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Peer-reviewed Literature only. If not (gray literature), please add to tab 2
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Author(s)YearTitleJournalJournal #pp.NotesDOIAbstract/Summary
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Ackerman JT, Eagles-Smith CA2010Agricultural wetlands as potential hotspots for mercury bioaccumulation: experimental evidence using caged fish.Environmental Science & Technology44(4)1451-1457
10.1021/es9028364
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Ackerman JT, Miles AK, Eagles-Smith CA2010Invertebrate mercury bioaccumulation in permanent, seasonal, and flooded rice wetlands within California's Central Valley.Science of the Total Environment408(3)666-671
10.1016/j.scitotenv.2009.10.030
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Agostinho A, Agostinho C, Pelicice F, Elineide M2012Fish ladders: safe fish passage or hotspot for predation?Neotropical Ichthyology 10(4)687-696
10.1590/S1679-62252012000400001
Fish ladders are a strategy for conserving biodiversity, as they can provide connectivity between fragmented habitats and reduce predation on shoals that accumulate immediately below dams. Although the impact of predation downstream of reservoirs has been investigated, especially in juvenile salmonids during their downstream movements, nothing is known about predation on Neotropical fish in the attraction and containment areas commonly found in translocation facilities. This study analysed predation in a fish passage system at the Lajeado Dam on the Tocantins River in Brazil. The abundance, distribution, and the permanence (time spent) of large predatory fish along the ladder, the injuries imposed by piranhas during passage and the presence of other vertebrate predators were investigated. From December 2002 to October 2003, sampling was conducted in four regions (downstream, along the ladder, in the forebay, and upstream of the reservoir) using gillnets, cast nets and counts or visual observations. The captured fish were tagged with thread and beads, and any mutilations were registered. Fish, birds and dolphins were the main predator groups observed, with a predominance of the first two groups. The entrance to the ladder, in the downstream region, was the area with the highest number of large predators and was the only region with relevant non-fish vertebrates. The main predatory fish species were Rhaphiodon vulpinus, Hydrolycus armatus, and Serrasalmus rhombeus. Tagged individuals were detected predating along the ladder for up to 90 days. Mutilations caused by Serrasalmus attacks were noted in 36% of species and 4% of individuals at the top of the ladder. Our results suggested that the high density of fish in the restricted ladder environment, which is associated with injuries suffered along the ladder course and the presence of multiple predator groups with different predation strategies, transformed the fish corridor into a hotspot for predation.
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Ahearn DS, Viers JH, Mount JF, Dahlgren RA2006Priming the productivity pump: flood pulse driven trends in suspended algal biomass distribution across a restored floodplain.Freshwater Biology51(8)1417-1433
10.1111/j.1365-2427.2006.01580.x
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Alpers CN, Fleck JA, Marvin-DiPasquale MC, Stricker CA, Stephenson M, Taylor HE2014Mercury cycling in agricultural and managed wetlands, Yolo Bypass, California: Spatial and seasonal variations in water quality.Science of the Total Environment484276-287
10.1016/j.scitotenv.2013.10.096
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Baranyi C, Hein T, Holarek C, Keckeis S, Schiemer F2002Zooplankton biomass and community structure in a Danube River ̄oodplain system: effects of hydrologyFreshwater Biology47473-482
10.1046/j.1365-2427.2002.00822.x
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Bellmore JR, Baxter CV, Ray AM, Denny L, Tardy K, Galloway E2012Assessing the potential for salmon recovery via floodplain restoration: a multitrophic level comparison of dredge-mined to reference segments.Environmental Management 49(3)734-750
10.1007/s00267-012-9813-x
Abstract: Pre-restoration studies typically focus on physical habitat, rather than the food-base that supports aquatic species. However, both food and habitat are necessary to support the species that habitat restoration is frequently aimed at recovering. Here we evaluate if and how the productivity of the food-base that supports fish production is impaired in a dredge-mined floodplain within the Yankee Fork Salmon River (YFSR), Idaho (USA); a site where past restoration has occurred and where more has been proposed to help recover anadromous salmonids. Utilizing an ecosystem approach, we found that the dredged segment had comparable terrestrial leaf and invertebrate inputs, aquatic primary producer biomass, and production of aquatic invertebrates relative to five reference floodplains. Thus, the food-base in the dredged segment did not necessarily appear impaired. On the other hand, we observed that off-channel aquatic habitats were frequently important to productivity in reference floodplains, and the connection of these habitats in the dredged segment via previous restoration increased invertebrate productivity by 58%. However, using a simple bioenergetic model, we estimated that the invertebrate food-base was at least 4× larger than present demand for food by fish in dredged and reference segments. In the context of salmon recovery efforts, this observation questions whether additional food-base productivity provided by further habitat restoration would be warranted in the YFSR. Together, our findings highlight the importance of studies that assess the aquatic food-base, and emphasize the need for more robust ecosystem models that evaluate factors potentially limiting fish populations that are the target of restoration.
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Bellmore JR, Baxter CV, Martens K, Connolly PJ2013The floodplain food web mosaic: a study of its importance to salmon and steelhead with implications for their recovery.Ecological Applications 23(1)189-207
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Bellmore JR, Pess GR, Duda JJ, O'Conner JE, East AE, Foley MM, Wilcox AC, Major JJ, Shafroth PB, Morley SA, Magirl CS, Anderson CW, Evans JE, Torgersen CE, Craig LS
2019Conceptualizing Ecological Responses to Dam Removal: If You Remove It, What's to Come?BioScience 69(1)26-39
10.1093/biosci/biy152
One of the desired outcomes of dam decommissioning and removal is the recovery of aquatic and riparian ecosystems. To investigate this common objective, we synthesized information from empirical studies and ecological theory into conceptual models that depict key physical and biological links driving ecological responses to removing dams. We define models for three distinct spatial domains: upstream of the former reservoir, within the reservoir, and downstream of the removed dam. Emerging from these models are response trajectories that clarify potential pathways of ecological transitions in each domain. We illustrate that the responses are controlled by multiple causal pathways and feedback loops among physical and biological components of the ecosystem, creating recovery trajectories that are dynamic and nonlinear. In most cases, short-term effects are typically followed by longer-term responses that bring ecosystems to new and frequently predictable ecological condition, which may or may not be similar to what existed prior to impoundment
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Benigno G M, Sommer TR2008Just add water: sources of chironomid drift in a large river floodplain.Hydrobiologia600(1)297-305
10.1007/s10750-007-9239-2
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Besemer K, Luef B, Preiner S, Eichberger B, Agis M, Peduzzi P2009Sources and composition of organic matter for bacterial growth in a large European river floodplain system (Danube, Austria)Organic Geochemistry40(3)321-331
10.1016/j.orggeochem.2008.12.005
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Björnsson BT, Bradley TM2007Epilogue: Past successes, present misconceptions and future milestones in salmon smoltification research.Aquaculture 273(2-3)384-391
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Bond MH, Nodine TG, Beechie TJ, Zabel RW2019Estimating the benefits of widespread floodplain reconnection for Columbia River Chinook salmon.Canadian Journal of Fisheries and Aquatic Sciences 76(7)1212-1226
10.1139/cjfas-2018-0108]
Abstract: In the Pacific Northwest, widespread stream channel simplification has led to a loss of habitat area and diversity for rearing salmon. Subsequent efforts throughout the Columbia River basin (CRB) have attempted to restore habitats altered through land development to recover imperiled salmon populations. However, there is scant evidence for demographic change in salmon populations following restoration. We used a process-based approach to estimate the potential benefit of floodplain reconnection throughout the CRB to Chinook salmon (Oncorhynchus tshawytscha) parr. Using satellite imagery, we measured stream habitats at 2093 CRB stream reaches to construct random forest models of habitat based on geomorphic and regional characteristics. Connected floodplain width was the most important factor for determining side channel presence. We estimated a current CRB-wide decrease in side channel habitat area of 26% from historical conditions. Reconnection of historical floodplains currently used for agriculture could increase side channel habitat by 25% and spring Chinook salmon parr total rearing capacity by 9% over current estimates. Individual watersheds vary greatly in habitat factors that limit salmon recovery, and large-scale estimates of restoration potential like these are needed to make decisions about long-term restoration goals among imperiled populations.
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Bond N, Costelloe J, King A, Warfe D, Reich P, Balcombe S2014Ecological risks and opportunities from engineered artificial flooding as a means of achieving environmental flow objectives.Frontiers in Ecology and the Environment 12(7)386-39410.1890/130259
Abstract: Restoration of floodplain ecosystems through the reinstatement of floods is often hampered by insufficient water as a result of competing human demands. An emerging alternative approach relies on floodplain infrastructure – such as levees, weirs, regulators, and pumps – to control water levels within floodplains without requiring landscape-scale overbank floods. This technique, albeit water efficient and capable of achieving some ecological targets, does not mimic the hydraulics, hydrodynamics, and lateral connectivity of natural floods. Engineering approaches like this may risk detrimental ecological outcomes, including reductions in biotic connectivity, river–floodplain productivity, and water quality, and thus may fail to support the range of ecological processes required to sustain healthy river–floodplain systems. Here, we review the potential benefits, risks, and mitigation options associated with engineered artificial flooding. Given the growing challenge of equitable water allocation, further research on and monitoring of engineered floods as a tool to sustain floodplain ecosystems are urgently required.
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Bottom DL, Jones KK1990Species composition, distribution, and invertebrate prey of fish assemblages in the Columbia River estuary.Progress in Oceanography25(1-4)243-270
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Bottom DL, Jones KK, Cornwell TJ, Gray A, Simenstad CA2005Patterns of Chinook salmon migration and residency in the Salmon River estuary (Oregon)Estuarine, Coastal and Shelf Science6479-93
10.1016/j.ecss.2005.02.008
We examined variations in the juvenile life history of fall-spawning Chinook salmon, Oncorhynchus tshawytscha, for evidence of change in estuarine residency and migration patterns following the removal of dikes from 145 ha of former salt-marsh habitat in the Salmon River estuary (Oregon). Mark-recapture studies and abundance patterns in the estuary during 2000–2002 describe the following life-history types among Chinook salmon: (1) fry disperse throughout the estuary, and many move into restored tidal-marsh habitats in the early spring soon after emergence; (2) juveniles reside in freshwater for several months, enter the estuary in June or July, and remain for (a) a few weeks or (b) several months before entering the ocean; and (3) juveniles enter the ocean later in the fall after an extended period of rearing upriver and/or in the estuary. The absence of fry migrants in the estuary during spring and early summer in 1975–1977 — a period that precedes restoration of any of the diked marshes — and the extensive use of marsh habitats by fry and fingerlings April–July, 2000–2002 indicate that wetland restoration has increased estuarine rearing opportunities for juvenile Chinook salmon. Year-to-year patterns of estuarine rearing and abundance by juvenile salmon may be influenced by flood and drought conditions that affected adult spawner distribution and over-winter survival of salmon eggs. However, persistent changes in spawner distribution since 1975–1977, including the concentration of hatchery strays in the lower river, may account for the large proportion of fry that now disperse into the estuary soon after emergence in the spring. Although few of these earliest migrants survived to the river mouth, many fry and fingerlings from mid- and upper-basin spawning areas distributed throughout a greater portion of the estuary during the spring and summer and migrated to the ocean over a broader range of sizes and time periods than thirty years ago. The results suggest that wetland recovery has expanded life history variation in the Salmon River population by allowing greater expression of estuarine-resident behaviors.
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Bouvier L, Cottenie K, Doka S2009Aquatic connectivity and fish metacommunities in wetlands of the lower Great Lakes.Canadian Journal of Fisheries and Aquatic Sciences66(6)933-94810.1139/F09-050
Although many local and regional variables structure fish assemblage composition, few studies have assessed the effects of aquatic connectivity on fish assemblages in wetlands. Fish and habitat surveys were conducted in 12 wetlands across the lower Great Lakes basin in the spring and fall of 2003 and 2004. Spatial and temporal connectivity were classified into four connectivity classes to evaluate the interaction between aquatic connectivity and fish assemblage structure. Sequential, nested analysis of covariance was used to model the effect of habitat area and connectivity at long- and short-term time scales on aggregate descriptors of assemblage structure (i.e., species richness, piscivore richness, abundance, and diversity). Although no species–area relationship was detected, increases in connectivity were shown to positively affect species richness and piscivore richness. A variation decomposition method indicated that a combination of aquatic connectivity, followed by environmental and area variables, was most influential in structuring fish assemblages at short-term time scales. Connectivity thus influences both the local species pool present, as well as the abundance of these species within a wetland. Future fundamental and applied studies (e.g., climate change predictions, impact of humans on water budget, wetland management) on wetland fish assemblages should include connectivity as an important structuring process.
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Bowerman T, Roumasset A, Keefer ML, Sharpe CS, Caudill CC2018Prespawn Mortality of Female Chinook Salmon Increases with Water Temperature and Percent Hatchery Origin.Transactions of the American Fisheries Society 147(1)31-42
10.1002/tafs.10022
Abstract High rates of prespawn mortality, when adult salmon die after completing migration but prior to spawning, can lead to population declines and can impede recovery of threatened stocks. In this study, annual prespawn mortality of female Chinook Salmon Oncorhynchus tshawytscha ranged from 1% to 100% over 14 years in seven study reaches located throughout the upper Willamette River basin, Oregon. Prespawn mortality rates were positively correlated with the annual maximum 7-d average maximum stream temperature and the percentage of spawning fish of hatchery origin. Observed prespawn mortality rates varied considerably, but annual female prespawn rates were consistently >80% where maximum temperatures exceeded 20°C and the composition of spawning fish was >80% hatchery origin. In several spawning tributaries, prespawn mortality rates generally decreased at higher elevations. The proximate cause of prespawn death was not evaluated here, and observed patterns likely reflected additional factors that influence mortality either directly or indirectly, such as handling, dam passage, fishing pressure, instream habitat, energetic budget, fish density, and pathogen loads.
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Brett MT, Lubnow FS, Villar-Argaiz M, Müller-Solger A, Goldman CR1999Nutrient control of bacterioplankton and phytoplankton dynamicsAquatic Ecology33135-145
10.1023/A:1009998915078
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Brown JH, Gillooly JF, Allen AP, Savage VM, West GB2004Toward a Metabolic Theory of EcologyEcology85(7)1771-178910.1890/03-9000
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Budy P, Thiede GP, Bouwes N, Petrosky CE, Schaller H2002Evidence linking delayed mortality of Snake River salmon to their earlier hydrosystem experience.North American Journal of Fisheries Management 22(1): 35-51.
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Bunn S, Arthington A2002Basic Principles and Ecological Consequences of Altered Flow Regimes for Aquatic Deflation Basin Lakes.Environmental management 30: 492-507.
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Bunt CM, Castro-Santos T, Huro A2012Performance of fish passage structures at upstream barriers to migration.River Research and Applications 28(4): 457-478.10.1002/rra.1565
Abstract: Attraction and passage efficiency were reviewed and compared from 19 monitoring studies that produced data for evaluations of pool-and-weir, Denil, vertical-slot and nature-like fishways. Data from 26 species of anadromous and potamodromous fishes from six countries were separated by year and taxonomic family into a matrix with 101 records. Attraction performance was highly variable for the following fishway structures: pool-and-weir (attraction range = 29–100%, mean = 77%, median = 81%), vertical-slot (attraction range = 0–100%, mean = 63%, median = 80%), Denil (attraction range = 21–100%, mean = 61%, median = 57%) and nature-like (attraction range = 0–100%, mean = 48%, median = 50%). Mean passage efficiency was inversely related to mean attraction efficiency by fishway structure type, with the highest passage for nature-like fishways (range = 0–100%, mean = 70%, median = 86%), followed by Denil (range = 0–97%, mean = 51%, median = 38%), vertical-slot (range = 0–100%, mean = 45%, median = 43%) and pool-and-weir (range = 0–100%, mean = 40%, median = 34%). Principal components analysis and logistic regression modelling indicated that variation in fish attraction was driven by biological characteristics of the fish that were studied, whereas variation in fish passage was related to fishway type, slope and elevation change. This meta-analysis revealed that the species of fish monitored and structural design of the fishways have strong implications for both attraction and passage performance, and in most cases, existing data are not sufficient to support design recommendations. Many more fishway evaluations are needed over a range of species, fishway types and configurations to characterize, to optimize and to design new fishways. Furthermore, these studies must be performed in a consistent manner to identify the relative contributions of fish attraction and passage to overall fishway performance at each site.
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Castro-Santos T, Haro A2003Quantifying migratory delay: a new application of survival analysis methods.Canadian Journal of Fisheries and Aquatic Sciences 60(8): 986-996.
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Cocherell SA, Chun SN, Cocherell DE, Thompson LC, Klimley AP, Cech Jr JJ2012A lateral-displacement flume for fish behavior and stranding studies during simulated pulsed flows.Environmental Biology of Fishes 93(1)143-150
10.1007/s10641-011-9894-z
In regulated rivers, fluctuating water depths associated with pulsed discharges may strand small fish in side channels and pools. Quantitative assessments of stranded fish are difficult in field studies (e.g., due to unknown effects of avian and terrestrial vertebrate predators). To assess such lateral displacement and stranding on juvenile stream fishes, we designed, constructed, and tested (with three species) a 2 × 1-m, lateral-displacement flume. The flume featured a main channel that never drained and a raised, wide “floodplain” channel that alternately flooded, with a simulated pulse, and became dewatered. The floodplain contained four pools, with different shapes and draining capacities, in which fish could become stranded as the water level subsided. Fish-stranding rates (8%) in this relatively compact laboratory flume, after exposure to simulated pulsed stream flows, were comparable to those observed in past investigations using larger, artificial streams.
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Connor WP, Tiffan KF, Plumb JM, Moffit CM2013Evidence for density-dependent changes in growth, downstream movement, and size of Chinook Salmon subyearlings in a large-river landscape.Transactions of the American Fisheries Society 142(5)1453-1468
10.1080/00028487.2013.806953
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Conrad JL, Holmes E, Jeffres C, Takata L, Ikemiyagi N, Katz J, Sommer T2016Application of passive integrated transponder technology to juvenile salmon habitat use on an experimental agricultural floodplain.North American Journal of Fisheries Management36(1)30-39
10.1080/02755947.2015.1111276
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Cook K, Lennox R, Hinch S, Cooke Steven2015Fish out of water: how much air is too much?Fisheries 40(9)452-461
10.1080/03632415.2015.1074570
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Cook KV, Hinch SG, Drenner SM, Raby GD, Patterson DA, Cooke SJ2018Dermal injuries caused by purse seine capture result in lasting physiological disturbances in coho salmon.
Comparative Biochemistry and Physiology Part A: Molecular & Integrative Physiology
22775-83
10.1016/j.cbpa.2018.09.026
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Cook KV, Hinch SG, Watson MS, Patterson DA, Reid AJ, Cooke SJ2018Experimental capture and handling of chum salmon reveal thresholds in injury, impairment, and physiology: Best practices to improve bycatch survival in a purse seine fishery.Fisheries Research 20696-108
10.1016/j.fishres.2018.04.021
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Cordoleani F, Notch J, McHuron AS, Ammann AJ, Michel CJ2018Movement and Survival of Wild Chinook Salmon Smolts from Butte Creek During Their Out‐Migration to the Ocean: Comparison of a Dry Year versus a Wet Year.Transactions of the American Fisheries Society 147(1)171-184
10.1002/tafs.10008
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Corline NJ, Peek RA, Montgomery J, Katz JVE, Jeffres CA2021Understanding community assembly rules in managed floodplain food websEcosphere12(2)1-14
10.1002/ecs2.3330
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Corline NJ, Sommer T, Jeffres CA, Katz J2017Zooplankton Ecology and Trophic Resources for Rearing Fish on an Agricultural Floodplain in the Yolo Bypass California, USAWetlands Ecology and Management25(5)533–545
10.1007/s11273-017-9534-2
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Craddock DR, Blahm TH, Parente WD1976Occurrence and utilization of zooplankton by juvenile chinook salmon in the lower Columbia River.Transactions of the American Fisheries Society 105(1)72-76
10.1577/1548-8659(1976)105<72:OAUOZB>2.0.CO;2
Abstract: The stomachs of juvenile chinook salmon, Oncorhynchus tshawytscha, taken in the Prescott-Kalama area of the Columbia River during July-November 1968 and March-December 1969 were examined to obtain information on their contents. Zooplankton, especially Daphnia, were the major item in the diet of the young salmon from July through October, whereas insects were the most important constitutents of the diet during spring and fall. The zooplankton in the area was sampled from January 1968 to November 1969 and examined in relation to the relative abundance of juvenile chinook salmon and their stomach contents. Daphnia, Bosmina, and cyclopoid copepods were major zooplankters in the area, and their periods of highest abundance were associated with high water temperatures of summer. Samples taken during daylight hours indicated Bosmina were most numerous at the surface, Daphnia were most numerous below 5 m, and cyclopoid copepods were relatively uniform in their vertical distribution. The zooplankton populations were generally increasing during the season of juvenile chinook abundance (April-July). Juvenile chinook were selective in their feeding habits and consistently consumed Daphnia in a much higher percentage than it was found in the zooplankton samples.
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Cranston P, Dominguez MC2007Hydrobaenus saetheri Cranston, new species, an aestivating, winter-emerging chironomid (Diptera: Chironomidae) from California.
Contributions to the Systematics and Ecology of Aquatic Diptera. A Tribute to Ole A. Sæther.
73-79
The Caddis Press, Columbus
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Crump KL, Trudeau VL2009Mercury‐induced reproductive impairment in fishEnvironmental Toxicology and Chemistry28(5)895-90710.1897/08-151.1.
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David AT, Ellings C, Woo I, Simenstad CA, Takekawa JY, Turner KL, Smith AL, Takekawa JE
2014Foraging and growth potential of juvenile Chinook salmon after tidal restoration of a large river delta.Transactions of the American Fisheries Society 143(6)1515-1529
10.1080/00028487.2014.945663
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David AT, Simenstad CA, Cordell JR, Toft JD, Ellings CS, Gray A, Berge HB2016Wetland loss, juvenile salmon foraging performance, and density dependence in Pacific Northwest estuaries.Estuaries and Coasts 39(3)767-780
10.1007/s12237-015-0041-5
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del Rosario RB, Redler YJ, Newman K, Brandes PL, Sommer T, Reece K, Vincik R2013Migration Patterns of Juvenile Winter-run-sized Chinook Salmon (Oncorhynchus tshawytscha) Through the Sacramento–San Joaquin Delta.San Francisco Estuary and Watershed Science11(1)
10.15447/sfews.2013v11iss1art3
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Feyrer F, Sommer T, Harrell W2006Importance of flood dynamics versus intrinsic physical habitat in structuring fish communities: evidence from two adjacent engineered floodplains on the Sacramento River, California.North American Journal of Fisheries Management26(2)408-417
10.1577/M05-113.1
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Feyrer F, Sommer T, Harrell W2006Managing floodplain inundation for native fish: production dynamics of age-0 splittail (Pogonichthys macrolepidotus) in California’s Yolo BypassHydrobiologia573(1)213-226
10.1007/s10750-006-0273-2
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Feyrer F, Sommer TR, Zeug SC, O'Leary G, Harrell W2004Fish assemblages of perennial floodplain ponds of the Sacramento River, California (USA), with implications for the conservation of native fishes.Fisheries Management and Ecology11(5)335-344
10.1111/j.1365-2400.2004.00386.x
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Flitcroft RL, Arismendi MV, Santelmann MV2019A Review of Habitat Connectivity Research for Pacific Salmon in Marine, Estuary, and Freshwater Environments.
JAWRA Journal of the American Water Resources Association
55(2)430-441
10.1111/1752-1688.12708
Abstract Long-term conservation planning for diadromous fishes would benefit from a better understanding of both the role of connectivity among environments and habitat variability in the expression of life-history diversity. Most of the scientific knowledge on habitat fragmentation and connectivity has been developed in terrestrial systems in the discipline of landscape ecology. Research on habitat connectivity in aquatic systems (e.g., salmonid research that spans the spectrum of habitats from freshwater to the sea) is uncommon and largely focused on barriers to fish passage. Here, we present a review of the literature characterizing current research patterns on habitat connectivity within and among environments for Pacific salmon. We found this topic is still incipient: the literature is dominated by studies of freshwaters, with few articles focusing on habitat needs in estuary and marine systems. Pan-environment studies are rare, pointing to a gap in our understanding of complex habitat relationships that might be significant in the development of long-term conservation and restoration plans for Pacific salmon, particularly in light of the potential impact of climate change.
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Fong S, Louie S, Werner I, Davis J, Connon RE2016Contaminant Effects on California Bay–Delta Species and Human Health.San Francisco Estuary and Watershed Science 14(4)35
10.15447/sfews.2016v14iss4art5
Many contaminants in the California Bay–Delta (Bay–Delta) exceed regulatory standards, affect aquatic species, and potentially affect human health. Recent studies provide multiple lines of evidence that contaminants affect species of concern in the Bay–Delta (e.g., the decline of several important fish species referred to as the “Pelagic Organism Decline” or POD). Contaminants occur as dynamic complex mixtures and exert effects at multiple levels of biological organization. Multiple chemicals impair processes at cellular and physiological levels (measured as growth, development, and behavior abnormalities), and when viability and reproductive output are affected, populations are affected. As an important example, the population decline of the endangered Delta Smelt (Hypomesus transpacificus) is significantly associated with multiple stressors, including insecticide use. New analyses presented in this paper show significant correlations between pyrethroid use and declining abundance of POD fish species. Water sampled from the Bay–Delta causes multiple deleterious effects in fish, and Delta Smelt collected from the Bay–Delta exhibit contaminant effects. Fish prey items are also affected by contaminants; this may have an indirect effect on their populations. Co-occurrence with thermal changes or disease can exacerbate contaminant effects. Contaminants also pose threats to human health via consumption of fish and shellfish, drinking water, and contact recreation, in particular, mercury, cyanobacteria toxins, disinfection byproducts, pathogens, pesticides, and pharmaceuticals and personal care products. The role of contaminants in the decline of Bay–Delta species is difficult to accurately assess in a complex, dynamic system. However, tools and approaches are available to evaluate contaminant effects on Bay–Delta species, and separate the effects of multiple stressors. Integrated monitoring and focused mechanistic studies are instrumental for addressing management needs. Effect and risk assessments should be conducted for different species across multiple life stages, with emphasis on early life stages of highpriority Bay–Delta species.
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Frantzich J, Sommer T, Schreier B2018Physical and Biological Responses to Flow in a Tidal Freshwater Slough Complex.San Francisco Estuary and Watershed Science16(1)
10.15447/sfews.2018v16iss1/art3
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Fullerton AH, Burnette KM, Steel EA, Flitcroft RL, Pess GR, Feist BE, Torgersen CE, Miller DJ, Sanderson BL
2010Hydrological connectivity for riverine fish: measurement challenges and research opportunities.Freshwater Biology 55(11)2215-2237
10.1111/j.1365-2427.2010.02448.x
In this review,we first summarize how hydrologic connectivity has been studiedfor riverine fish capable ofmoving long distances, and then identify research opportunities that have clear conservation significance. Migratory species, such as anadromous salmonids, are good model organisms for understanding ecological connectivity in rivers because the spatial scale over which movements occur among freshwater habitats is large enough to be easily observed with available techniques; they are often economically or culturally valuable with habitats that can be easily fragmented by human activities; and they integrate landscape conditions from multiple surrounding catchment(s) with in-river conditions. Studies have focussed on three themes: (i) relatively stable connections (connections controlled by processes that act over broad spatio-temporal scales >1000 km2 and >100 years); (ii) dynamic connections (connections controlledbyprocesses actingoverfine tomoderatespatio-temporal scales 1–1000 km2 and <1–100 years); and (iii) anthropogenic influences on hydrologic connectivity, including actions that disrupt or enhance natural connections experienced by fish. 2. We outline eight challenges to understanding the role of connectivity in riverine fish ecology, organized under three foci: (i) addressing the constraints of river structure; (ii) embracing temporal complexity in hydrologic connectivity; and (iii) managing connectivity for riverine fishes. Challenges include the spatial structure of stream networks, the force and direction of flow, scale-dependence of connectivity, shifting boundaries, complexity of behaviour and life histories and quantifying anthropogenic influence on connectivity and aligning management goals. As we discuss each challenge, we summarize relevant approaches in the literature and provide additional suggestions for improving research and management of connectivity for riverine fishes. 3. Specifically, we suggest that rapid advances are possible in the following arenas: (i) incorporating network structure and river discharge into analyses; (ii) increasing explicit consideration of temporal complexity and fish behaviour in the scope of analyses; and (iii) parsing degrees of human and natural influences on connectivity and defining acceptable alterations. Multiscale analyses are most likely to identify dominant patterns of connections and disconnections, and the appropriate scale at which to focus conservation activities.
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Garnache C2015Fish, Farmers, and Floods: Coordinating Institutions to Optimize the Provision of Ecosystem Services.
Journal of the Association of Environmental and Resource Economists
2(3)367-39910.1086/682167
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Goertler P, Jones K, Cordell J, Schreier B, Sommer T2018Effects of Extreme Hydrologic Regimes on Juvenile Chinook Salmon Prey Resources and Diet Composition in a Large River FloodplainTransactions of the American Fisheries Society147(2)287-299
10.1002/tafs.10028
51
Goertler PAL, Sommer TR, Satterthwaite WH, Schreier BM2018Seasonal floodplain-tidal slough complex supports size variation for juvenile Chinook salmon (Oncorhynchus tshawytscha)Ecology of Freshwater Fish27(2)580-59310.1111/eff.12372
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Grantham TE, Figueroa R, Prat N2012Water management in mediterranean river basins: a comparison of management frameworks, physical impacts, and ecological responsesHydrobiologia
10.1007/s10750-012-1289-4
53
Grosholz E, Gallo E2006The influence of flood cycle and fish predation on invertebrate production on a restored California floodplain.Hydrobiologia 568(1)91-109
Although floodplains are known to be tightly controlled by the flood cycle, we know comparatively little about how flooding influences predators and their consumption of secondary production, particularly in highly seasonal floodplains typical of Mediterranean climates. In this study, we investigate how the seasonal dynamics of a central California floodplain influence the timing and magnitude of fish predation and the abundance and composition of invertebrates. For 3 years (2000–2002), we compared changes in abundances and size distributions of invertebrates through the flood season (January–June) with seasonal changes in the abundance of larval and juvenile fishes. Using diet analysis of fishes and manipulative feeding experiments with fishes in field enclosures, we link specific changes in invertebrate populations directly to feeding preferences of seasonally abundant fish. Early in the flood season prior to March, we found little influence of fish predation, consistent with the near absence of larval and juvenile fishes during this period. Coinciding with the midseason increase in the abundance of larval and juvenile fishes in April, we found significant declines in zooplankton abundance as well as declines in the size of zooplankton consistent with fish feeding preferences. Our results were consistent with results from feeding enclosure experiments that showed that fish rapidly depressed populations of larger cladocerans with much less effect on smaller cladocerans and calanoid copepods. At the end of the flood season, zooplankton abundances rapidly increased, consistent with a switch in the feeding of juvenile fish to aquatic insects and subsequent fish mortality. We also found that zooplankton biomass on the floodplain reached a maximum 2–3 weeks after disconnection with the river. We suggest that floodplain restoration in this region should consider management strategies that would ensure repeated flooding every 2–3 weeks during periods that would best match the peaks in abundance of native fishes.
54
Hall JE, Greene CM, Stefankiv O, Anderson JH, Timpane-Padgham B, Beechie TJ, Pess GR
2018Large river habitat complexity and productivity of Puget Sound Chinook salmon.PLOS ONE 13(11): e0205127
10.1371/journal.pone.0205127
55
Haro A, Odeh M, Noreika J, Castro-Santos T1998Effect of water acceleration on downstream migratory behavior and passage of Atlantic salmon smolts and juvenile American shad at surface bypasses.Transactions of the American Fisheries Society 127(1)118-127
10.1577/1548-8659(1998)127<0118:EOWAOD>2.0.CO;2
56
Hayes SA, MH Bond, CV Hanson, EV Freund2008Steelhead Growth in a Small Central California Watershed: Upstream and Estuarine Rearing PatternsTransaction of the American Fisheries Society137114-128
57
Hayes DS, Brändle JM, Seliger C, Zeiringer B, Ferreira T, Schmutz S2018Advancing towards functional environmental flows for temperate floodplain rivers.Science of The Total Environment 6331089-1104
10.1016/j.scitotenv.2018.03.221
Abstraction, diversion, and storage of flow alter rivers worldwide. In this context, minimum flow regulations are applied to mitigate adverse impacts and to protect affected river reaches from environmental deterioration. Mostly, however, only selected instream criteria are considered, neglecting the floodplain as an indispensable part of the fluvial ecosystem. Based on essential functions and processes of unimpaired temperate floodplain rivers, we identify fundamental principles to which we must adhere to determine truly ecologically-relevant environmental flows. Literature reveals that the natural flow regime and its seasonal components are primary drivers for functions and processes of abiotic and biotic elements such as morphology, water quality, floodplain, groundwater, riparian vegetation, fish, macroinvertebrates, and amphibians, thus preserving the integrity of floodplain river ecosystems. Based on the relationship between key flow regime elements and associated environmental components within as well as adjacent to the river, we formulate a process-oriented functional floodplain flow (ff-flow) approach which offers a holistic conceptual framework for environmental flow assessment in temperate floodplain river systems. The ff-flow approach underlines the importance of emulating the natural flow regime with its seasonal variability, flow magnitude, frequency, event duration, and rise and fall of the hydrograph. We conclude that the ecological principles presented in the ff-flow approach ensure the protection of floodplain rivers impacted by flow regulation by establishing ecologically relevant environmental flows and guiding flow restoration measures.
58
Henery RE, Sommer TR, Goldman CR2010Growth and methylmercury accumulation in juvenile Chinook salmon in the Sacramento River and its floodplain, the Yolo Bypass.Transactions of the American Fisheries Society139(2)550-563
10.1577/T08-112.1
59
Henning JA, Gresswell, RE, Fleming IA2006Juvenile Salmonid Use of Freshwater Emergent Wetlands in the Floodplain and Its Implications for Conservation ManagementNorth American Journal of Fisheries Management26367-376
10.1577/M05-057.1
60
Holmes EJ, Saffarinia P, Rypel AL, Bell-Tilcock MN, Katz JV, Jeffres CA2021Reconciling fish and farms: Methods for managing California rice fields as salmon habitatPlos One16(2): e0237686
10.1371/journal.pone.0237686
61
Howard JK, Klausmeyer KR, Fesenmyer KA, Furnish J, Gardali T, Grantham T, Katz JVE, Kupferberg S, McIntyre P, Moyle PB, Ode PR, Peek R, Quiñones RM, Rehn AC, Santos N, Schoenig S, Serpa L, Shedd JD, Slusark J, Viers JH, Wright A, Morrison SA
2015Patterns of Freshwater Species Richness, Endemism, and Vulnerability in CaliforniaPLoS ONE
10.1371/journal.pone.0130710
62
Jeffres CA, Holmes EJ, Sommer TR, Katz JVE2020Detrital food web contributes to aquatic ecosystem productivity and rapid salmon growth in a managed floodplainPLoS ONE15(9)1-20
10.1371/journal.pone.0216019
63
Jeffres CA, Opperman JJ, MoylePB2008Ephemeral floodplain habitats provide best growth conditions for juvenile Chinook salmon in a California riverEnvironmental Biology of Fishes83(4)449-458
10.1007/s10641-008-9367-1
64
Johnston ME, Steel AE, Espe M, Sommer T, Klimley AP, Sandstrom P, Smith D2018Survival of Juvenile Chinook Salmon in the Yolo Bypass and the Lower Sacramento River, California.San Francisco Estuary and Watershed Science16(2)1-17
10.15447/sfews.2018v16iss2art4
65
Johnston M, Frantzich J, Espe MB, Goertler P, Singer G, Sommer T, Klimley AP2020Contrasting the migratory behavior and stranding risk of White Sturgeon and Chinook Salmon in a modified floodplain of California.Environmental Biology of Fishes 103481-493
10.1007/s10641-020-00974-9
66
Junk WJ, Bayley PB2007The Scope of the Flood Pulse Concept Regarding Riverine Fish and Fisheries, Given Geographic and Man-Made Differences between SystemsAmerican Fisheries Society Symposium49587-603
67
Junk WJ, Bayley PB, Sparks RE1989The Flood Pulse Concept in River-Floodplain SystemsCanadian Journal of Fisheries and Aquatic Sciences106110-127
Proceedings of the International Large River Symposium Canadian Special Publication of Fisheries and Aquatic Sciences
68
Katz J, Moyle PB, Quiñones RM, Israel J, Purdy S2013Impending extinction of salmon, steelhead, and trout (Salmonidae) in California.Environmental Biology of Fishes96(10-11)1169-1186
10.1007/s10641-012-9974-8
69
Katz JVE, Jeffres C, Conrad JL, Sommer TR, Martinez J, Brumbaugh S, Corline N, Moyle PB
2017Floodplain farm fields provide novel rearing habitat for Chinook salmon.PLoS ONE12(6): e01774091-16
10.1371/journal.pone.0177409
70
Koehler ME, Fresh KL, Beauchamp DA, Cordell JR, Simenstad CA, Seiler DE2006Diet and bioenergetics of lake-rearing juvenile Chinook salmon in Lake Washington.Transactions of the American Fisheries Society 135(6)1580-1591
10.1577/T05-178.1
71
Lehman PW, Sommer T, Rivard L2008The influence of floodplain habitat on the quantity and quality of riverine phytoplankton carbon produced during the flood season in San Francisco EstuaryAquatic Ecology42(3)363-378
10.1007/s10452-007-9102-6
72
Levy DA, Northcote TG1982Juvenile Salmon Residency in a Marsh Area of the Fraser River EstuaryCanadian Journal of Fisheries and Aquatic Sciences39270-276
73
Limm MP, Marchetti MP2009Juvenile Chinook salmon (Oncorhynchus tshawytscha) growth in off-channel and main-channel habitats on the Sacramento River, CA using otolith increment widthsEnvironmental Biology of Fishes85(2)141-151
10.1007/s10641-009-9473-8
74
Macneale KH, Kiffney PM, Scholz NL2010Pesticides, aquatic food webs, and the conservation of Pacific salmon.Frontiers in Ecology and the Environment 8(9)475-48210.1890/090142
75
Magnusson A, Hilborn R2003Estuarine influence on survival rates of coho (Oncorhynchus kisutch) and chinook salmon (Oncorhynchus tshawytscha) released from hatcheries on the U.S. Pacific coast.Estuaries 26(4)1094-1103
While it has long been known that Pacific salmon use estuarine habitat, it has proven much harder to establish that the loss of estuarine habitat results in reduced survival. We used coded-wire tagging of hatchery fish to estimate the survival from release until maturity and related this survival to several indicators of estuarine condition. We found a significant relationship between the survival of chinook salmon (Oncorhynchus tshawytscha) and the percentage of the estuary that is in pristine condition, but no significant relationship for coho salmon (Oncorhynchus kisutch). This supports field observations that chinook salmon use estuarine habitat much more than coho salmon and confirms that the loss of estuarine habitat results in lower survival of chinook salmon.
76
Mahardja B, Hobbs JA, Ikemiyagi N, Benjamin A, Finger AJ2019Role of freshwater floodplain-tidal slough complex in the persistence of the endangered delta smelt.PLoS ONE14(1): e0208084
10.1371/journal.pone.0208084
Seasonal floodplain wetland is one of the most variable and diverse habitats found in coastal ecosystems, yet it is also one of the most highly altered by humans. The Yolo Bypass, the primary floodplain of the Sacramento River in California’s Central Valley, USA, has been shown to provide various benefits to native fishes when inundated. However, the Yolo Bypass exists as a tidal dead-end slough during dry periods and its value to native fishes has been less studied in this state. During the recent drought (2012–2016), we found higher abundance of the endangered Delta Smelt (Hypomesus transpacificus), than the previous 14 years of fish monitoring within the Yolo Bypass. Meanwhile, Delta Smelt abundance elsewhere in the estuary was at record lows during this time. To determine the value of the Yolo Bypass as a nursery habitat for Delta Smelt, we compared growth, hatch dates, and diets of juvenile Delta Smelt collected within the Yolo Bypass with fish collected among other putative nursery habitats in the San Francisco Estuary between 2010 and 2016. Our results indicated that when compared to other areas of the estuary, fish in the Yolo Bypass spawned earlier, and offspring experienced both higher quality feeding conditions and growth rates. The occurrence of healthy juvenile Delta Smelt in the Yolo Bypass suggested that the region may have acted as a refuge for the species during the drought years of 2012–2016. However, our results also demonstrated that no single region provided the best rearing habitat for juvenile Delta Smelt. It will likely require a mosaic of habitats that incorporates floodplain-tidal sloughs in order to promote the resilience of this declining estuarine fish species.
77
Maier GO, Simenstad CA2009The role of marsh-derived macrodetritus to the food webs of juvenile Chinook salmon in a large altered estuary.Estuaries and Coasts 32(5)984-998
78
Marine KR, Cech Jr JJ2004Effects of high water temperature on growth, smoltification, and predator avoidance in juvenile Sacramento RiverChinook Salmon.North American Journal of Fisheries Management 24(1)198-210
79
Marvin-DiPasquale M, Windham-Myers L, Agee JL, Kakouros E, Kieu LH, Fleck JA, Alpers CN, Stricker CA
2014Methylmercury production in sediment from agricultural and non-agricultural wetlands in the Yolo Bypass, California, USA.Science of the Total Environment484288-299
10.1016/j.scitotenv.2013.09.098
80
Matella MK, Jagt K2014Integrative method for quantifying floodplain habitat.Journal of Water Resources Planning and Management 140(8): 06014003
10.1061/(ASCE)WR.1943-5452.0000401
81
McInerney PJ, Stoffels RJ, SHackleton ME, Davey CD2017Flooding drives a macroinvertebrate biomass boom in ephemeral floodplain wetlands.Freshwater Science 36(4)726-73810.1086/694905
82
McKay SK, Schramski JR, Conyngham JN, Fischenich JC2013Assessing upstream fish passage connectivity with network analysis.Ecological Applications 23(6)1396-140910.1890/12-1564.1
83
Meador JP2013Do chemically contaminated river estuaries in Puget Sound (Washington, USA) affect the survival rate of hatchery-reared Chinook salmon?Canadian Journal of Fisheries and Aquatic Sciences 71(1)162-180
10.1139/cjfas-2013-0130
84
Michel CJ, Ammann AJ, Chapman ED, Sandstrom PT, Fish HE, Thomas MJ, Singer GP, Lindley ST, Klimley AP, MacFarlane RB
2013The effects of environmental factors on the migratory movement patterns of Sacramento River yearling late-fall run Chinook salmon (Oncorhynchus tshawytscha).Environmental Biology of Fishes96(2-3)257-271
10.1007/s10641-012-9990-8
85
Michel CJ, Ammann AJ, Lindley ST, Sandstrom PT, Chapman ED, Thomas MJ, Singer GP, Klimley AP, MacFarlane RB
2015Chinook salmon outmigration survival in wet and dry years in California’s Sacramento River.Canadian Journal of Fisheries and Aquatic Sciences 72(11)1749-1759
10.1139/cjfas-2014-0528
86
Michel CJ, Notch JJ, Cordoleani F, Ammann AJ, Danner EM2021Nonlinear survival of imperiled fish informs managed flows in a highly modified river.Ecosphere 12(5): e03498
10.1002/ecs2.3498
87
Moyle PB, Crain PK, Whitener K2007Patterns in the use of a restored California floodplain by native and alien fishes.San Francisco Estuary and Watershed Science5(3)
10.15447/sfews.2007v5iss5art
88
Muller-Solger AB, Jassby AD, Muller-Navarra DC2002Nutritional quality of food resources for zooplankton (Daphnia) in a tidal freshwater system (Sacramento–San Joaquin River Delta)Limnology and Oceanography47(5)1468-1476
10.4319/lo.2002.47.5.1468
89
Myrick C, Cech J2004Temperature effects on juvenile anadromous salmonids in California's Central Valley: What don't we know?Reviews in Fish Biology and Fisheries14113-123
The anadromous Chinook salmon (Oncorhynchus tshawytscha) (4 runs) and steelhead (rainbow trout, O. mykiss), are both native to California’s Sacramento-San Joaquin River (SSJR) system, whose watershed encompasses the central valley of California. The SSJR system holds the southernmost extant Chinook salmon populations in the Eastern Pacific Ocean, whereas coastal anadromous steelhead populations are found at more southerly latitudes. Populations of both species of anadromous salmonid have experienced dramatic declines during the past 100 years, at least partly from water impoundments and diversions on most central valley rivers and their tributaries. These changes restricted the longitudinal distribution of these salmonids, often forcing the superimposition of steelhead populations and Chinook salmon populations in the same reaches. This superimposition is problematic in part because the alterations to the river systems have not only changed the historic flow regimes, but have also changed the thermal regimes, resulting in thermally-coupled changes in fish development, growth, health, distribution, and survival. Given the highly regulated nature of the system, resource managers are constantly trying to strike a balance between maintaining or increasing the population size of anadromous fish runs and with other demands for the water, such as irrigation and water quality. To do so, in this review, we summarize the published information on the temperature tolerance and growth of the stream-associated life stages of these two valuable species, which are so central to the natural heritage of the State and its cultures. We show that many of these limits and growth-related effects are specific regarding life stage and that some may be specific to distinct strains or races of Chinook salmon and steelhead within the system. Because the number of published studies on the physiology of central valley salmonids was surprisingly low, we also use this review to highlight critical areas where further research is needed. Overall, this review should assist biologists and resource decision-makers with improved understanding for the protection and enhancement of these native fishes.
90
Nagrodski A, Raby GD, Hasler CT, Taylor MK, Cooke SJ2012Fish stranding in freshwater systems: sources, consequences, and mitigation.Journal of Environmental Management 93(1)133-141
10.1016/j.jenvman.2012.03.007
Fish can become stranded when water levels decrease, often rapidly, as a result of anthropogenic (e.g., canal drawdown, hydropeaking, vessel wakes) and natural (e.g., floods, drought, winter ice dynamics) events. We summarize existing research on stranding of fish in freshwater, discuss the sources, consequences, and mitigation options for stranding, and report current knowledge gaps. Our literature review revealed that approximately 65.5% of relevant peer-reviewed articles were found to focus on stranding associated with hydropower operations and irrigation projects. In fact, anthropogenic sources of fish stranding represented 81.8% of available literature compared to only 19.9% attributed to natural fish stranding events. While fish mortality as a result of stranding is well documented, our analysis revealed that little is known about the sublethal and long-term consequences of stranding on growth and population dynamics. Furthermore, the contribution of stranding to annual mortality rates is poorly understood as are the potential ecosystem-scale impacts. Mitigation strategies available to deal with stranding include fish salvage, ramping rate limitations, and physical habitat works (e.g., to contour substrate to minimize stranding). However, a greater knowledge of the factors that cause fish stranding would promote the development and refinement of mitigation strategies that are economically and ecologically sustainable.
91
Naughton GP, Caudill CC, Peery CA, Clabough TS, Jepson MA, Bjornn TC, Stuehrenberg LC
2007Experimental evaluation of fishway modifications on the passage behavior of adult Chinook salmon and steelhead at lower Granite Dam, Snake River, USA.River Research and Applications 2399-11110.1002/rra.957
92
Opperman JJ2012A conceptual model for floodplains in the Sacramento-San Joaquin Delta.San Francisco Estuary and Watershed Science10(3)
10.15447/sfews.2012v10iss3art4
93
Opperman JJ, GE Galloway, J Fargione, JF Mount, BD Richter, S Secchi2009Sustainable Floodplains Through Large-Scale Reconnection to RiversScience of the Total Environment3261487-1488
94
Perry RW, Pope AC, Romine JG, Brandes PL, Burau JR, Blake AR, Ammann AJ, Michel CJ
2018Flow-mediated effects on travel time, routing, and survival of juvenile Chinook salmon in a spatially complex, tidally forced river delta.Canadian Journal of Fisheries and Aquatic Sciences 75(11)1886-1901
10.1139/cjfas-2017-0310
95
Poff NL, Allan JD, Bain MB, Karr JR, Prestegaard KL, Richter BD, Sparks RE, Stromberg JC
1997The Natural Flow RegimeBioScience47(11)769-78410.2307/1313099
96
Poff NL, Zimmerman J2010Ecological responses to altered flow regimes: a literature review to inform the science and management of environmental flows.Freshwater Biology55194-205
97
Pope AC, Perry RW, Harvey BN, Hance DJ, Hansel HC2021Juvenile Chinook Salmon Survival, Travel Time, and Floodplain Use Relative to Riverine Channels in the Sacramento–San Joaquin River Delta.Transactions of the American Fisheries Society 150(1)38-55
10.1002/tafs.10271
98
Power ME, Sun A, Parker G, Dietrich WE, Wootton JT1995Hydraulic Food-Chain Models: An approach to the study of food-web dynamics in large rivers.BioScience 45(3)159-16710.2307/1312555
99
Power ME, Parker MS, Dietrich WE2008Seasonal reassembly of a river food web: Floods, droughts, and impacts of fish.Ecological Monographs 78(2)263-282
10.1890/06-0902.1
100
Riley AJ, Dodds WK2013Whole-stream metabolism: strategies for measuring and modeling diel trends of dissolved oxygenFreshwater Science32(1)56-6910.1899/12-058.1