4+ year old cisco (Coregonus artedi) pre-spawn and spawning/near-spawning behavioral data were collected and compiled at the Tunison Laboratory of Aquatic Science in Cortland, NY USA, between August-October 2021 and November-December 2021. Data are comprised of fish reactions in choice flume video data (attractance/avoidance). Cisco were exposed/not exposed to an imprinting chemical (amino acids: alanine, histidine, morpholine, proline, and serine) through early life stages, and later tested based on their treatment to see how individuals reacted to the presence of exposure chemicals during subsequent life stages. These data show how the adult stage cisco of this study ((non exposed (control) and treatment (amino acid exposed)) react to timed exposure of morpholine dilution at the 4+ year life stages.

Subadult and smolt behavioral data were compiled by Ali Mokdad from Trevor Pitcher's lab at the University of Windsor, Ontario, Canada. Data are comprised of fish reactions in choice flume video data (attractance/avoidance) collected by Jeremy Kraus at Tunison Lab of Aquatic Science, August 2021 and February 2020 respectively. Atlantic salmon were exposed/not exposed to imprinting chemical (morpholine) through early life stages and later tested based on their treatment to see how individuals react to the presence of exposure chemicals during subsequent life stages. These data show how the adult stage Atlantic salmon of this study ((non exposed (control) and treatment (morpholine exposed)) react to timed exposure of morpholine dilution at the 3+ and 1+ year life stages. Imprinted Atlantic salmon morphometric data were collected Feb 20, 2020 at Tunison Lab. These data represent growth (length (mm) and weight (g)) of experimental Atlantic salmon, just after imprinting flume tests were completed for their life stage/age.

Subadult and smolt behavioral data were compiled by Ali Mokdad from Trevor Pitcher's lab at the University of Windsor, Ontario, Canada. Data are comprised of fish reactions in choice flume video data (attractance/avoidance) collected by Jeremy Kraus at Tunison Lab of Aquatic Science, August 2021 and February 2020 respectively. Atlantic salmon were exposed/not exposed to imprinting chemical (morpholine) through early life stages and later tested based on their treatment to see how individuals react to the presence of exposure chemicals during subsequent life stages. These data show how the adult stage Atlantic salmon of this study ((non exposed (control) and treatment (morpholine exposed)) react to timed exposure of morpholine dilution at the 3+ and 1+ year life stages. Imprinted Atlantic salmon morphometric data were collected Feb 20, 2020 at Tunison Lab. These data represent growth (length (mm) and weight (g)) of experimental Atlantic salmon, just after imprinting flume tests were completed for their life stage/age.

The dataset is composed of two data tables containing information from electrofishing surveys conducted in the Catskill and Adirondack regions. The first data table contains fish collection information and the second data table contains information on the sampled reaches. First posted September 25, 2018, ver. 1.0 Revised July 2019, ver. 2.0 Revised November 2020, ver. 3.0 Revised March 2022, ver. 4.0 Revised September 2022, ver. 5.0 Revised February 2023, ver. 6.0 Revised December 2023, ver. 7.0 Version 7.0: This version of the dataset has the same structure (two data tables containing the same column headings) as Versions 6.0, 5.0, 4.0, 3.0, 2.0, and 1.0 but includes the addition of data from electrofishing surveys conducted in 2023 at 8 sites in the Catskill Mountain region and 2 sites in the Adirondack Mountain region. All data in Version 6.0 have been retained in Version 7.0 and are unchanged. Version 6.0: This version of the dataset has the same structure (two data tables containing the same column headings) as Versions 5.0, 4.0, 3.0, 2.0, and 1.0 but includes the addition of data from electrofishing surveys conducted in 2022 at 8 sites in the Catskill Mountain region and 1 site in the Adirondack Mountain region. All data in Version 5.0 have been retained in Version 6.0 and are unchanged. Version 5.0: This version of the dataset has the same structure (two data tables containing the same column headings) as Versions 4.0, 3.0, 2.0, and 1.0 but includes the addition of data from electrofishing surveys conducted in 2021 at 11 sites in the Catskill Mountain region. All data in Version 4.0 have been retained in Version 5.0 and are unchanged with one exception: the USGS Station Number associated with the site ID ‘ElkBRest’ has been changed from 0136219205 to 420312074273701. Version 5.0 data are available upon request. Version 4.0: This version of the dataset has the same structure (two data tables containing the same column headings) as Versions 3.0, 2.0, and 1.0 but includes the addition of data from electrofishing surveys conducted in 2020 at 40 sites in the Adirondack Mountain region and 11 sites in the Catskill Mountain region. All data in Version 3.0 have been retained in Version 4.0 and are unchanged with two exceptions: 1) the species identification of 4 fish captured in Browns Creek on 7/29/14 have been changed from Northern Pearl Dace (Margariscus nachtriebi) to Allegheny Pearl Dace (Margariscus margarita) as a result of subsequent expert assessment of archived specimens, and 2) the USGS Station Number associated with the site ID ‘Windfall’ has been changed from 434813074505701 to 04253660. Version 4.0 data are available upon request. Version 3.0: This version of the dataset has the same structure (two data tables containing the same column headings) as Versions 2.0 and 1.0 but includes the addition of data from electrofishing surveys conducted in the upper Neversink River and upper Rondout Creek and their tributaries in the Catskill region during the period 1988-2019. All data in Version 2.0 have been retained in Version 3.0 and are unchanged with two exceptions: 1) the “Year” column in both data tables has been replaced with a “Date” column providing the exact date a survey was conducted, and 2) the USGS Station Number associated with the site ID ‘Slide’ on the West Branch Neversink River has been changed from 420034074253201 to 0143402120. Version 3.0 data are available upon request. Version 2.0: This version of the dataset has the same structure (two data tables containing the same column headings) as Version 1.0 but includes the addition of data from electrofishing surveys conducted on the Esopus Creek and its tributaries in the Catskill region during the period 2009-2018. All data in Version 1.0 have been retained and are unchanged with the exception of a correction to the USGS Station Number associated with Wheeler Creek. Version 2.0 data are available upon request. Version 1.0: This version of the dataset

In the spring of 2003, California Department of Fish and Game (CDFG) personnel began quarterly sampling of Salton Sea fish at fourteen stations around the sea, as the basis of a long term monitoring program. To allow comparison of current and future monitoring efforts by CDFG to past results, the protocol was adapted from those previously used by researchers at the Salton Sea. Each quarter, if conditions allow, this protocol will produce about 816 net-hours of sampling. To date data collection was started in the spring of 2003, continuing quarterly. Data collection is ongoing as of 2008. Two seasons were missed due to unavailability of launch sites: Fall 2007 and Winter 2007. *Note: This dataset should be viewed with the Quarterly Water Quality Surveys - Salton Sea [ds429] dataset. Methods: The 11 sampling sites comprise three broad habitat types: pelagic (3 sites), near-shore (8 sites), and estuarine (3 sites). The pelagic sites are in the approximate middles of the north basin, south basin and inter-basin areas of the Sea. The near-shore sites are spaced widely apart, four each, near the west and east shores, to capture as much breadth of habitat as possible. The estuarine sites are in the body of the Sea, close enough to the mouths of the New, Alamo, and Whitewater Rivers, to be under the influence of their outflows. Sampling takes place during each of the putative seasons, as follows: spring- April and May; summer- July and August; fall- October and November; winter- January and February. We attempt to compress the total sampling period into as few days as possible, to the extent that the weather, equipment maintenance, and personnel scheduling constraints allow. Nets are typically set at one or two sites in the morning, and hauled in after approximately 24 hours. The exact number of hours set is recorded for each net, to the nearest quarter-hour. Fish are sampled by deploying multi-panel monofilament gill nets with 6 X 30 foot panels of 0.5, 1, 2, 3, and 4 inch mesh. Two nets are set at all sites at the waters surface. The nets are set far enough apart to allow room for maneuvering a boat during setting and retrieval, usually 100-200 meters. The nets at near-shore and estuarine sites are set in 2.5 to 4.5 meters of water, typically 200-300 meters from the shore. Two additional nets are set at the bottom of water column at the three pelagic sites. The conditions fish experience at the bottom in deep water is different enough from the surface water, in dissolved oxygen, light, food availability and temperature, that this can be considered a discrete habitat, and thus we sample it as though it were a separate site. At the time of each set and retrieval, water depth, water temperature, conductivity, salinity, and dissolved oxygen are measured and recorded. When nets are pulled in the following day, all fish are removed and immediately stored on ice. Data are collected from these fish as soon as possible, almost always the same day they are hauled in. All fish are identified to species level and counted. For the four sport fish in the Salton Sea, (tilapia, Gulf croaker, orangemouth corvina and sargo) weights, lengths (fork length), sex, physical condition, and reproductive status are recorded. Fish above five pounds are weighed to the nearest ounce. Fish below five pounds are weighed to the nearest half ounce. Lengths of fish under 50 centimeters are recorded to the nearest millimeter. Lengths of fish over 50 centimeters are recorded to the nearest centimeter. The sex of adult fish is determined by dissection. A sample of at least ten fish of each species is also dissected to determine physical condition and breeding status. Changes to Protocol after Year One: For previous researchers, deep water habitats provided some low level of productivity for the fisheries, and were important habitat components to sample. During the first year of sampling, however, the three deep water sites (north basin, south basin and inter-basin)

The dataset is composed of two data tables containing information from electrofishing surveys conducted in the Catskill and Adirondack regions. The first data table contains fish collection information and the second data table contains information on the sampled reaches. First posted September 25, 2018, ver. 1.0 Revised July 2019, ver. 2.0 Revised November 2020, ver. 3.0 Revised March 2022, ver. 4.0 Revised September 2022, ver. 5.0 Revised February 2023, ver. 6.0 Revised December 2023, ver. 7.0 Version 7.0: This version of the dataset has the same structure (two data tables containing the same column headings) as Versions 6.0, 5.0, 4.0, 3.0, 2.0, and 1.0 but includes the addition of data from electrofishing surveys conducted in 2023 at 8 sites in the Catskill Mountain region and 2 sites in the Adirondack Mountain region. All data in Version 6.0 have been retained in Version 7.0 and are unchanged. Version 6.0: This version of the dataset has the same structure (two data tables containing the same column headings) as Versions 5.0, 4.0, 3.0, 2.0, and 1.0 but includes the addition of data from electrofishing surveys conducted in 2022 at 8 sites in the Catskill Mountain region and 1 site in the Adirondack Mountain region. All data in Version 5.0 have been retained in Version 6.0 and are unchanged. Version 5.0: This version of the dataset has the same structure (two data tables containing the same column headings) as Versions 4.0, 3.0, 2.0, and 1.0 but includes the addition of data from electrofishing surveys conducted in 2021 at 11 sites in the Catskill Mountain region. All data in Version 4.0 have been retained in Version 5.0 and are unchanged with one exception: the USGS Station Number associated with the site ID ‘ElkBRest’ has been changed from 0136219205 to 420312074273701. Version 5.0 data are available upon request. Version 4.0: This version of the dataset has the same structure (two data tables containing the same column headings) as Versions 3.0, 2.0, and 1.0 but includes the addition of data from electrofishing surveys conducted in 2020 at 40 sites in the Adirondack Mountain region and 11 sites in the Catskill Mountain region. All data in Version 3.0 have been retained in Version 4.0 and are unchanged with two exceptions: 1) the species identification of 4 fish captured in Browns Creek on 7/29/14 have been changed from Northern Pearl Dace (Margariscus nachtriebi) to Allegheny Pearl Dace (Margariscus margarita) as a result of subsequent expert assessment of archived specimens, and 2) the USGS Station Number associated with the site ID ‘Windfall’ has been changed from 434813074505701 to 04253660. Version 4.0 data are available upon request. Version 3.0: This version of the dataset has the same structure (two data tables containing the same column headings) as Versions 2.0 and 1.0 but includes the addition of data from electrofishing surveys conducted in the upper Neversink River and upper Rondout Creek and their tributaries in the Catskill region during the period 1988-2019. All data in Version 2.0 have been retained in Version 3.0 and are unchanged with two exceptions: 1) the “Year” column in both data tables has been replaced with a “Date” column providing the exact date a survey was conducted, and 2) the USGS Station Number associated with the site ID ‘Slide’ on the West Branch Neversink River has been changed from 420034074253201 to 0143402120. Version 3.0 data are available upon request. Version 2.0: This version of the dataset has the same structure (two data tables containing the same column headings) as Version 1.0 but includes the addition of data from electrofishing surveys conducted on the Esopus Creek and its tributaries in the Catskill region during the period 2009-2018. All data in Version 1.0 have been retained and are unchanged with the exception of a correction to the USGS Station Number associated with Wheeler Creek. Version 2.0 data are available upon request. Version 1.0: This version of the dataset

Research support for various organizations in NOAA (Northwest Regional Office (NWR), HQ Office of Protected Resources, National Ocean Service (NOS) Coastal Services Center) for copper related to the harmful impacts of urban stormwater runoff, pesticide use, antifoulant use, and mining (e.g., proposed hardrock mining in Alaska). This has been a core focus of Ecotoxicology research for years, and may redirect to address key and high-profile data gaps specific to salmon habitat threats in Alaska. Behavioral observations and video of salmonids responding to odors and predators.

In the spring of 2003, California Department of Fish and Game (CDFG) personnel began quarterly sampling of Salton Sea fish at fourteen stations around the sea, as the basis of a long term monitoring program. To allow comparison of current and future monitoring efforts by CDFG to past results, the protocol was adapted from those previously used by researchers at the Salton Sea. Each quarter, if conditions allow, this protocol will produce about 816 net-hours of sampling. To date data collection was started in the spring of 2003, continuing quarterly. Data collection is ongoing as of 2008. Two seasons were missed due to unavailability of launch sites: Fall 2007 and Winter 2007. *Note: This dataset should be viewed with the Quarterly Water Quality Surveys - Salton Sea [ds429] dataset. Methods: The 11 sampling sites comprise three broad habitat types: pelagic (3 sites), near-shore (8 sites), and estuarine (3 sites). The pelagic sites are in the approximate middles of the north basin, south basin and inter-basin areas of the Sea. The near-shore sites are spaced widely apart, four each, near the west and east shores, to capture as much breadth of habitat as possible. The estuarine sites are in the body of the Sea, close enough to the mouths of the New, Alamo, and Whitewater Rivers, to be under the influence of their outflows. Sampling takes place during each of the putative seasons, as follows: spring- April and May; summer- July and August; fall- October and November; winter- January and February. We attempt to compress the total sampling period into as few days as possible, to the extent that the weather, equipment maintenance, and personnel scheduling constraints allow. Nets are typically set at one or two sites in the morning, and hauled in after approximately 24 hours. The exact number of hours set is recorded for each net, to the nearest quarter-hour. Fish are sampled by deploying multi-panel monofilament gill nets with 6 X 30 foot panels of 0.5, 1, 2, 3, and 4 inch mesh. Two nets are set at all sites at the waters surface. The nets are set far enough apart to allow room for maneuvering a boat during setting and retrieval, usually 100-200 meters. The nets at near-shore and estuarine sites are set in 2.5 to 4.5 meters of water, typically 200-300 meters from the shore. Two additional nets are set at the bottom of water column at the three pelagic sites. The conditions fish experience at the bottom in deep water is different enough from the surface water, in dissolved oxygen, light, food availability and temperature, that this can be considered a discrete habitat, and thus we sample it as though it were a separate site. At the time of each set and retrieval, water depth, water temperature, conductivity, salinity, and dissolved oxygen are measured and recorded. When nets are pulled in the following day, all fish are removed and immediately stored on ice. Data are collected from these fish as soon as possible, almost always the same day they are hauled in. All fish are identified to species level and counted. For the four sport fish in the Salton Sea, (tilapia, Gulf croaker, orangemouth corvina and sargo) weights, lengths (fork length), sex, physical condition, and reproductive status are recorded. Fish above five pounds are weighed to the nearest ounce. Fish below five pounds are weighed to the nearest half ounce. Lengths of fish under 50 centimeters are recorded to the nearest millimeter. Lengths of fish over 50 centimeters are recorded to the nearest centimeter. The sex of adult fish is determined by dissection. A sample of at least ten fish of each species is also dissected to determine physical condition and breeding status. Changes to Protocol after Year One: For previous researchers, deep water habitats provided some low level of productivity for the fisheries, and were important habitat components to sample. During the first year of sampling, however, the three deep water sites (north basin, south basin and inter-basin)

The Ecology Section at the USGS, EESC, S. O. Conte Research Laboratory studied brook trout in a small coastal stream (Stanley Brook) from 2006 - 2013. The goal was to understand the mechanisms and consequences of anadromoy, as well as strength and direction of drivers on fish growth, movement, reproduction and survival in the wild. We hope to provide a comprehensive understanding of fish population dynamics for this stream and life history form and ultimately individual fitness (natural selection and evolution) in the study area.

General Fish Surveys compare trends among the fishery species in Lake Skinner utilizing data that calculates catch per unit of effort (CPUE), relative abundance of each species and several population indices including length distribution, weight-length relationships, relative weight (Wr), and proportional size distributions (PSD) This data and metadata were submitted by California Department of Fish and Wildlife (CDFW) Staff though the Data Management Plan (DMP) framework with the id: DMP000449. For more information, please visit https://wildlife.ca.gov/Data/Sci-Data.