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Invasive Cyprinid fishes auditory evoked potentials and behavioral thresholds in a lab
This data set contains auditory evoked potentials for four species of invasive carp; silver carp, black carp, grass carp, bighead carp, as well as goldfish (100-150 millimeters in total length) and behavioral thresholds on goldfish in a tank (dimensions 240 centimeters X 100 centimeters; depth of 25 centimeters) at the Columbia Environmental Research Center, Columbia, MO USA. Ambient sound and experimental tones were recorded using a hydrophone (STD 300; Ocean Instruments, Auckland, NZ) located where fish were placed in the experimental setup. Auditory evoked potentials were collected using a signal processor and bioamplifier (RZ6 and 4Z, Tucker-Davis Technology, Florida, USA) and recorded using the BioSigRZ software (Tucker-Davis Technology, Florida, USA). The stimulus was 100 ms tone bursts at 300, 500, 800, 1000, and 1500 Hz with a cosine-squared gate and 10 ms rise and fall time. Behavioral thresholds were collected for goldfish. To determine threshold, tones were presented to a conditioned fish beginning at approximately 30 decibels (dB) re 1 micropascal above the expected threshold. Each time the goldfish showed detection (suppressing respiration), the tone was lowered by 10 dB. When the fish did not respond, the tone level was increased by 5 dB for a final presentation. Water temperature of the tank was collected with a data logger (HOBO data logger, OnSet, Massachusetts, USA).
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Bioacoustic manipulation of invasive Bigheaded carp: Common Carp phonotaxis data
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This dataset includes the behavioral responses to a broadband sound for common carp in an outdoor concrete pond. Broadband sound (0.06 to 10 kHz) has shown potential as an acoustic deterrent for bigheaded carps, but the response of common carp to broadband sound has not been evaluated. Since common carp are ostariophysians, possessing Weberian ossicles similar to bigheaded carps, it is possible that sound can be used as an acoustical deterrent for all three species.
Acoustic deterrence of bighead carp (Hypophthalmichthys nobilis) to a broadband sound stimulus: Data
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Recent studies have shown the potential of acoustic deterrents against invasive silver carp (Hypophthalmichthys molitrix). This study examined the phonotaxic response of the bighead carp (H. nobilis) to pure tones (500– 2000 Hz) and playbacks of broadband sound from an underwater recording of a 100 hp outboard motor (0.06–10 kHz) in an outdoor concrete pond (10 × 5 × 1.2 m) at the U.S. Geological Survey Upper Midwest Envi- ronmental Science Center in La Crosse, WI. The number of consecutive times the fish reacted to sound from alter- nating locations at each end of the pond was assessed. Bighead carp were relatively indifferent to the pure tones with median consecutive responses ranging from 0 to 2 reactions away from the sound source. However, fish consistently exhibited significantly (P b 0.001) greater negative phonotaxis to the broadband sound (outboard motor recording) with an overall median response of 20 consecutive reactions during the 10 min trials. In over 50% of broadband sound tests, carp were still reacting to the stimulus at the end of the trial, implying that fish were not habituating to the sound. This study suggests that broadband sound may be an effective deterrent to bighead carp and provides a basis for conducting studies with wild fish.
Silver Carp (Hypophthalmichthys molitrix) Locations in Earthen Ponds Exposed to Three Acoustic Signals, June though August, 2018
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This data set includes acoustic telemetry positions for silver carp ranging in total length from 251 to 359 mm (mean = 294 mm) and weight 131 – 427 g (mean = 231 g) tagged with 795-LD transmitters in four earthen ponds at the Columbia Environmental Research Center, Columbia, MO, USA. Positions were monitored using a 16-hydrophone array in each pond before and during a series of trials where fish were exposed to one of three acoustic signals for a length of 30 minutes. Trials occurred from June 11 to August 7, 2018. The telemetry positions were filtered to include 30 minutes before silver carp were exposed to one of three acoustic signals, and 30 minutes during signal playback. This was repeated for five trials with a new lot of fish for each trial, but Trial 4 data were excluded from the dataset due to fish health concerns.
Impacts of bird predation on the detection of acoustic telemetry tags in fish (ver. 2.0, September 2025)
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This data release contains the methodology and results of three field experiments performed in 2024 and 2025 to better understand how predation impacts detection efficiency of acoustic tags. The first experiment was a static approach focusing on how different tag types, tag power, depth, distance to passive receivers, and predation would affect detection efficiency and utilized both tagged yellow perch (Perca flavescens) as well as double-crested cormorants (Phalacrocorax auritus) that had "consumed" a tagged yellow perch and indicated that proximity to the surface as well as range from passive receivers were significant factors. The second experiment was designed to simulate cormorant diving activity and determine how that behavior and tags with different nominal signal delays affects detection efficiency. The third experiment was a static approach similar to the first experiment and was designed to fill in data gaps of the first experiment utilizing both tagged yellow perch and double-crested cormorants.
Acoustic detection and biological data for Lake Trout, Salvelinus namaycush, in Lake Ontario
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Acoustic Telemetry is gaining popularity for use in fisheries research as a method to estimate survival and observe behaviors of native fish species. Methodology for capture and tagging of fish is typically context and species-specific, requiring a case by case basis for best practices to maximize survival of tagged individuals. This dataset includes acoustic detection data from 320 adult Lake Trout, Salvelinus namaycush, captured and acoustic-tagged in Lake Ontario during April-June of 2023. Biological data (total length), capture data (surface water temperature, capture depth), capture location, and capture gear (angling, bottom trawls, gillnets) are also included in the dataset as covariates that can be analyzed to determine if any of these factors affect post-release survival of tagged Lake Trout. Acoustic detection data is available from April 2023 to November 2024. Survival of acoustic-tagged Lake Trout was estimated through acoustic telemetry detections indicating the status of the Lake Trout (alive vs. dead).
Voltage Gradient Behavioral Response Thresholds of Bighead Carp (Hypophthalmichthys nobilis), Black Carp (Mylopharyngodon piceus), Grass Carp (Ctenopharyngodon idella), and Silver Carp (Hypophthalmichthys molitrix), to a Suite of Direct and Alternating Current Electrofishing Waveforms
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Voltage gradient behavioral response thresholds of Bighead Carp (Hypophthalmichthys nobilis), Black Carp (Mylopharyngodon piceus), Grass Carp (Ctenopharyngodon idella), and Silver Carp (Hypophthalmichthys molitrix), to a suite of direct and alternating current electrofishing waveforms.
Dolphin Sound Production Recorded at SanctSound Site CI04 04
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This record represents dolphin whistle and moan sound production detected from raw passive acoustic data. All acoustic data were processed through Pamguard's Whistle and Moan Detector (v. 2.01.03, Gillespie et al. 2013). A frequency range of 4-20 kHz was selected to encompass the frequency range of common dolphins, Pacific white-sided dolphins, and bottlenose dolphins. Presence in an hour was defined as 1+ detected whistles (or part of whistle) so long as it was not a solitary tone. Each detection was not annotated but rather the hour as a whole was marked with a 0 or 1. Only full hours of data were analyzed. These data were recorded at SanctSound Site CI04_04 between January 31, 2020 and May 22, 2020.
Dolphin Sound Production Recorded at SanctSound Site CI01 04
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This record represents dolphin whistle and moan sound production detected from raw passive acoustic data. All acoustic data were processed through Pamguard's Whistle and Moan Detector (v. 2.01.03, Gillespie et al. 2013). A frequency range of 4-20 kHz was selected to encompass the frequency range of common dolphins, Pacific white-sided dolphins, and bottlenose dolphins. Presence in an hour was defined as 1+ detected whistles (or part of whistle) so long as it was not a solitary tone. Each detection was not annotated but rather the hour as a whole was marked with a 0 or 1. Only full hours of data were analyzed. These data were recorded at SanctSound Site CI01_04 between January 24, 2020 and June 04, 2020.
Dolphin Sound Production Recorded at SanctSound Site CI02 04
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This record represents dolphin whistle and moan sound production detected from raw passive acoustic data. All acoustic data were processed through Pamguard's Whistle and Moan Detector (v. 2.01.03, Gillespie et al. 2013). A frequency range of 4-20 kHz was selected to encompass the frequency range of common dolphins, Pacific white-sided dolphins, and bottlenose dolphins. Presence in an hour was defined as 1+ detected whistles (or part of whistle) so long as it was not a solitary tone. Each detection was not annotated but rather the hour as a whole was marked with a 0 or 1. Only full hours of data were analyzed. These data were recorded at SanctSound Site CI02_04 between February 05, 2020 and June 04, 2020.
Dolphin Sound Production Recorded at SanctSound Site CI04 03
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This record represents dolphin whistle and moan sound production detected from raw passive acoustic data. All acoustic data were processed through Pamguard's Whistle and Moan Detector (v. 2.01.03, Gillespie et al. 2013). A frequency range of 4-20 kHz was selected to encompass the frequency range of common dolphins, Pacific white-sided dolphins, and bottlenose dolphins. Presence in an hour was defined as 1+ detected whistles (or part of whistle) so long as it was not a solitary tone. Each detection was not annotated but rather the hour as a whole was marked with a 0 or 1. Only full hours of data were analyzed. These data were recorded at SanctSound Site CI04_03 between August 13, 2019 and November 21, 2019.