature values adjusted by -0.2 degrees Celsius to correct for calibration drift, based on pre-survey verification readings. This correction was applied to the near-streambed thalweg surveys on Aug. 10 and 11, 2021, the near-surface right bank survey on Aug. 10, 2021, the near-streambed left bank survey on Aug. 11, 2021, and the near-surface thalweg and near-streambed right bank surveys on Aug. 2 and 3, 2022. Float surveys targeted a start time in the late morning and an end time in the late afternoon during the diurnal increase in water temperature such that deviations from the diurnal increase may be attributed to groundwater discharge, tributaries, or other sources of water that differ in temperature from the river. The data is projected in UTM10N and the horizontal datum is NAD83(2011). Reference Cited: Vaccaro, J.J., Keys, M.E., Julich, R.J., and Welch, W.B., 2008, Thermal profiles for selected river reaches in the Yakima River Basin, Washington: U.S. Geological Survey Data Series 342. [Also available online at https://pubs.usgs.gov/ds/342].
3. Longitudinal Stream Temperature Profiles from Float Surveys of the Quillayute River, August 2021 and 2022
공공데이터포털
This dataset provides a zipfile containing 20 shapefiles with geo-referenced longitudinal water temperature profiles (LTPs; .shp). Profiles were obtained from longitudinal “Lagrangian” drag-probe temperature surveys ("float surveys") of the Quillayute River. Near-streambed and near-surface water temperature and conductivity were measured at three-second intervals and the spatial locations of each measurement was recorded using a GPS from a kayak drifting downstream at ambient stream velocity following the method of Vaccaro and Maloy (2006). The study area consisted of the Quillayute River from its upstream-most point at the confluence of the Sol Duc and Bogachiel Rivers to its outlet at the Pacific Ocean (8 river kilometers). The float surveys were conducted August (Aug.) 10 and 11, 2021, and Aug. 2 and 3, 2022, during different tidal conditions. Three longitudinal profiles were measured near-simultaneously on each survey date, along the left bank, right bank, and thalweg. Each shapefile was named according to the depth of the measurements at near-surface (SRF) or near-streambed (BED), and whether it was along the left bank (L), right bank (R), or thalweg (C). Only twenty profiles are included because data from four surveys was unusable due to sensor malfunction. The missing profiles were from the following dates and sensor locations: Aug. 10, 2021, near-surface left bank; Aug. 10, 2021, near-streambed left bank; Aug. 11, 2021, near-surface right bank; and Aug. 3, 2022, near-streambed left bank. Two of the sensors used in the float surveys had temperature values adjusted by -0.2 degrees Celsius to correct for calibration drift, based on pre-survey verification readings. This correction was applied to the near-streambed thalweg surveys on Aug. 10 and 11, 2021, the near-surface right bank survey on Aug. 10, 2021, the near-streambed left bank survey on Aug. 11, 2021, and the near-surface thalweg and near-streambed right bank surveys on Aug. 2 and 3, 2022. Float surveys targeted a start time in the late morning and an end time in the late afternoon during the diurnal increase in water temperature such that deviations from the diurnal increase may be attributed to groundwater discharge, tributaries, or other sources of water that differ in temperature from the river. The data is projected in UTM10N and the horizontal datum is NAD83(2011). Reference Cited: Vaccaro, J.J., Keys, M.E., Julich, R.J., and Welch, W.B., 2008, Thermal profiles for selected river reaches in the Yakima River Basin, Washington: U.S. Geological Survey Data Series 342. [Also available online at https://pubs.usgs.gov/ds/342].