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Research about Columbia River, Snake River

Source-linked reports with geographic coverage including Columbia River, Snake River.

10 recordsLinked to original sources
USGS2023

Monitoring native nonsalmonids for the incidence of gas bubble trauma downstream of Snake and Columbia River dams during the spring spill season, 2022

In 2020, a new spill program was implemented to aid the downstream passage of juvenile salmonids at mainstem dams on the Snake and Columbia rivers. Under this program, the total dissolved gas (TDG) cap was increased to 125% and monitoring of native nonsalmonids for gas bubble trauma (GBT) became a requirement. The primary objective of this work was to measure the incidence and severity of GBT in native nonsalmonids resulting from increased juvenile fish passage spill and associated levels of TDG during the spring spill period. Native nonsalmonids were collected downstream from Bonneville, McNary, Ice Harbor, and Lower Granite dams and examined for the incidence and severity of GBT in 2022. Fish were collected at each location weekly (4 April to 13 June) during the spring spill period by backpack electrofishing and beach seining. Washington and Oregon state water quality agencies established minimum and target sample sizes for monitoring, but the minimum sample size of 50 fish and target sample size of 100 fish were not met in all weeks at individual projects due to high water flows and resulting low fish collections. Collected fish were examined for GBT according to the criteria and protocol established for the regional smolt monitoring program (SMP). Overall, GBT incidence and severity rankings were low and did not exceed the thresholds that would have triggered changes to the spill program. Using SMP criteria, maximum weekly GBT incidences were 1.9% downstream from Bonneville Dam, 8.6% downstream from McNary Dam, 7.7% downstream from Ice Harbor Dam, and 3.4% downstream from Lower Granite Dam. In contrast to 2021, several species showed signs of GBT in 2022, and GBT was commonly observed in fins and body locations other than the unpaired fins and eyes (i.e., SMP criteria). In general, the observed signs of GBT according to SMP criteria were not severe (i.e., ranks 1 and 2). Although TDG reached the gas cap, particularly late in the spring spill season, GBT incidence rates were not high probably due to factors such as habitat-related variability in TDG, species composition and varying tolerance to high TDG, low power to detect GBT incidence at small sample sizes, and unknown exposure history.

Oregon, Washington↗
USGS2023

Nonsalmonid gas bubble trauma investigations

From 2020 to 2023, a new spill program was implemented to aid the downstream passage of juvenile salmonids at mainstem dams on the Snake and Columbia rivers. Under this program, the total dissolved gas (TDG) cap was increased to 125% and monitoring of nonsalmonids for gas bubble trauma (GBT) became a requirement. The primary objective of this work and report was to measure the incidence and severity of GBT in nonsalmonids resulting from increased juvenile salmonid passage spill and associated levels of TDG during the spring spill period in 2023. Nonsalmonids were collected downstream from Bonneville, McNary, Ice Harbor, and Lower Granite dams and examined for the incidence and severity of GBT in 2023. Fish were collected at each location weekly (3 April to 20 June) during the spring spill period by backpack electrofishing and beach seining. Washington and Oregon State water quality agencies established minimum and target sample sizes for monitoring, but the minimum sample size of 50 fish and target sample size of 100 fish were not met in all weeks at individual projects due to high water flows and resulting low fish collections. Collected fish were examined for GBT according to the criteria and protocol established for the regional smolt monitoring program (SMP). TDG levels were often high relative to the 10-year average. GBT incidence rates and severity (according to SMP criteria) were low to moderate in most weeks. We found no apparent relationship between GBT incidence and TDG due to exposure history and interspecies susceptibility to elevated TDG that could not be quantified. GBT incidence rates exceeded the 15% threshold on two occasions below Ice Harbor Dam, triggering a reduction in spill under the State water quality standards. In the weeks immediately following the spill reductions, GBT incidence was zero or relatively low at this location. Sculpin (genus Cottus ) was the main species collected at all locations. As in past years, we did find GBT in non-SMP protocol areas, particularly in sculpin. The variability in GBT incidence rates is likely due to variability in environmental conditions, fish exposure history to TDG, and species sensitivity to TDG. Many of the species encountered in shallow shoreline habitats rear for extended times and probably do not seek the water depths that would help them reduce the effects of exposure to elevated TDG through depth compensation. Limited systematic sampling of TDG in the tailraces of each project showed that TDG can vary spatially within the tailrace and with percentage of water spilled. We investigated GBT progression and mortality in sculpin and threespine stickleback ( Gasterosteus aculeatus ) in laboratory experiments (Chapter Two of this report). Fish were tested at 120%, 125%, and 130% TDG. We found that sculpin are more sensitive to TDG than stickleback and that GBT and associated mortality progress faster in sculpin than in stickleback. GBT prevalence and severity increased through time at all TDG levels tested, but relationships between severity and exposure time were weak or nonexistent. GBT and mortality progressed more rapidly as TDG increased in both species. The SMP criteria used to rank GBT did not fully capture the incidence and severity of GBT in sculpin and stickleback compared to using criteria based on all areas of the fish. The lateral line, body, dorsal fin, and pectoral fins were common locations of GBT in sculpin at 120 and 125% TDG, but signs were more prevalent in all areas at 130% TDG. In stickleback, GBT was most common on the head and body at all TDG levels tested. Positive buoyancy of fish with severe GBT was observed in both species and may have consequences for similarly impaired fish in the wild. The proximate cause of GBT-related death in sculpin and stickleback was bubbles in the gills and heart, but unlike in other species, bubbles appeared rapidly just before the point of death. Our results help fill the information void GBT progression and mortality for sculpin and stickleback.

Oregon, Washington↗
USGS2021

Monitoring native, resident nonsalmonids for the incidence of gas bubble trauma downstream of Snake and Columbia River Dams, 2021

In 2020, a new spill program was implemented to aid the downstream passage of juvenile salmonids at mainstem dams on the Snake and Columbia rivers. Under this program, the total dissolved gas (TDG) cap was increased to 125% and monitoring of native, resident nonsalmonid (NRN) fishes for gas bubble trauma (GBT) became a requirement. The primary objective of this work was to measure the incidence and severity of GBT in NRN fishes resulting from increased juvenile fish passage spill and associated levels of TDG during the spring spill period. A secondary objective was to measure the incidence of GBT in incidentally collected juvenile salmonids when NRN sample size targets were met. NRN fishes were collected downstream from Bonneville, McNary, and Ice Harbor dams and examined for the incidence and severity of GBT in 2021. Fish were collected at each location weekly (6 April to 17 June) during the spring spill period by backpack electrofishing and beach seining. Washington and Oregon state water quality agencies established minimum and target sample sizes for monitoring, and in all weeks the minimum sample size of 50 fish was met and in most weeks the target sample size of 100 fish was met. Collected fish were examined for GBT according to the criteria and protocol established for the regional smolt monitoring program (SMP). Overall, GBT incidence and severity rankings were low and did not exceed the thresholds that would have triggered changes to the spill program. Using SMP criteria, weekly GBT incidences ranged from 0 to 1.0% downstream from Bonneville Dam, 0 to 6.2% downstream from McNary Dam, and 0 to 1.9% downstream from Ice Harbor Dam. Except for one three-spined stickleback (Gasterosteus aculeatus) collected downstream of Bonneville Dam, the only NRN species that showed signs of GBT was sculpin spp. GBT was observed in sculpin in body locations other than the unpaired fins and eyes (i.e., SMP criteria). If GBT incidence in all areas on the fish (i.e., paired fins, unpaired fins, eyes, body) are combined, then weekly GBT incidence rates increase and range from 0 to 4.3% downstream from Bonneville Dam, 0 to 15.4% downstream from McNary Dam, and 0 to 4.7% downstream from Ice Harbor Dam. This illustrates the effect of using different criteria to determine the incidence of GBT in NRN fishes. It also shows how the proportion of a species in a sample that is more prone to show GBT can influence GBT incidence rate. On a number of occasions, incidental catch of subyearling fall Chinook salmon were examined for GBT downstream of Bonneville Dam but none showed any signs. The DG was generally below 120% and never reached the 125% gas cap during the spring spill season, which may be why GBT incidence rates were so low as past research has shown that GBT signs in NRN fishes are relatively low below this TDG level.

Oregon, Washington↗
USGS2018

A bioenergetics evaluation of temperature‐dependent selection for the spawning phenology by Snake River fall Chinook salmon

High water temperatures can increase the energetic cost for salmon to migrate and spawn, which can be important for Snake River fall‐run Chinook salmon because they migrate great distances (>500 km) at a time when river temperatures (18–24°C) can be above their optimum temperatures (16.5°C). Average river temperatures and random combinations of migration and spawning dates were used to simulate fish travel times and determine the energetic consequences of different thermal experiences during migration. An energy threshold criterion (4 kJ/g) was also imposed on survival and spawning success, which was used to determine how prevailing temperatures might select against certain migration dates and thermal experiences, and in turn, explain the selection for the current spawning phenology of the population. Scenarios of tributary use for thermal refugia under increasing water temperatures (1, 2, and 3°C) were also run to determine which combinations of migration dates, travel rates, and resulting thermal experiences might be most affected by energy exhaustion. As expected, when compared to observations, the model under existing conditions and energy use could explain the onset, but not the end of the observed spawning migration. Simulations of early migrants had greater energy loss than late migrants regardless of the river temperature scenario, but higher temperatures disproportionately selected against a larger fraction of early‐migrating fish, although using cold‐water tributaries during migration provided a buffer against higher energy use at higher temperatures. The fraction of simulated fish that exceeded the threshold for migration success increased from 58% to 72% as average seasonal river temperatures over baseline temperatures increased. The model supports the conclusion that increases in average seasonal river temperatures as little as 1°C could impose greater thermal constraints on the fish, select against early migrants, and in turn, truncate the onset of the current spawning migration.

Columbia River, Snake River↗
USGS2015

Seasonal dynamics of zooplankton in Columbia–Snake River reservoirs,with special emphasis on the invasive copepod Pseudodiaptomus forbesi

The Asian copepod Pseudodiaptomus forbesi has recently become established in the Columbia River. However, little is known about its ecology and effects on invaded ecosystems. We undertook a 2-year (July 2009 to June 2011) field study of the mesozooplankton in four reservoirs in the Columbia and Snake Rivers, with emphasis on the relation of the seasonal variation in distribution and abundance of P. forbesi to environmental variables. Pseudodiaptomus forbesi was abundant in three reservoirs; the zooplankton community of the fourth reservoir contained no known non-indigenous taxa. The composition and seasonal succession of zooplankton were similar in the three invaded reservoirs: a bloom of rotifers occurred in spring, native cyclopoid and cladoceran species peaked in abundance in summer, and P. forbesi was most abundant in late summer and autumn. In the uninvaded reservoir, total zooplankton abundance was very low year-round. Multivariate ordination indicated that temperature and dissolved oxygen were strongly associated with zooplankton community structure, with P. forbesi appearing to exhibit a single generation per year . The broad distribution and high abundance of P. forbesi in the Columbia–Snake River System could result in ecosystem level effects in areas intensively managed to improve conditions for salmon and other commercially and culturally important fish species.

Columbia River, Snake River↗
USGS2011

Migration depths of juvenile Chinook salmon and steelhead relative to total dissolved gas supersaturation in a Columbia River reservoir

The in situ depths of juvenile salmonids Oncorhynchus spp. were studied to determine whether hydrostatic compensation was sufficient to protect them from gas bubble disease (GBD) during exposure to total dissolved gas (TDG) supersaturation from a regional program of spill at dams meant to improve salmonid passage survival. Yearling Chinook salmon O. tshawytscha and juvenile steelhead O. mykiss implanted with pressure-sensing radio transmitters were monitored from boats while they were migrating between the tailrace of Ice Harbor Dam on the Snake River and the forebay of McNary Dam on the Columbia River during 1997-1999. The TDG generally decreased with distance from the tailrace of the dam and was within levels known to cause GBD signs and mortality in laboratory bioassays. Results of repeated-measures analysis of variance indicated that the mean depths of juvenile steelhead were similar throughout the study area, ranging from 2.0 m in the Snake River to 2.3 m near the McNary Dam forebay. The mean depths of yearling Chinook salmon generally increased with distance from Ice Harbor Dam, ranging from 1.5 m in the Snake River to 3.2 m near the forebay. Juvenile steelhead were deeper at night than during the day, and yearling Chinook salmon were deeper during the day than at night. The TDG level was a significant covariate in models of the migration depth and rates of each species, but no effect of fish size was detected. Hydrostatic compensation, along with short exposure times in the area of greatest TDG, reduced the effects of TDG exposure below those generally shown to elicit GBD signs or mortality. Based on these factors, our results indicate that the TDG limits of the regional spill program were safe for these juvenile salmonids.

Oregon, Washington↗
USGS2003

Comparison of migration rate and survival between radio-tagged and PIT-tagged migrant yearling chinook salmon in the Snake and Columbia rivers

A study was conducted to compare the travel times, detection probabilities, and survival of migrant hatchery-reared yearling chinook salmon Oncorhynchus tshawytscha tagged with either gastrically or surgically implanted sham radio tags (with an imbedded passive integrated transponder [PIT] tag) with those of their cohorts tagged only with PIT tags in the Snake and Columbia rivers. Juvenile chinook salmon with gastrically implanted radio tags migrated significantly faster than either surgically radio-tagged or PIT-tagged fish, while migration rates were similar among surgically radio-tagged and PIT-tagged fish. The probabilities of PIT tag detection at downstream dams varied by less than 5% and were not significantly different among the three groups. Survival was similar among treatments for median travel times of less than approximately 6 d (migration distance of 106 km). However, for both gastrically and surgically radio-tagged fish, survival was significantly less than for PIT-tagged fish, for which median travel times exceeded approximately 10 d (migration distance of 225 km). The results of this study support the use of radio tags to estimate the survival of juvenile chinook salmon having a median fork length of approximately 150 mm (range, 127-285 mm) and a median travel time of migration of less than approximately 6 d.

Oregon, Washington↗
USGS1996

Incidence of Renibacterium salmoninarum infections in juvenile hatchery spring chinook salmon in the Columbia and Snake Rivers

From 1988 through 1992, we assessed the prevalence (frequency of occurrence) and severity (degree of infection) of Renibacterium salmoninarum (RS) among fish in marked groups of Columbia River basin and Snake River basin hatchery spring chinook salmon Oncorhynchus tshawytscha before release and during their seaward migration. During the study, prevalence of RS infection decreased (from >90% to <65%) in six of the eight hatchery groups. We attributed this decrease to changes in hatchery practices that reduced vertical and horizontal transmission. Fish from Snake River hatcheries had a higher prevalence of infection when sampled at dams (mean >90%) than in the hatchery (mean <70%), but there were no differences in similar comparisons of Columbia River fish. Although prevalence and severity of RS infection were not correlated in the groups studied, it appears that fish from the Snake River were more severely infected than those from the Columbia River. Some groups of Snake River fish had higher severity of infection at dams than in the hatchery, but infection in fish from Columbia River hatcheries did not change. These differences between Snake River and Columbia River fish might have resulted from differences in river conditions and the distances from hatcheries to dams.

Oregon, Washington↗