ICES Journal of Marine Science, 60: 658–661. 2003 doi:10.1016/S1054–3139(03)00052-3 Acoustic observation and assessment of fish in high-relief habitats K. Cooke, R. Kieser, and R. D. Stanley Cooke, K., Kieser, R., and Stanley, R. D. 2003. Acoustic observation and assessment of fish in high-relief habitats. – ICES Journal of Marine Science, 60: 658–661. Acoustics present an alternative sampling strategy in areas characterized by steep slopes and rugged terrain where fishing is impractical. However, when the interference between echoes from fish targets and boundaries is severe, acoustic observations require careful interpretation of the echo returns. This article outlines a method of generating a representative 3D model of the bottom topography that can assist in near-boundary fish discrimination. Images provide greater insight to echo source and highlight some of the difficulties associated with classifying acoustic sign. The results emphasize the importance of good survey design aimed at minimizing side-lobe interference and reducing acoustic-shadow zones. Crown Copyright Ó 2003 Published by Elsevier Science Ltd on behalf of International Council for the Exploration of the Sea. All rights reserved. Keywords: acoustics, acoustic-shadow zones, assessment methods, mapping, 3D imaging. K. Cooke, R. Kieser, and R. D. Stanley: Pacific Biological Station, Fisheries and Oceans, Canada, 3190 Hammond Bay Road, Nanaimo, British Columbia, Canada V9T 6N7. Correspondence to K. Cooke: tel.: þ1 250 756 7125; fax: þ1 250 756 7053; e-mail: [email protected]. Introduction Acoustic observation and assessment of fishes is highly influenced by fish behaviour, target size, species mix, and soundbeam characteristics as well as bottom proximity, roughness, and scattering properties. In regions where the acoustic-scattering properties of the substrate are unknown, near-boundary detection problems suggest that the application of acoustics for biomass estimation of some demersal species is problematic (Stanley et al., 2000) and, in some cases, impractical (Richards et al., 1991; Stanley et al., 1999). This work emphasizes that better near-boundary detection requires knowledge of the 3D boundary shape as well as acoustic parameters such as target size, beam pattern, and beam attitude. We describe a sampling strategy using conventional sounders for surveying an area where acoustic bottom returns modified, obscured, or appeared like returns from the target species (Stanley et al., 1999, 2000). Our methods help to visualize the acoustic data in a way that leads to a better understanding of bottom structure and of fish behaviour in relation to their habitat. Background The study site was located at the continental-shelf edge off the west coast of Vancouver Island, British Columbia near 1054–3139/03/000658þ04 $30.00 Pisces Canyon, and had been termed ‘‘Pisces Pinnacles’’ by local fishers (Figure 1). Their acoustic observations showed ‘‘dense rockfish schools’’, but these schools were extremely difficult to fish. Their trawling efforts typically resulted in lost or damaged gear and they were quick to caution that ‘‘what you see is not what you get’’. The area had long been recognized by fishers as one that, despite its relatively innocent look, was considered virtually untrawlable (B. Mose, pers. comm.). We agreed to examine the area acoustically to assess what it was that appeared to be very dense aggregations of rockfish but was in fact ‘‘something more’’ than just fish. Methods Acoustic system and data acquisition Survey operations were carried out from the Canadian Coast Guard Ship ‘‘W.E. Ricker’’, a 58-m stern trawler using a calibrated SIMRAD EK500 sounder, ram-mounted, 38 Hz split-beam transducer (Foote et al., 1987; Simrad, 1993a; Cooke et al., 1996), and BI500 data logger (Simrad, 1993b). We sounded continuously during a 32-h period, 5– 6 February 1998, repeating a sector pattern constructed of six lines bounded by an outer circle of about 2-nmi diameter. Each line crossed a central area of intersection at increments of about 30 . We introduced minor adjustments Crown Copyright Ó 2003 Published by Elsevier Science Ltd on behalf of International Council for the Exploration of the Sea. All rights reserved. Acoustic observation and assessment of fish in high-relief habitats 659 Figure 1. The ‘‘Pisces Pinnacles’’ study site near Pisces Canyon off the west coast of Vancouver Island, British Columbia, with an example of the sector survey pattern used. to line spacing and course heading after each completed circumference of the grid. Geo-referenced, ping-by-ping volume-backscattering strengths (Sv) at 0.5-m depth resolution were continuously logged along the ship’s track to a maximum range of 250 m. Data processing and visualization Sounder-detected, bottom-depth data were used to create an interpolated surface and a series of 3D elevation maps to visualize the bottom topography from various directions and viewpoints (Golden Software, 1996). Echo-editing software (SonarData, 1999) was used to view echograms and to identify ping number, range, Sv, and bottom-detected values. Frame grabs of 2D and 3D bottom images and portions of zoomed echograms were stored in jpeg format (Jasc Software, 2000) and overlaid using Powerpoint97 (Que, 1997) to show ping location and echo returns in relation to bottom structures. Since automatic bottom tracking was often intermittent when the trackline crossed the steepest terrain, we pieced together manually a new ‘‘true bottom’’ outline of the pinnacles based on maximum Sv colour value observed along all transects. Our new ‘‘true bottom’’ outline was superimposed on each of the passes to provide operators with a better understanding of signal source, regardless of proximity of each pass to the formations. Results Survey pattern and mapping We completed five rotations of the grid and added two separate lines for a total of 32 crossings over the central area of intersection (Figure 1). All bottom-depth data were used to generate an interpolated surface and create multiple 2D and 3D views of the same ground (Figure 2). Elevation could only be measured with limited accuracy owing to the motion of the ship caused by wave heights in excess of 3 m. No attempt was made to correct for roll and pitch of the soundbeam. We chose to exaggerate the depth scale to illustrate bottom features more clearly. The images showed a series of closely spaced pinnacles with a maximum height of 12–15 m that rise sharply on all sides, each from a base of about 20 m in diameter. The overall longitudinal extent of the feature is about 150 m with a northwest–southeast orientation. Pinnacle separation varied; some were poorly defined given the relatively few data points used to identify individual structures. Our confidence in the reality of the maps is derived from the overall density of measured depths, the repeatability of their locations as shown from the various passes and knowledge of the relative size of the soundbeam footprint. The interpolated maps provide a visual appreciation of the topography that is essential for improving echogram interpretation. 660 K. Cooke et al. Figure 2. An example of a 3D interpolated elevation map with portions of echograms from two passes overlaid on a ‘‘true bottom’’ image showing ping-by-ping trackline, bottom-detection locations, and Sv values relative to pinnacles. Circled areas indicate the region zoomed for a ‘‘best fit’’ alignment of ping-by-ping positions. Pass 3303 ran parallel but adjacent to the longitudinal axis of the pinnacles; pass 3503 crossed directly over the middle section of the pinnacles. The yellow lines and markers represent sounder-detected bottom tracking for each pass. The darker blue outline depicts the ‘‘true bottom’’ overlay we created to define more clearly acoustic sign near boundaries and identify possible side-lobe signals. Echogram editing Our sounder was unable to track bottom continuously along any transect that crossed directly over all or most of the pinnacles owing to the steepness of the terrain (Figure 2, Pass 3503 bottom track). Little of the high-density acoustic sign observed along these tracks could be classified with certainty, since there was little separation from the bottom signal. For passes that ran near, but not over, the formations, the sounder was able to track bottom (Figure 2, Pass 3303 bottom track). At first, we viewed much of the off-bottom backscatter as typical of high-density fish aggregations. Acoustic observation and assessment of fish in high-relief habitats However, by overlaying the ‘‘true bottom’’ outline, we can more clearly identify possible bottom-tracking limitations and shadow zones associated with side-lobe echoes of the formations. This new insight was the key for classification of echo sign that appeared removed from bottom. Using different perspectives of the same image, and by rotating the images around the formations, we were better able to identify transect bearings that were less affected by bottom structure and soundbeam characteristics, and which were more appropriately oriented for the detection of fish targets. Zones of uncertainty could be better defined or removed entirely from the integration process. Discussion Our images help explain possible reasons for the gear loss experienced by the fishers and serve as a reminder that even the most experienced of operators can easily misinterpret acoustic sign. We were not able to ground truth the acoustic signal but, nonetheless, our work illustrates that having even a limited knowledge of bottom structures can help in survey design and may provide a strong warning against conducting fishing operations in regions of uncertainty. Our results emphasize the need to map and preview study sites and to incorporate all data in the scrutinizing process, especially when near-boundary detection is attempted. In the absence of high-resolution bathymetric data, a single pass with a downward-looking multibeam sonar, or several closely spaced transects with an echosounder could map a narrow survey corridor and assess the acoustic suitability of the area. Once identified, the corridors could be revisited on subsequent surveys. This approach will be valuable for the planning of assessment surveys for near-bottom fish in areas with difficult bottom structure. Although ship time is a major consideration, a single survey may be sufficient to characterize an area and produce suitable maps that could be used over the course of subsequent surveys. Imaging of acoustic data in 3D is an effective tool for examining target distributions (Greene et al., 1998) and shoal behaviour (Stanley et al., 2002). This work describes a new technique for mapping habitat and visualizing echo returns in relation to bottom signal, side-lobe echoes, and beam characteristics. Our results offer a greater under- 661 standing of echo source and improved interpretation of the acoustic returns. References Cooke, K., Saunders, M. W., Andrews, W. T., and Kieser, R. 1996. A hydroacoustic survey of Pacific hake on the continental shelf off British Columbia from the Canada/U.S. boundary to Queen Charlotte Sound: 15–31 August 1994. Canadian Manuscript Report of Fisheries and Aquatic Science, 2363: 51 pp. Foote, K. G., Knudsen, H. P., Vestnes, G., MacLennan, D. N., and Simmonds, E. J. 1987. Calibration of acoustic instruments for fish-density estimation: a practical guide. ICES Cooperative Research Report, No. 144. 70 pp. Golden Software Inc. 1996. Surfer for Windows Version 6 User’s Guide, Contouring and 3D Mapping. Golden Software Inc., Golden, CO. Greene, C. H., Wiebe, P. H., Pelkie, C., Benfied, M. C., and Popp, J. M. 1998. Three-dimensional acoustic visualization of zooplankton patchness. Deep-Sea Research Part II Tropical Studies in Oceanography, 45: 1201–1217. Jasc Software Inc. 2000. Paint Shop Pro 7 and Animation Shop 3 Reference Guide. Jasc Software Inc., Eden Prairie, MN. Que Inc. 1997. Platinum Edition Using Microsoft Office 97. Que Corporation, Indianapolis, IN. Richards, L. J., Kieser, R., Mulligan, T. J., and Candy, J. R. 1991. Classification of fish assemblages based on echo-integration surveys. Canadian Journal of Fisheries and Aquatic Science, 48: 1264–1272. Simrad 1993a. Simrad EK500 Split-Beam Echosounder Instruction Manual. Simrad Subsea A/S, Horten, Norway. Simrad 1993b. Simrad BI500 Post-Processing System Instruction Manual. Simrad Subsea A/S, Horten, Norway. SonarData 1999. SonarData Echoview V1.51 User’s Manual. SonarData Tasmania Pty. Ltd., Hobart, Tasmania, Australia. Stanley, R. D., Cornthwaite, A. M., Kieser, R., Cooke, K., Workman, G. D., and Mose, B. 1999. An acoustic-biomass survey of the Triangle Island widow rockfish (Sebastes entomelas) aggregation by Fisheries and Oceans, Canada and the Canadian Groundfish Research and Conservation Society, 16 January to 7 February 1998. Canadian Technical Report of Fish and Aquatic Science, 2262: 51 pp. Stanley, R. D., Kieser, R., Cooke, K., Surry, A. M., and Mose, B. 2000. Estimation of widow rockfish (Sebastes entomelas) shoal off British Columbia, Canada as a joint exercise between stockassessment staff and the fishing industry. ICES Journal of Marine Science, 57: 1035–1049. Stanley, R. D., Kieser, R., and Hajirakar, M. 2002. Three-dimensional visualization of a widow rockfish (Sebastes entomelas) shoal over interpolated bathymetry. ICES Journal of Marine Science, 59: 151–155.
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