Bottom Trawl Surveys - Proceedings of a Workshop Held at Ottawa ...
Bottom Trawl Surveys - Proceedings of a Workshop Held at Ottawa ...
Bottom Trawl Surveys - Proceedings of a Workshop Held at Ottawa ...
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2. TRAWL GEAR<br />
The fishing gear used during the research<br />
surveys on board the "CRYOS" is the standard<br />
trawl "L<strong>of</strong>oten" with 31.20 m headline and 17.70<br />
m footrope, 140 mm stretched mesh in the wings<br />
and body and 50 mm stretched mesh in the<br />
codend. A detailed diagram <strong>of</strong> this gear is<br />
provided in Fig. 1.<br />
The design <strong>of</strong> the rigging as well as<br />
details <strong>of</strong> flo<strong>at</strong>s, sweepline, boards and opening<br />
<strong>of</strong> the trawl are given in Fig. 2. More precise<br />
details <strong>of</strong> the groundrope and steel-bobbins used<br />
can be obtained from Fig. 3.<br />
3. SAMPLING DESIGN<br />
STRATIFICATION - The scheme used is<br />
described by Pinhorn (1g72) and Pitt (1g76) and<br />
-shown in Fig. 4.<br />
The str<strong>at</strong>ified portion <strong>of</strong> NAFD Subdiv. 3Ps<br />
represents 17.575 square nautical miles divided<br />
into 33 str<strong>at</strong>a.<br />
SELECTION PROCEDURE - Positions <strong>of</strong> the<br />
trawling st<strong>at</strong>ions are determined by selecting,<br />
for each str<strong>at</strong>um, the sampling units <strong>of</strong> the<br />
master chart using a random number table. In<br />
case <strong>of</strong> rough bottom, as observed on the shelf<br />
<strong>of</strong> St. Pierre Bank <strong>at</strong> depths inferior to 30<br />
f<strong>at</strong>homs in str<strong>at</strong>a No. 314 and 320, the loc<strong>at</strong>ion<br />
<strong>of</strong> the tow is chosen to be as close as possible<br />
to the originally selected position.<br />
Two to five sets are chosen for each<br />
str<strong>at</strong>um, depending on its surface.<br />
TRAWLING OPERATIONS - St<strong>at</strong>ions are visited<br />
on a twelve-hour basis, during daylight.<br />
Dur<strong>at</strong>ion <strong>of</strong> the tow is 30 minutes on the bottom<br />
(measured between the applic<strong>at</strong>ion and the<br />
release <strong>of</strong> the winch brakes), <strong>at</strong> a speed <strong>of</strong> 4<br />
knots. The length <strong>of</strong> wire varies with depth by<br />
a r<strong>at</strong>io <strong>of</strong> 3 to 4 in these shallow w<strong>at</strong>ers, as<br />
illustr<strong>at</strong>ed by Fig. 5.<br />
To gain inform<strong>at</strong>ion on the n<strong>at</strong>ure <strong>of</strong> the<br />
bottom, a special device is fixed on the<br />
groundrope to collect a sample <strong>of</strong> sediments<br />
during the tow. Also a system<strong>at</strong>ic XBT cast is<br />
made during or after trawling.<br />
When the gear grips on the bottom, the tow<br />
may be interrupted before the 30 minutes have<br />
elapsed. If the tow lasts <strong>at</strong> least 15 minutes,<br />
the results are considered valid and weighted<br />
for a 3D-minute dur<strong>at</strong>ion. When it lasts for<br />
less than 15 minutes, the results <strong>of</strong> the tow are<br />
not taken into account.<br />
In cases <strong>of</strong> serious damage to the gear or<br />
rigging, after a 30-minute dur<strong>at</strong>ion tow, the<br />
results are system<strong>at</strong>ically discarded.<br />
All this field inform<strong>at</strong>ion as well as th<strong>at</strong><br />
on meteorology, gear, c<strong>at</strong>ches and w<strong>at</strong>er<br />
temper<strong>at</strong>ure are recorded on the form shown in<br />
Fig. 6A.<br />
SAMPLING OF CATCHES- All c<strong>at</strong>ches are<br />
sorted by species. Each species <strong>of</strong> fish is<br />
weighed; the totality <strong>of</strong> each species sampled<br />
(or a random sub-sample in the case <strong>of</strong> large<br />
c<strong>at</strong>ches) is numbered. Thus, for each species,<br />
the number and weight per 30-minute tow is<br />
obtained. Among the invertebr<strong>at</strong>es (mainly<br />
crustaceans and molluscs) the non-commercial<br />
species are noted, their abundance estim<strong>at</strong>ed and<br />
observ<strong>at</strong>ions on communities and other pertinent<br />
ecological factors recorded. The commercial<br />
species <strong>of</strong> invertebr<strong>at</strong>es are weighted and<br />
numbered using the same method as for fish.<br />
The main commercial species (cod, redfish,<br />
American plaice, witch, yellowtail, haddock,<br />
halibut, anglerfish, squid, scallops, ... ) are<br />
measured in totality, or after sampling (random<br />
or str<strong>at</strong>ified according to the size <strong>of</strong><br />
species). All measurements are made, after sex<br />
determin<strong>at</strong>ion, in order to obtain length<br />
frequencies <strong>of</strong> sexes separ<strong>at</strong>ely and sex-r<strong>at</strong>io.<br />
Measurements are made on standard boards (or<br />
with a calliper-square) and recorded on the d<strong>at</strong>a<br />
sheet (Fig. 6B). For fish, total length is<br />
measured to the nearest centimeter (or<br />
half-centimeter) below. Squid mantles are<br />
measured to the nearest half-centimeter below<br />
and height <strong>of</strong> shells to the nearest millimeter<br />
below. For crustaceans, carapace lengths are<br />
measured from the hi<strong>at</strong>us <strong>of</strong> the eye to the<br />
posterior edge.<br />
For each commercial fish (mostly gadoids,<br />
redfish and fl<strong>at</strong>fishes) a str<strong>at</strong>ified sample <strong>of</strong><br />
otoliths is progressively obtained <strong>at</strong> each<br />
st<strong>at</strong>ion during the whole survey. For cod, 4<br />
pairs are sampled per 1 em class for fish<br />
measuring less than 60 em, or 8 pairs for fish<br />
larger than 60 em. For redfish, 10 pairs are<br />
sampled per 1 em class and for fl<strong>at</strong>fishes, 5<br />
pairs are sampled per 1 em class.<br />
For length-weight keys, individual weights<br />
are obtained on small precise scales.<br />
Also, when sexing fish, m<strong>at</strong>urity stages are<br />
observed using a standard m<strong>at</strong>urity scale for<br />
each species and recorded on the forms.<br />
Observ<strong>at</strong>ions on repletion and stomach<br />
contents are also roughly noted for the main<br />
commercial fish, unless a special feeding study<br />
justifies collection <strong>of</strong> frozen stomachs.<br />
Miscellaneous observ<strong>at</strong>ions on c<strong>at</strong>ches are<br />
also made and reported on forms (necrosis,<br />
parasites, ... ). Samples <strong>of</strong> 6 kg <strong>of</strong> each species<br />
are also collected during each survey, for<br />
pollution studies (hydrocarbons, radio-activity,<br />
etc ... ).<br />
ABUNDANCE ESTIMATES<br />
The following formulae (Pennington and<br />
Grosslein, 1g78) are_used for the calcul<strong>at</strong>ion <strong>of</strong><br />
the str<strong>at</strong>ified mean Yst_(weight or number per<br />
tow and its variance V{Ystl:<br />
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