Abstract:A set of empirical equations has been developed for use in determining the target strength or acoustic cross section of an individual fish at any insonified aspect as a function of fish size and insonifying frequency in the range 1?L/λ? 100, where L is fish length and λ is acoustic wavelength. The equations were developed by interpolating experimental data obtained by insonifying individual fish as they were rotated about one of their principal axes. It was found that acoustic cross section σ is proportional t… Show more
“…However, data are available in the form of target strength, which can be used to estimate the size of the fish detected (Love 1977). Using data supplied by the Lake Roosevelt Net Pen Program on the sizes of kokanee and rainbow trout released upstream of Grand Coulee Dam in Lake Roosevelt in 2001, we calculated that these fish would have target strengths within the range of -42 to -32 dB (Table 4.1).…”
“…However, data are available in the form of target strength, which can be used to estimate the size of the fish detected (Love 1977). Using data supplied by the Lake Roosevelt Net Pen Program on the sizes of kokanee and rainbow trout released upstream of Grand Coulee Dam in Lake Roosevelt in 2001, we calculated that these fish would have target strengths within the range of -42 to -32 dB (Table 4.1).…”
“…The average TS of the ensonified ping pong ball was -39.9 dB for Transducer 415; -39.5 dB for Transducer 418; and -39.8 dB for Transducer 428), and pre-and post-season averages were within 1 dB of each other. The final detection threshold for processing echoes was -56 dB referenced to 1 µPa at 1 m for on-axis fish, which is roughly equivalent to a 35-mm-long fish according to the any-aspect equation of Love (1977). Fine woody debris suspended in the water column, particularly during the pool refill period (April and May) had TSs between -60 and -56 dB, and influenced our choice of a detection threshold because we did not want to inflate counts with non-fish targets.…”
The 2008 Willamette Project Biological Opinion requires improvements to operations and structures to reduce impacts on Upper Willamette River Chinook salmon and steelhead, including evaluations of the feasibility of installing new juvenile collection and bypass facilities at three dams on the Willamette River in Oregon: Cougar, Detroit, and Lookout Point dams. Understanding the distribution of juvenile salmonids in the reservoirs will be critical for the development and operation of structures to pass fish safely and efficiently. This report describes results of mobile hydroacoustic surveys of fish distributions in Cougar Reservoir, a 518-ha impoundment behind Cougar Dam on the South Fork of the McKenzie River near Blue River, Oregon.Day and night mobile hydroacoustic surveys of Cougar Reservoir were conducted once a month from April through December 2011 to quantify the horizontal and vertical distributions of fish. An inflatable pontoon raft, outfitted with a frame holding four 6° split-beam transducers and a global positioning system, was pushed about 4 m ahead of the survey vessel to minimize fish avoidance of the bow wave and boat and maximize detectability. In November and December, transducers were deployed from the front of a pontoon boat with similar results. Two hydroacoustic systems were used to acquire echo trace data to estimate densities at night and during the day. A Precision Acoustic System transceiver controlled three forward-looking split-beams aimed 4°, 11°, and 18° below horizontal to sample fish in three respective depth strata (0−2, 2−4, and 4−6 m) 12.9−15.6 m ahead of the raft. A BioSonics DT-X system controlled one split-beam transducer aimed 10° forward from vertical to sample fish in 2-m strata from 6 to 62 m deep.The length of the smallest fish that could be detected with the -56 dB threshold was about 35 mm, but given the narrowness of acoustic beams for detecting fish <-53 dB, we only had reasonable detectability for fish >-53 dB (about 50 mm long). We estimated the areal density of fish (fish/hectare) and total numbers of fish in two length classes (50 to 200 mm, and > 200 mm) for the entire reservoir and five reservoir zones by month, and plotted densities on maps of the reservoir for every month surveyed. Surveys were scheduled to coincide with U.S. Geological Survey (USGS) Lampara seine sampling of pelagic areas and Oregon Department of Fish and Wildlife (ODFW) trap-net sampling of littoral areas to obtain concurrent species composition data.Hydroacoustic estimates of fish densities in pelagic areas were low, as were Lampara seine catches (39 fish in 353 hauls over 9 months; 31 [79.5%] of which were Chinook salmon). Given low catches in the Lampara net, species composition information for pelagic areas was not as robust as that derived from trap netting in littoral areas. The ODFW trap nets caught 1072 fish in 35 trap-net nights over 8 months, and the species composition was 69.2% dace, 24.3% Chinook salmon smolts, 3.6% rainbow trout, and 2.9% cutthroat trout. The smallest dace ...
“…Fork lengths of trawl caught fish were converted to the same acoustic scale using Love's (1977) empirical relation and compared to acoustic size distributions in order to verify the most appropriate size cut-off to separate age 0+ from age 1-3+ kokanee. Since it was not possible to distinguish between age 1, 2, and 3 fish using acoustic data, the proportions of these age groups could only be based on trawl catches.…”
Section: Hydro Acoustics and Trawl Samplingmentioning
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