26.03.2013 Views

Acoustic target strength of capelin measured by single-target ...

Acoustic target strength of capelin measured by single-target ...

Acoustic target strength of capelin measured by single-target ...

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

ICES Journal <strong>of</strong> Marine Science, 59: 1081–1085. 2002<br />

doi:10.1006/jmsc.2002.1239, available online at http://www.idealibrary.com on<br />

<strong>Acoustic</strong> <strong>target</strong> <strong>strength</strong> <strong>of</strong> <strong>capelin</strong> <strong>measured</strong> <strong>by</strong> <strong>single</strong>-<strong>target</strong><br />

tracking in a controlled cage experiment<br />

Roar Jørgensen and Kjell Olsen<br />

Jørgensen, R., and Olsen, K. 2002. <strong>Acoustic</strong> <strong>target</strong> <strong>strength</strong> <strong>of</strong> <strong>capelin</strong> <strong>measured</strong> <strong>by</strong><br />

<strong>single</strong>-<strong>target</strong> tracking in a controlled cage experiment. – ICES Journal <strong>of</strong> Marine<br />

Science, 59: 1081–1085.<br />

Knowledge <strong>of</strong> the acoustic <strong>target</strong> <strong>strength</strong> (TS) <strong>of</strong> <strong>capelin</strong>, Mallotus villosus (Müller),<br />

is important to scale integrator outputs for use in acoustic surveys, but experimental<br />

measurements <strong>of</strong> <strong>capelin</strong> TS are scarce. This paper reports a new ex situ experiment on<br />

<strong>capelin</strong> TS. Small groups <strong>of</strong> the fish were kept in a large sea cage that allowed them to<br />

swim freely between 4.5 and 10 m deep. TS measurements were made vertically with a<br />

scientific split-beam echosounder. Differences in behaviour could induce at least a 5 db<br />

change in TS owing to changes in tilt angle. The observed mean TS for <strong>capelin</strong> from<br />

the local Balsfjord stock was >1 db higher than expected from the TS–length<br />

relationship for Barents Sea <strong>capelin</strong> used during abundance estimation.<br />

2002 International Council for the Exploration <strong>of</strong> the Sea. Published <strong>by</strong> Elsevier Science Ltd.<br />

All rights reserved.<br />

Keywords: cage experiment, <strong>capelin</strong>, <strong>target</strong> <strong>strength</strong>, <strong>target</strong> tracking.<br />

Received 24 July 2001; accepted 30 March 2002.<br />

R. Jørgensen and K. Olsen: Norwegian College <strong>of</strong> Fishery Science, University<br />

<strong>of</strong> Tromsø, N-9037 Tromsø, Norway; tel: +47 77 646084; fax: +47 77 646020;<br />

e-mail: roarj@nfh.uit.no.<br />

Introduction<br />

The stock <strong>of</strong> <strong>capelin</strong>, Mallotus villosus (Müller), in the<br />

Barents Sea is potentially the largest in the world,<br />

its biomass in some years reaching 6–8 million tons.<br />

It is the largest stock <strong>of</strong> pelagic fish in the Barents Sea<br />

and supports many populations <strong>of</strong> predatory fish,<br />

marine mammals, and seabirds. It has provided an<br />

annual fishery harvest <strong>of</strong> up to 3 million tons<br />

(Gjøsæter, 1998). <strong>Acoustic</strong> surveys in addition to<br />

information from catch statistics have provided the<br />

only information on stock status to date (Gjøsæter,<br />

1998; Toresen et al., 1998). In situ and (or) experimental<br />

measurements <strong>of</strong> <strong>capelin</strong> acoustic <strong>target</strong><br />

<strong>strength</strong> (TS) are scarce, but knowledge <strong>of</strong> <strong>capelin</strong> TS<br />

is important for scaling integrator output for use in<br />

acoustic surveys. Dalen et al. (1976) <strong>measured</strong> dead or<br />

stunned <strong>capelin</strong> and derived an equation for total<br />

length dependency <strong>of</strong> the maximum dorsal aspect TS<br />

for a mixture <strong>of</strong> several physostome fish (including<br />

<strong>capelin</strong>). Olsen and Angell (1983) conducted TS<br />

measurements on small groups <strong>of</strong> live <strong>capelin</strong> enclosed<br />

in a cage and found that the TS <strong>of</strong> mature fish was<br />

tilt-angle dependent, when observed <strong>by</strong> a 38 kHz echosounder.<br />

The mean <strong>target</strong> <strong>strength</strong> currently used for acoustic<br />

abundance estimates <strong>of</strong> the Barents Sea <strong>capelin</strong> stock is<br />

a pooled result <strong>of</strong> experimental and field measurements,<br />

including counting/integration on <strong>single</strong>-fish echo traces<br />

(Dalen and Nakken, 1983; Dommasnes and Røttingen,<br />

1984). The equation used is<br />

TS=19.1log 10(l)74 (1)<br />

where l is total length.<br />

This paper reports on <strong>capelin</strong> TS at 38 kHz <strong>measured</strong><br />

<strong>by</strong> <strong>single</strong>-<strong>target</strong> tracking in a controlled experiment.<br />

Material and methods<br />

The experiment was carried out in a net pen at the<br />

fish farming plant <strong>of</strong> the Ka˚rvika Aquaculture Station,<br />

situated at Ringvassøya, an island northwest <strong>of</strong> Tromsø<br />

in northern Norway. Capelin were captured from the<br />

local stock in Balsfjord, close to Tromsø, during April<br />

2000. They were caught during beach-spawning with a<br />

small shore-seine and carefully transported to Ka˚rvika<br />

in a tank with oxygenated water. The fish were kept in<br />

larger tanks at the station, and were fed until the day<br />

they were transferred to the net pen.<br />

1054–3139/02/101081+05 $35.00/0 2002 International Council for the Exploration <strong>of</strong> the Sea. Published <strong>by</strong> Elsevier Science Ltd. All rights reserved.


1082 R. Jørgensen and K. Olsen<br />

Figure 1. Schematic overview <strong>of</strong> the experimental set-up: (1)<br />

pier, (2) net pen, (3) net ro<strong>of</strong>, (4) big weight, (5) small weight,<br />

(6) air-filled aluminium frame, (7) split-beam transducer, (8)<br />

cable, (9) dry lab with echosounder and computer equipment.<br />

The arrows show how the net pen and the aluminium frame<br />

could be lifted and suspended <strong>by</strong> pulling the smaller weights.<br />

Small groups <strong>of</strong> <strong>capelin</strong> were allowed to swim freely in the pen;<br />

only one fish is shown here.<br />

The experimental net pen was 5510 m with a<br />

mesh size <strong>of</strong> 11 mm (Figure 1). The bottom <strong>of</strong> the pen<br />

was attached to a 5.25.2 m air-filled aluminium frame<br />

stabilized <strong>by</strong> four 20 kg weights. The net pen and the<br />

aluminium frame could be lifted and suspended <strong>by</strong><br />

pulling smaller weights attached to the aluminium frame<br />

(Midling et al., 1998). To keep the <strong>capelin</strong> well outside<br />

the transducer nearfield, a ‘‘ro<strong>of</strong>’’ was installed in the net<br />

pen at a depth <strong>of</strong> 4.5 m. Under the ro<strong>of</strong>, <strong>capelin</strong> were<br />

allowed to move freely between 4.5 and 10 m deep in a<br />

120 m 3 cage shaped as a 554.5 m box with an<br />

additional ro<strong>of</strong> extension 1 m high. The echo from the<br />

net ro<strong>of</strong> (TS


Table 1. Parameter settings and calibration parameters for the EY500 system.<br />

Parameter<br />

maximal vertical movement between consecutive detections<br />

was 10 cm. The tracking output files were reformatted<br />

and imported to SYSTAT (SPSS Inc.) and<br />

MATLAB (Math Works Inc.) for final statistical<br />

analysis.<br />

TS measurements were conducted on several different<br />

groups <strong>of</strong> <strong>capelin</strong>. However, results from just one group<br />

passed the criteria for <strong>single</strong>-fish echo traces: other<br />

groups did not disperse sufficiently to avoid multiple<br />

echoes. This actual group was transferred to the net pen<br />

on 22 June 2000; it consisted <strong>of</strong> 12 female and 3 male<br />

post-spawning Balsfjord <strong>capelin</strong>. The fish were allowed<br />

to acclimatize for 10 h in the net pen prior to TS data<br />

collection. In all, 5 fish, all females, died during the two<br />

2 d experiments. Fish schooled during daylight, but<br />

partly dispersed at night and in the early morning.<br />

Echo-trace data were recorded between 5.8 and<br />

9 m deep; they consisted <strong>of</strong> 6569 TS data distributed<br />

in 273 echo traces, with 5–91 TS detections in each<br />

trace.<br />

A relationship between tilt angle and <strong>target</strong> <strong>strength</strong><br />

for an individual <strong>capelin</strong> was estimated <strong>by</strong> relating TS to<br />

the movement <strong>of</strong> a fish in a selected 33-ping-long echo<br />

trace. For one transmission (‘‘ping’’), n, the angles and<br />

define the <strong>target</strong> direction relative to the acoustic<br />

axis in alongship and athwartship planes respectively.<br />

For small angles, the angle from the acoustic axis is<br />

Date (2000)<br />

05 June 05 June 05 June 26 June 26 June<br />

Sound speed (m s 1 ) 1472 1472 1472 1480 1480<br />

Ping rate (s) 1 1 1 0.0 1<br />

Range (m) 4 5 6 6.4 6.4<br />

RMS (dB) 0.10 0.08 0.08 0.12 0.10<br />

TS gain (dB) 21.3 21.2 21.1 20.5 21.1<br />

3dBbeamwidth()<br />

Athwartship 11.8 12.0 12.1 12.1 12.0<br />

Alongship 12.0 12.3 12.4 12.4 12.4<br />

Offset angle ()<br />

Athwartship 0.19 0.04 0.19 0.00 0.22<br />

Alongship 0.14 0.00 0.18 0.01 0.18<br />

Table 2. Target <strong>strength</strong> detection parameters for the EY500.<br />

Parameter Value<br />

Minimum value<br />

Echo length<br />

70 dB<br />

Minimum 0.8 ms<br />

Maximum 1.8 ms<br />

Maximum gain compensation 6.0 dB<br />

Maximum phase deviation 3.0 steps<br />

<strong>Acoustic</strong> <strong>target</strong> <strong>strength</strong> <strong>of</strong> <strong>capelin</strong><br />

given <strong>by</strong>:<br />

n=√( 2<br />

n+ 2<br />

n) (Reynisson, 1999) (2)<br />

The three-dimensional movement <strong>of</strong> the <strong>capelin</strong> at a<br />

given range (r n) was thus transformed to Cartesian<br />

coordinates alongship:<br />

x n=r n sin( n) (3)<br />

and athwartship:<br />

y n=r n sin( n) (4)<br />

In depth this gives:<br />

1083<br />

z n= r n cos( n) (5)<br />

Random variations <strong>of</strong> <strong>target</strong> positioning were<br />

removed <strong>by</strong> smoothing each coordinate with kernelweighted<br />

polynomial regression (Wilkinson, 1999), with<br />

time as independent variable. The angle, n, between the<br />

line <strong>of</strong> movement from ping n1 to ping n and the<br />

transducer’s face was given <strong>by</strong>:<br />

n=atan{(z nz n1)/√[(x nx n1) 2 +(y ny n1) 2 ]} (6)<br />

The tilt angle in the first ping was estimated to be<br />

equal to the tilt angle in the second ping ( 1= 2).<br />

The smoothed angle from the acoustic axis ( n) was<br />

computed from the smoothed Cartesian coordinates:<br />

n=acos{√[z n/(x 2<br />

n+y 2<br />

n+z 2<br />

n)]} (7)<br />

Because the fish in the selected trace moved approximately<br />

parallel to the alongship axis (x), the tilt angle<br />

could be computed <strong>by</strong> simply adding n to n (x n>0) or<br />

subtracting n from n (x n


1084 R. Jørgensen and K. Olsen<br />

Count<br />

1000<br />

800<br />

600<br />

400<br />

200<br />

0<br />

–57<br />

Results<br />

–56 –55 –54 –53 –52 –51 –50 –49<br />

Target <strong>strength</strong> (dB)<br />

Figure 2. Target-<strong>strength</strong> distribution <strong>of</strong> all observations in the<br />

ex situ experiment (n=6569). The vertical line shows the mean<br />

<strong>target</strong> <strong>strength</strong>, 52.5 db.<br />

Depth (m)<br />

5.55<br />

5.6<br />

5.65<br />

5.7<br />

5.75<br />

5.8<br />

5.85<br />

–0.4<br />

–0.2 0 0.2 0.4 0.6<br />

Alongship (m)<br />

Figure 3. Vertical movements <strong>of</strong> a <strong>capelin</strong> in one echo trace<br />

(n=33). Crosses show actual measurements and arrows show<br />

the direction <strong>of</strong> movement. The smoothed line describes<br />

estimated movement alongship and in depth.<br />

The total length <strong>of</strong> the 15 fish ranged from 10.5 to<br />

12.3 cm, with a mean <strong>of</strong> 11.3 cm (s.d.=0.5). The mean<br />

length <strong>of</strong> the 10 fish alive at the end <strong>of</strong> the experiment<br />

was 11.4 cm (s.d.=0.5).<br />

The TS distribution <strong>of</strong> all valid measurements (Figure<br />

2) is rather narrow, ranging from 49 to 57 dB.<br />

By computing the mean <strong>of</strong> the acoustic backscattering<br />

cross-section, the corresponding mean TS was<br />

52.5 dB (vertical line in Figure 2).<br />

The swimming behaviour <strong>of</strong> a fish in an echo trace is<br />

shown in Figure 3. This fish moved approximately<br />

parallel to the alongship axis through the centre <strong>of</strong> the<br />

beam. The effect <strong>of</strong> tilt angle on TS for this trace<br />

Target <strong>strength</strong> (dB)<br />

–50<br />

–51<br />

–52<br />

–53<br />

–54<br />

–55<br />

Head up<br />

Head down<br />

–56<br />

30 20 10 0 –10 –20 –30 –40 –50<br />

Tilt angle (°)<br />

Figure 4. Successive <strong>target</strong>-<strong>strength</strong> observations (circles) in<br />

relation to estimated tilt angle during one echo trace (n=33).<br />

observation is estimated and plotted in Figure 4. For<br />

this <strong>single</strong> <strong>capelin</strong>, the dotted lines that connect the<br />

estimated points (circle) in Figure 4 suggest a maximum<br />

TS with near-horizontal swimming behaviour. The echo<br />

trace has about 5 dB range in TS.<br />

Discussion<br />

If the current TS-length relationship used for Barents<br />

Sea <strong>capelin</strong> surveys (equation 1) is applied, a mean TS <strong>of</strong><br />

53.8 dB for the 10 <strong>capelin</strong> that survived the experiment<br />

would be generated. This is 1.3 dB lower than<br />

estimated during the current measurements. This discrepancy<br />

could be due to differences in behaviour <strong>of</strong><br />

captive <strong>capelin</strong> compared with fish in the open ocean.<br />

Capelin in their natural environment may have a different<br />

tilt-angle distribution than in the net pen, and this<br />

could influence the mean TS (Olsen and Angell, 1983).<br />

Target <strong>strength</strong> in this experiment has been <strong>measured</strong><br />

close to the surface, whereas TS at greater depth may be<br />

lower owing to there being no compensation for<br />

the swimbladder during vertical migration (Ona, 1990).<br />

Furthermore, seasonal variations caused <strong>by</strong> the fat cycle<br />

and gonad development can effect the TS <strong>of</strong> fish such as<br />

herring Clupea harengus (Ona, 1990) and <strong>capelin</strong> (Rose,<br />

1998). These factors may cause the <strong>target</strong> <strong>strength</strong> <strong>of</strong> the<br />

lean post-spawning Balsfjord <strong>capelin</strong> to be different<br />

from that <strong>of</strong> Barents Sea <strong>capelin</strong> during the acoustic<br />

assessment survey in autumn, when <strong>capelin</strong> have a<br />

higher fat content. Reduced swimbladder size as a result<br />

<strong>of</strong> higher fat content may in fact lead to a reduced mean<br />

<strong>target</strong> <strong>strength</strong>. A general conclusion is, however, that,<br />

at surface levels, the <strong>target</strong> <strong>strength</strong> <strong>of</strong> <strong>capelin</strong> is lower<br />

than that <strong>of</strong> other species such as cod Gadus morhua and<br />

herring.


The bimodality <strong>of</strong> the TS distributions shown in<br />

Figure 2 may be related to up-and-down swimming<br />

behaviour <strong>of</strong> the <strong>capelin</strong> or differences in the acoustic<br />

backscattering properties for different fish in the group.<br />

The 30 dB<br />

range found in a similar experiment with mature herring<br />

(Zhao, 1996). At 38 kHz, the drop in <strong>target</strong> <strong>strength</strong><br />

attributable to changes in tilt angle is expected to be<br />

considerably smaller for a more omnidirectional backscattering<br />

<strong>target</strong> such as a 11 cm <strong>capelin</strong>, than for a<br />

30 cm herring (Nakken and Olsen, 1977). This is because<br />

the difference between fish length and the wavelength <strong>of</strong><br />

the transmitted sound at 38 kHz is smaller for <strong>capelin</strong><br />

than for herring.<br />

Acknowledgements<br />

We thank E. Ona and I. Svellingen (IMR) for technical<br />

assistance and for valuable comments on the manuscript.<br />

Special thanks to local fisher H. Frydenlund for<br />

catching the Balsfjord <strong>capelin</strong>, and to J. S. Christiansen<br />

and B. S. Sæther for keeping them in tanks and providing<br />

us with live material. We are grateful to L. P.<br />

Jørgensen and his crew at the fish farming plant at the<br />

Tromsø Aquaculture Research Station for all their various<br />

assistance. The Norwegian Research Council funded<br />

the study.<br />

References<br />

Brede, R., Kristensen, F. H., Solli, H., and Ona, E. 1990.<br />

Target tracking with a split-beam echo sounder. Rapports et<br />

Procès-Verbaux des Réunions du Conseil International pour<br />

l’Exploration de la Mer, 189: 254–263.<br />

Dalen, J., and Nakken, O. 1983. On the application <strong>of</strong> the echo<br />

integration method. ICES CM 1983/B: 19, 30 pp.<br />

Dalen, J., Raknes, A., and Røttingen, R. 1976. Target <strong>strength</strong><br />

measurements and acoustic biomass estimation <strong>of</strong> <strong>capelin</strong><br />

and 0-group fish. ICES CM 1976/B: 37, 9 pp.<br />

Dommasnes, A., and Røttingen, I. 1984. <strong>Acoustic</strong> stock<br />

measurements <strong>of</strong> the Barents Sea <strong>capelin</strong> 1972–1984, a<br />

review. In Proceedings <strong>of</strong> the Soviet-Norwegian Symposium<br />

<strong>Acoustic</strong> <strong>target</strong> <strong>strength</strong> <strong>of</strong> <strong>capelin</strong><br />

1085<br />

on the Barents Sea Capelin, pp. 45–63. Ed. <strong>by</strong> H. Gjøsæter.<br />

Institute <strong>of</strong> Marine Research, Bergen, Norway.<br />

Foote, K. G., and MacLennan, D. N. 1984. Comparison <strong>of</strong><br />

copper and tungsten carbide spheres. Journal <strong>of</strong> the<br />

<strong>Acoustic</strong>al Society <strong>of</strong> America, 75: 612–616.<br />

Foote, K. G., Aglen, A., and Nakken, O. 1986. Measurement<br />

<strong>of</strong> fish <strong>target</strong> <strong>strength</strong> with a split-beam echo sounder.<br />

Journal <strong>of</strong> the <strong>Acoustic</strong>al Society <strong>of</strong> America, 80: 612–621.<br />

Gjøsæter, H. 1998. The population biology and exploitation <strong>of</strong><br />

<strong>capelin</strong> (Mallotus villosus) in the Barents Sea. Sarsia, 83:<br />

453–496.<br />

Midling, K. Ø., Aas, K., Isaksen, B., Pettersen, J., and<br />

Jørgensen, S. H. 1998. A new design in transportation and<br />

net cage technology for live seafood and aquacultural<br />

purposes. ICES CM 1998/L: 15, 7 pp.<br />

Nakken, O., and Olsen, K. 1977. Target <strong>strength</strong> measurements<br />

<strong>of</strong> fish. Rapports et Procès-Verbaux des Réunions du Conseil<br />

International pour l’Exploration de la Mer, 170: 52–69.<br />

Olsen, K., and Angell, J. 1983. A comparison <strong>of</strong> different<br />

echo abundance conversion methods. ICES CM 1983/B: 17,<br />

12 pp.<br />

Ona, E. 1990. Physiological factors causing natural variations<br />

in acoustic <strong>target</strong> <strong>strength</strong> <strong>of</strong> fish. Journal <strong>of</strong> the Marine<br />

Biological Association <strong>of</strong> the United Kingdom, 70: 107–127.<br />

Ona, E., and Hansen, D. 1991. S<strong>of</strong>tware for <strong>target</strong> tracking<br />

with split beam echo sounders. User manual. Institute <strong>of</strong><br />

Marine Research, Bergen, Norway, October 1991. 21 pp.<br />

Ona, E., Zhao, X., Svellingen, I., and Foote, K. G. 1996. Some<br />

pitfalls <strong>of</strong> short-range standard-<strong>target</strong> calibration. ICES CM<br />

1996/B: 36, 18 pp.<br />

Reynisson, P. 1999. Split beam method. In Methodology for<br />

Target Strength Measurements, pp. 19–27. Ed. <strong>by</strong> E. Ona.<br />

ICES Cooperative Research Report, 235.<br />

Rose, G. A. 1998. <strong>Acoustic</strong> <strong>target</strong> <strong>strength</strong> <strong>of</strong> <strong>capelin</strong> in<br />

Newfoundland waters. ICES Journal <strong>of</strong> Marine Science, 55:<br />

918–923.<br />

SIMRAD. 1999. SIMRAD EY500 Portable Scientific Echo<br />

Sounder (Version 5.33). Instruction manual. SIMRAD,<br />

Norway. 243 pp.<br />

Toresen, R., Gjøsæter, H., and de Barros, P. 1998. The acoustic<br />

method as used in the acoustic abundance estimation <strong>of</strong><br />

<strong>capelin</strong> (Mallotus villosus Müller) and herring (Clupea<br />

harengus Linné) in the Barents Sea. Fisheries Research, 34:<br />

27–37.<br />

Wilkinson, L. 1999. Manuals. SYSTAT 9.0. SPSS Inc. 2469 pp.<br />

Zhao, X. 1996. Target <strong>strength</strong> <strong>of</strong> herring (Clupea harengus L.)<br />

<strong>measured</strong> <strong>by</strong> the split-beam tracking method. Masters thesis,<br />

Department <strong>of</strong> Fisheries and Marine Biology, Bergen.<br />

103 pp.

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!