CCAMLR Science, Vol. 9 (2002): 83–105
83
DISTRIBUTION AND SIZE OF ANTARCTIC KRILL (EUPHAUSIA SUPERBA DANA)IN POLISH COMMERCIAL CATCHES TAKEN IN THE ATLANTIC SECTOR
OF THE SOUTHERN OCEAN FROM 1997 TO 1999
E. Jackowski Sea Fisheries Institute
ul. Kollataja 181-332 Gdynia, Poland
Email – [email protected]
Abstract
The distribution and internal structure of commercial krill concentrations were investigated in the areas of the South Shetland, Elephant, South Georgia and South Orkney Islands in the spring and summer from 1997 to 1999. The density of concentrations varied with area and season. The densest concentrations were found near the South Shetlands. Concentrations at night were several times less dense than those observed during the day. Between February and April the density of concentrations increased, while in May and June it decreased. From February to June the period of daylight becomes progressively shorter, therefore it must be assumed that there are factors other than daylight which have an impact on the density of krill concentrations. The internal structure of concentrations was very diverse, and mean density varied from 11 to 31 370 specimens per 1 000 m3. At night, krill concentrations were scattered throughout the water column, however no clear evidence of vertical migrations was found. Between February and April concentrations occurred in much shallower waters at night than during the day, while in May and June they occurred at the same depths at night as during the day or sometimes even deeper. Between February and April concentrations during the day were found in shallower waters, while between April and June they were found in deeper waters. The size structure of the krill varied during all periods and in all areas, however krill size was observed to decrease as the season progressed.
Résumé
Étude de la distribution et la structure interne des concentrations commerciales de krill dans les secteurs des îles Shetland du Sud, Éléphant, de la Géorgie du Sud et des Orcades du Sud pendant les printemps et étés de 1997 à 1999. La densité des concentrations variait en fonction du secteur et de la saison avec les plus fortes densités près des îles Shetland du Sud. La nuit, les concentrations étaient nettement moins denses que celles qui avaient été observées pendant la journée. De février à avril la densité des concentrations a augmenté, alors qu’elle a diminué en mai et en juin. De février à juin, la durée du jour devient de plus en plus courte, ce qui laisse penser que la densité des concentrations de krill dépend de facteurs autres que la lumière du jour. La structure interne des concentrations était très diverse, la densité moyenne variant de 11 à 31 370 spécimens par 1 000 m3. La nuit, les concentrations de krill s’éparpillaient dans la colonne d’eau, sans toutefois qu’une migration verticale n’ait été mise en évidence. De février à avril, les concentrations fréquentaient des eaux beaucoup moins profondes la nuit que le jour, alors qu’en mai et juin, les profondeurs étaient les mêmes, ou parfois plus grandes la nuit. De février à avril, elles évoluaient dans les eaux moins profondes pendant la journée, alors que d’avril à juin, on les trouvait dans des eaux plus profondes. La structure de tailles du krill variait en fonction de chaque période et de chaque secteur, mais la taille du krill observé a diminué tout au long de la saison.
Резюме
Были изучены распределение и внутренняя структура коммерческих концентраций криля в районах Южной Георгии, Южных Шетландских и Южных Оркнейских о-вов и о-ва Элефант весной и летом 1997–1999 г. Плотность концентраций изменялась в зависимости от района и сезона. Самые плотные скопления были отмечены у Южных Шетландских о-вов. Плотность концентраций ночью была в несколько раз ниже, чем днем. С февраля по апрель плотность концентраций увеличивалась, а в мае и июне она сокращалась. С февраля по июнь период дневного освещения постепенно сокращается, поэтому необходимо предположить, что на плотность скоплений криля влияют факторы, отличные от продолжительности
Jackowski
84
INTRODUCTION
In the CCAMLR Convention Area krill is mostly harvested in the Atlantic sector of the Southern Ocean (FAO Statistical Area 48).
Commercial krill concentrations in the Atlantic sector (Everson and Goss, 1991) occur mainly in the vicinity of the South Shetland, South Orkney and South Georgia Islands. Studies focused on the biology and distribution of krill concentrations have been carried out since the beginning of commercial exploitation. However, most of these studies have been short term, therefore their results do not refl ect the year-round structure of krill concentrations. Additionally, the use of various in-vestigation methods makes evaluating the structure and distribution of krill concentrations diffi cult. Some studies have examined the seasonal and interannual variability of krill concentrations. The use of hydroacoustic techniques has yielded basic information on the structure of krill concentrations (Kalinowski and Witek, 1982, 1985a, 1985b; Witek et al., 1981; Macaulay et al., 1984).
Antarctic krill (Euphausia superba) forms dense concentrations over an area of many square kilo-metres. The structure of these concentrations is very diverse, and they can consist of smaller or larger shoals of various densities (Kalinowski and Witek, 1982; Watkins et al., 1990). Sometimes the shoals in one concentration can be as dense as 30 000 specimens per m-3 of water (Hamner et al., 1983).
Hardy and Günther (1935) and Marr (1962) produced a diagram showing the distribution of krill aggregations at different times of day and night in the South Georgia area. Shevtsov and Makarov (1969) have described krill distribu-tion in the Atlantic sector. Pavlov (1974) produced a diagram illustrating the vertical migration of E. superba in relation to diurnal feeding rate. Mohr (1976) described vertical distribution in the South Sandwich Islands area in relation to the daylight cycle. Kalinowski and Witek (1980) considered krill distribution relative to periods of daylight, feeding and environmental condition.
дня. Внутренняя структура концентраций была очень разнообразной: средняя плотность составляла от 11 до 31 370 особей на 1000 м3. Ночью скопления криля рассредоточивались в толще воды, однако явных доказательств вертикальной миграции не было. С февраля по апрель концентрации встречались в намного более мелких водах ночью, чем днем, в то время как в мае и июне они находились ночью на тех же глубинах, что и днем, а иногда даже глубже. В дневное время скопления встречались в более мелких водах в период с февраля по апрель и в более глубоких водах в апреле и июне. Размерная структура криля варьировала во все периоды и во всех районах, однако, по наблюдениям, размер криля уменьшался с течением сезона.
Resumen
Se estudió la distribución y estructura interna de las concentraciones comerciales de kril en los archipiélagos de las islas Shetland del Sur, Elefante, Georgia del Sur y Orcadas del Sur en la primavera y verano de los años 1997 a 1999. La densidad de las concentraciones varió de acuerdo con la región y temporada. Las concentraciones más densas se encontraron cerca de las islas Shetland del Sur. La densidad de las concentraciones observada durante la noche fue mucho menor que la observada durante el día. La densidad aumentó de febrero a abril y disminuyó en mayo y junio. De febrero a junio el período de luz diurna se acorta progresivamente, por lo tanto cabe suponer que hay otros factores que afectan la densidad de las concentraciones de kril aparte de las horas de luz diurna. La estructura interna de las agregaciones varió considerablemente y la densidad promedio fl uctuó entre 11 y 31 370 ejemplares por 1 000 m3. En la noche las concentraciones de kril se encontraron dispersas a través de la columna de agua, sin embargo, no se encontraron pruebas fehacientes de migraciones verticales. Entre febrero y abril se observó que el kril se concentró en aguas menos profundas por la noche, mientras que en mayo y junio no hubo diferencia en el intervalo de profundidad entre la noche y el día, e incluso a veces, las concentraciones se encontraron en aguas más profundas. Entre febrero y abril el kril se congregó en aguas menos profundas durante el día, mientras que de abril a junio esto ocurrió en aguas más profundas. En todos los períodos y en todas las regiones la estructura de tallas del kril fue diferente, sin embargo, se observó que la talla del kril disminuye en el transcurso de la temporada.
Keywords: krill, density, vertical migration, length, CCAMLR
85
Distribution and size of krill in Polish commercial catches, 1997–1999
Most of the works cited above have dealt with a limited amount of material, therefore the results were frequently contradictory and it was impos-sible to draw general conclusions. In order to better understand how the Southern Ocean ecosystem functions, and to protect its living resources, the biology of E. superba, the key species in Antarctica, needs to be studied in more detail. Knowledge of krill density and the migration process is neces-sary to understand the trophic relationships in the Southern Ocean ecosystem and to make a proper estimation of krill biomass.
The aim of this study is to characterise com-mercial concentrations of krill, and their density and distribution relative to the season, depth strata and krill size in these concentrations during the 1997, 1998 and 1999 krill fi shing seasons in the Atlantic sector.
MATERIALS AND METHODS
Material for the investigations was collected on board the Polish commercial vessel FV Pollux in the summers of 1997, 1998 and 1999 (Figure 1). This vessel fi shed for krill alongside other vessels in different areas of the Atlantic sector that yield the best commercial catches of krill. Each year, the periods when krill concentrations were found in various areas of the sector were determined. Entries in the ship’s log were used to determine krill distribution. A WP/42+42/94 x 4 pelagic trawl with 20 mm mesh (10 mm side) in the codend was used.
Krill density in each haul was estimated as the ratio of krill weight in the catch to the volume of water fi ltered, and was expressed as the number of specimens per 1 000 m3 (specimens/1 000 m3). For calculating the volume of water fi ltered, the vertical trawl opening was assumed to be 35–40 m (average 37.5 m). The trawling speed varied from 2.1 to 2.8 knots and was recorded separately for each haul. Mean daytime haul duration varied from 39.8 to 74.5 min (SD: 17.2 and 25.03 respect-ively), while mean night-time haul duration was from 57.3 to 90.7 min (SD: 15.2 and 27.6 respect-ively).
Records of the beginning and the end of each trawling were used in order to determine the dura-tion of each haul. The beginning of trawling was the time at which shooting was completed and the net began to fi sh. The end of trawling was the time at which hauling stopped and the net was back on deck. To determine the vertical distribution of krill concentrations, average trawling depths, derived
using an echosounder, were recorded separately for each haul. The daylight period was determined according to the nautical dawn and dusk reference table (CCAMLR, 2001b).
All hauls completed before or up to 10 min after dawn or dusk were categorised as night or day hauls respectively.
To determine the density of krill concentra-tions, samples of krill were taken from almost every fi fth haul, or 16.8% of the total. The average krill weight in samples was used to estimate krill catch weight in each haul. Krill length measurements were taken as the total length (in mm) from the front of the eye to the tip of the telson, rounded down to the nearest millimetre. Between 123 and 187 krill specimens were measured from each sampled haul.
Pairwise comparisons of krill length between year and area were conducted using ANOVA. The level of statistical signifi cance was assumed to be 0.01.
The vertical distribution of krill concentrations was determined for each 25 m layer of the water column.
RESULTS
Distribution of Commercial Krill Concentrations in Various Fishing Areas of the Atlantic Sector
The periods of occurrence of commercial krill concentrations varied in each fi shing area and year. They fi rst started to occur in the Elephant Island area between February and April (this period varied with year), and then in the South Shetlands area (i.e. King George Island to Livingston Island) between February and June (Figure 2). The krill fi shery was signifi cantly infl uenced by weather conditions. In 1999, fi shing for krill in the South Shetlands area stopped much earlier (April) than in 1997 and 1998 (June) due to the heavy ice cover. In 1999, no commercial krill concentrations were observed in the Elephant Island area, while they were observed in the South Orkneys area. It must be emphasised that in the years immediately pre-ceding these studies, no large krill concentrations suitable for exploitation were observed in the South Orkneys area. However, in the 1980s and early 1990s krill concentrations in this area were found to be numerous and large catches were taken (CCAMLR, 2001a; Litvinov et al., 2001).
Jackowski
86
Density of Commercial Krill Concentrations
Krill concentrations were not equally distributed throughout the Atlantic sector; they were mainly located in the South Shetland, Elephant, South Orkney and South Georgia Islands areas (Figure 1). Most frequently they occurred on shelves and only in the South Georgia area did they occur in waters beyond the shelf. This is a typical distribution of krill in this area (see catch statistics in CCAMLR, 2001a).
The mean density of krill concentrations from 1997 to 1999 varied from 663 to 1 215 specimens/ 1 000 m3; these fi gures varied by area and season (Figure 3). The highest mean krill densities were found in the South Georgia area (1 215 specimens/ 1 000 m3) and the South Orkneys area (1 204 speci-mens/1 000 m3), and the lowest was in the South Shetlands area (663 specimens/1 000 m3).
The data presented here show that the density of krill concentrations varied by month (Table 1). The density of the concentrations increased as the catch season progressed from February to April in all areas and years. However, density decreased after this period. The monthly density values in-creased up to two- to three-fold (Elephant Island area – 1997, South Shetlands area – 1998), while the
maximum density of krill concentrations varied from 1 768 to 3 339 specimens/1 000 m3 and from 4 756 to 31 370 specimens/1 000 m3 in February and April respectively.
At night, krill concentrations were scattered throughout the water column and their density was several times lower than during the day (Figure 4). The most stable concentrations were observed in the Elephant Island area, while the most variable were noted in the South Shetlands area, although the distribution pattern of day and night densities was similar in all the areas. The dispersion of night concentrations differed from area to area. In February, March and April, night-time krill concentrations in relation to daytime con-centrations were less dispersed (1:1.67, 1:3.22 and 1:2.87 respectively) than in May and June (1:4.08 and 1:3.56 respectively) (Table 2).
In 1997 and 1998, krill concentrations in the Elephant Island area and the South Shetlands area were distributed in the water column from the surface to 124 m, and only in the South Georgia area were they located slightly deeper, to 149 m. In 1999, krill concentrations in the South Shetlands area were observed in much deeper waters, to 174 m, and even to 249 m in the South Orkneys area (Table 3). During the day, concentrations were usually located in deeper water layers (up
Table 1: Krill density in areas of the Southwest Atlantic sector of the Southern Ocean, from 1997 to 1999. Density is expressed as mean specimens per 1 000 m3.
Area Year Month No. ofSamples
Mean SD Min. Max.
Elephant Island 1997 February 114 378 315 22 1 768 March 133 629 833 12 7 242April 182 1 565 2 175 32 19 072
1998 February 218 972 721 11 3 339March 21 1 529 1 168 236 4 322
South Shetlands 1997 May 186 685 864 11 8 979 June
43 571 509 56 2 083
1998 March 98 1 330 1 380 11 10 541 April 112 3 902 5 249 54 31 370 May 190 1 428 1 874 15 22 585 June 139 1 092 991 62 4 404
1999 February 82 827 552 88 2 252March 186 876 811 18 4 692April 179 984 982 15 10 244
South Georgia 1997 June 82 1 215 1 765 20 15 616
South Orkneys 1999 April 20 1 598 1 232 63 4 756 May 203 1 143 1 141 12 6 659 June 170 1 231 1 396 15 11 282
87
Distribution and size of krill in Polish commercial catches, 1997–1999
Tab
le 2
: D
ay a
nd n
ight
kri
ll ab
aund
ance
(spe
cim
ens/
1 00
0 m
3 ) in
vari
ous
area
s of
the
Sout
hwes
t Atl
anti
c se
ctor
of t
he S
outh
ern
Oce
an, f
rom
199
7 to
199
9.
Are
aY
ear
Mon
thN
o. o
f D
ayN
o. o
f N
ight
Sa
mpl
esM
ean
SDM
in.
Max
.Sa
mpl
esM
ean
SDM
in.
Max
.
Ele
phan
t Isl
and
19
97Fe
brua
ry96
410
320
221
768
1721
922
616
758
Mar
ch10
175
391
412
7 24
232
240
240
441
309
Apr
il11
52
171
2 53
0 32
19 0
72
6652
543
351
1 73
4
1998
Febr
uary
180
1 12
9 69
511
3 33
9 38
227
142
1158
9M
arch
171
741
1 19
2 32
44
322
462
642
423
61
135
Sout
h Sh
etla
nds
1997
May
105
1 06
1 98
715
8 97
9 81
197
176
1189
6
June
2278
543
312
01
497
2123
396
7544
9
1998
Mar
ch66
1 66
3 1
460
9410
541
32
644
879
113
953
Apr
il60
4 67
2 5
934
402
31 3
70
523
013
4 20
9 54
20 9
13
May
922
279
2 32
9 28
22 5
85
9862
864
715
5 64
6 Ju
ne57
1 98
4 96
573
4 40
4 82
472
281
621
850
1999
Febr
uary
4788
355
888
2 25
210
420
284
149
827
Mar
ch12
21
138
843
184
692
5937
643
834
2 68
1 A
pril
100
1 31
4 1
160
1510
244
79
567
419
732
794
Sout
h G
eorg
ia
1997
June
381
953
2 35
9 20
15 6
16
4457
743
020
1 75
7
Sout
h O
rkne
ys
1999
Apr
il11
2 35
2 1
171
634
756
967
639
120
41
189
May
103
1 73
1 1
272
146
6 65
9 10
053
851
112
3 80
5 Ju
ne76
1 97
2 1
777
1511
382
93
632
425
162
213
Jackowski
88
Tab
le 3
: V
erti
cal d
istr
ibut
ion
of k
rill
abun
dan
ce (s
peci
men
s/1
000
m3 ) d
urin
g th
e d
ay in
var
ious
are
as o
f the
Sou
thw
est A
tlan
tic
sect
or o
f the
Sou
ther
n O
cean
, fro
m 1
997
to 1
999.
Are
a
Y
ear
Mon
thD
epth
(m)
>25
25–4
950
–74
75–9
910
0–12
412
5–14
915
0–17
417
5–19
920
0–22
422
5–24
9
Ele
phan
t Isl
and
19
97Fe
brua
ry36
738
260
81
049
Mar
ch43
6
73
51
012
178
0A
pril
1 51
4 2
610
1 84
8 1
335
1998
Febr
uary
889
1 17
8 1
243
1 06
8 M
arch
1 79
3 90
8
Sout
h Sh
etla
nds
1997
May
4 72
4 1
014
973
932
857
June
950
701
299
1998
Mar
ch1
638
1 80
4 A
pril
5 34
4 4
367
3 50
1 3
165
May
2 08
7 2
946
2 36
9 Ju
ne1
660
2 26
9 1
188
1 47
5
1999
Febr
uary
624
963
453
949
728
1 21
9 M
arch
822
1 03
1 1
698
1 41
7 76
4A
pril
353
1 30
5 1
394
1 44
9 1
395
798
Sout
h G
eorg
ia
1997
June
781
950
2 60
0 1
664
1 84
5 1
201
Sout
h O
rkne
ys
1999
Apr
il1
929
3 09
2 M
ay87
51
734
1 82
7 2
095
June
968
1 95
1 2
439
2 32
3 1
619
2 87
2 1
387
1 52
7
89
Distribution and size of krill in Polish commercial catches, 1997–1999
to 249 m) than at night (up to 149 m) (Table 3 and Table 4). This was particularly true in February and March, while in April, May and June night-time concentrations were located in slightly deeper waters and the range of their vertical distribution sometimes overlapped with that of the daytime concentrations. During the day the density of concentrations increased with depth, while during night-time more scattered concentrations occupied the water column from 25 to 74 m. The latter pat-tern was observed in February, March and April, and less frequently in May and June. The night-time concentrations were found in deeper waters than the daytime concentrations only in May and June 1998 in the South Shetlands area. In 1998, in the South Shetlands area where the densest con-centrations of krill were observed, density was the greatest in the 25–49 m water layer and con-centrations were more dispersed in deeper waters.
In the South Orkneys area, where the range of vertical krill distribution was the greatest at depths to 249 m, the density of krill concentrations during the day varied at different depths, while at night the greatest densities were noted for concentrations at a depth range of 75–124 m (Table 4).
Krill Size
The krill concentrations consisted of specimens 25 to 60 mm long (Figure 5). Using the ANOVA test for mean length, statistically signifi cant dif-ferences (P < 0.01) were observed with respect to both area and season. As the season progressed, the specimens observed were increasingly smaller (Figure 6, Table 5). The length distribution had a single peak, with the exception of the multi-peaked distribution in the Elephant Island area in 1997.
The size of krill caught during the day varied at all depths (Figures 7 to 9), and no correlation was found between krill size and the depth of oc-currence. An increase in mean length was some-times observed in catches taken in deeper waters, e.g. in the South Shetlands area in April and June 1998 (Figure 8). Precisely the opposite trend was observed in the South Shetlands area in March and April 1999 (Figure 9). The size of krill varied at different depths in the Elephant Island area, and also in the South Orkneys area. The lack of data from the night-time hauls for all areas and months investigated makes it impossible to determine the relationship between krill size and depth of occurrence. Some night-time hauls were examined for the South Shetlands area in May and June and of the South Orkneys area in June. A clear relationship between krill length and depth
of occurrence was observed from these data; at depths between 50 and 124 m the size of krill in-creased with water depth (Figure 10).
DISCUSSION
While considering the results of the studies, it must be kept in mind that they were derived from commercial catch data, which means that the hauls were carried out in areas where krill concentrations were optimal for krill fi shing. This refers to both horizontal and vertical location of hauls, as well as their duration. The depth range of trawling was often broad, however sometimes catches were taken in narrow depth ranges and these hauls best refl ected the real structure of krill concentrations. The trawl hauling technique also infl uenced the interpretation of the vertical structure of krill concentrations. While the nets were being hauled aboard the vessel, they continued to catch krill between the depth of the haul recorded and the surface. This obviously had an impact on the evaluation of both the size of specimens and the density of concentrations. Therefore, it seems that using the average haul values to determine the structure of krill concentrations is the most accurate method.
Horizontal Distribution
The results obtained confi rm the general pat-tern of the distribution of the densest krill concen-trations near the islands in the South Atlantic sector, such as the South Shetland, Elephant, South Orkney and South Georgia Islands (Mackintosh, 1973; Ichii, 1990; Everson and Goss, 1991). The catch distribution from 1997 to 1999, although dif-ferent from year to year, represented a certain pat-tern which had been observed in previous seasons (Ichii, 1990), i.e. krill concentrations were fi rst ob-served in the Elephant Island area, and then in the South Shetlands, South Orkneys and South Georgia areas.
The lack of catches reported in 1999 for the Elephant Island area, which until then had been an abundant area, and in 1997 and 1998 in the South Orkneys area, is surprising. This phenomenon had previously been observed in these areas and also around South Georgia (Siegel, 1988; Siegel et al., 1997; Sushin and Shulgovsky, 1999). Catch statistics for the Atlantic sector confi rm this phenomenon (CCAMLR, 2001a), and also indicate that catches in different areas are very high in some seasons, while in others they are very low. This phenomenon is probably linked to the period
Jackowski
90
Tab
le 4
: V
erti
cal
dis
trib
utio
n of
kri
ll ab
und
ance
(sp
ecim
ens/
1 00
0 m
3 ) at
nig
ht i
n va
riou
s ar
eas
of t
he S
outh
wes
t A
tlan
tic
sect
or o
f th
e So
uthe
rn
Oce
an, f
rom
199
7 to
199
9.
Are
a
Y
ear
Mon
thD
epth
(m)
>25
25–4
950
–74
75–9
910
0–12
412
5–14
915
0–17
417
5–19
920
0–22
422
5–24
9
Ele
phan
t Isl
and
19
97Fe
brua
ry84
237
Mar
ch24
6
164
Apr
il64
557
543
497
1998
Febr
uary
210
269
Mar
ch97
728
0
Sout
h Sh
etla
nds
1997
May
239
187
177
286
June
222
246
1998
M
arch
162
639
324
1A
pril
345
385
4M
ay1
108
539
484
369
June
495
466
451
756
1999
Fe
brua
ry42
0M
arch
301
602
251
Apr
il54
560
952
723
2
Sout
h G
eorg
ia
1997
June
748
414
445
Sout
h O
rkne
ys
1999
Apr
il67
6
May
537
464
150
6Ju
ne23
761
664
396
535
6
Tab
le 5
: M
onth
ly a
nd in
tera
nnua
l val
ues
of m
ean
krill
leng
th (
mm
) in
var
ious
are
as o
f th
e So
uthw
est
Atl
anti
c se
ctor
of
the
Sout
hern
Oce
an, f
rom
199
7 to
199
9.
Mon
thE
leph
ant I
slan
d
Sout
h Sh
etla
nds
Sout
h G
eorg
ia
Sout
h O
rkne
ys
19
9719
9819
9919
9719
9819
9919
9719
99
Febr
uary
49.5
141
.56
48.3
145
.39
Mar
ch
45.9
641
.86
41.4
244
.64
Apr
il42
.28
41.0
044
.08
48.3
7M
ay
42.2
440
.42
46.0
2Ju
ne
41.2
639
.98
38.3
345
.50
91
Distribution and size of krill in Polish commercial catches, 1997–1999
of decreased ice cover in these areas. In 1983, when summer arrived quickly and the pack-ice was gone by October, the density of krill concentrations increased rapidly in the Bransfi eld Strait and adjacent areas (Rakusa-Suszczewski and Lipski, 1985).
Density of Concentrations
Previous studies reported that small krill con-centrations were very dense and characterised by a diverse internal structure, both in terms of density and specimen size (Hamner et al., 1983; Watkins, 1986; Watkins et al., 1990). Larger concentrations consisted of small, high-density aggregations which were observed mainly during the day and which scattered at night (Kalinowski and Witek, 1982). The results presented in this work demonstrate signifi cant diversity in concentration density, rang-ing from 11 to 31 370 specimens/1 000 m3. The greatest density (31 370 specimens/1 000m3) was observed during one fi ve-minute haul in the South Shetlands area in April 1998. Such a dense concentration was observed only once and, as can be assumed, corresponded to an extremely small and very dense shoal. The average densities in some areas and seasons varied from 378 to 3 902 specimens/1 000 m3. Variations in concentration density refl ected a pattern that was character-istic for all areas and seasons studied: between February and April the concentration density in-creased and then decreased. This feature of the internal structure of concentrations is best refl ected by data from the Elephant Island area (1997) and South Shetlands area (1998). During this period, night-time progressively increased from about two hours in February to about 14 hours in June (Figure 11), and since decreased densities were observed in April, it must be assumed that there are other factors besides daylight which have an impact on krill density. It may be assumed that the krill concentration pattern in February–June depends on krill biological activity related to spawning, as was observed in the Elephant Island area by Loeb and Siegel (1994), however, they recorded the maximum krill density in February, while it was recorded in April in each of the three consequent years of this study.
Vertical Migration
The results obtained indicate that commercial krill concentrations most often occurred in waters at depths to about 125 m, which concurs with the results of investigations carried out from
aboard the RV Profesor Siedlecki in 1978 and 1979 (Kalinowski and Witek, 1980). However, it should not be assumed that this is the maximum range of occurrence: in 1999 commercial concen-trations were found at a depth of 175 m in the South Shetlands area and at about 250 m around the South Orkneys. It should be noted that com-mercially negligent krill concentrations may be traced much deeper. According to Gutt and Siegel (1994), sampling by scientifi c nets shows that krill aggregations may occur at depths to 480 m.
However, the range of vertical distribution in each area is different during the day and at night. In general, during the night, krill concentrations occur in the upper water layers ranging between areas from 20 to 70 m depth (Marr, 1962; Kalinowski and Witek, 1980), while during the day they occur in signifi cantly deeper layers. According to the same and other authors (e.g. Hardy and Günther, 1935; Shevtsov and Makarov, 1969; Pavlov, 1974; Mohr, 1976; Kalinowski, 1978), krill migrate to the upper water layers at night, and when the light intensity increases during the day they migrate to the lower layers. However, night concentrations sometimes occur at much higher depths than day concentrations; this contradicts the general scheme of krill distribution. This phenomenon was ob-served in the South Georgia area (Kalinowski and Witek, 1980).
The results presented in this paper confi rm the general pattern of day and night krill dis-tribution. However the observed features relate only to February–March during the studied fi shing seasons. During this period, night concentrations occurred in layers closer to the surface than day ones. However, even in March this relationship was not always clear. In April, May and June krill were found in much deeper waters at night than during the day. This was especially evident in the South Shetlands area in 1998, when the longer period of studies helped to clarify the pat-tern observed. The pattern observed was that as nights became longer, krill scattered more widely throughout the deeper layers, and the range of its vertical distribution was sometimes greater than during the day. This may indicate that food rather than light governs diurnal krill migrations (Pavlov, 1974; Fischer, 1976; Kalinowski and Witek, 1980). All these authors confi rmed that krill feed mainly at night, and environmental conditions such as dis-solved oxygen and water temperature or water mass movements determine availability of phyto-plankton.
Jackowski
92
Length of Krill
The results of our study revealed that the size of krill in concentrations varies depending on the season and area of fi shing; this concurs with observations of other authors (Jazdzewski et al., 1978; Kawaguchi et al., 1997; Makarov et al., 1970; Siegel, 1989; Siegel et al., 1990; Siegel et al., 1997; Watkins, 1986; Watkins, 1999). Observations made by Watkins (1986) regarding the lack of correlation between krill size and depth of occurrence were also confi rmed (0.01 < R2 < 0.14; 0.18 < P < 0.24).
The largest individual krill were observed in the Elephant Island and South Shetlands areas, and the smallest in the South Georgia area, confi rm-ing the results of earlier studies (Jazdzewski et al., 1978; Wolnomiejski et al., 1980; Siegel et al., 1997). Analysis of krill size structure in the South Shetlands area (Subarea 48.1) revealed statistically signifi cant differences between krill sizes (two-sample test: P < 0.01) in the Elephant Island and South Shetlands areas. In the three years analysed (1997–1999), larger krill specimens were observed in the Elephant Island area than in the South Shetlands area.
For all periods and areas the length distribution curve was unimodal, indicating the homogenous structure of krill concentrations. The only excep-tion were data from the Elephant Island area in 1997, which indicated the existence of three size groups, with peaks at 39, 45 and 51 mm. During the same season, a bimodal distribution of krill sizes was observed for the South Georgia area (37 and 40.5 mm) and a unimodal distribution (peak at 42 mm) for the South Shetlands area. This distribution (in accordance with criteria for age estimation by Martin et al. (1997) and Watkins (1999)) indicates a multi-generation struc-ture of the stocks (2+, 3+ and 4+ age groups) in the Elephant Island area. In the South Georgia area there were two age groups (2+ and 3+), and in the South Shetlands area only the 3+ age group predominated. The signifi cant number of krill from the 2+ age group refl ects good recruitment from the 1994/95 generation, which has been regarded as very abundant (Watkins, 1999).
Results of studies published to date report an increase of krill size over fi shing season (Martin et al., 1997; Siegel and Kalinowski, 1994). These authors suggest that ‘these changes are related to the drift of swarms, not to changes in krill be-haviour thought to occur during the winter post-spawning non-feeding season. It is hard to explain these changes by the impact of the fi shery on larger krill specimens’. The results presented here appear
to be the opposite to those expected: the average krill sizes in each area decreased as the season progressed and the differences were statistically signifi cant (P < 0.01). Similar observations were made in the South Orkneys area from March to June (Vagin et al., 1992).
Since the fi shing season partially overlapped with the spawning season (Siegel et al., 1997), the conclusion can be drawn that larger specimens spawn fi rst and are followed by smaller ones.
CONCLUSIONS
(i) Commercially important krill concentrations occur at the depth range to 125–250 m. The variations in depth relate to the location of krill occurrence: in the Elephant Island area the depth is up to 125 m, South Georgia area – 150 m, South Shetlands area – 175 m and the South Orkneys area – 250 m.
(ii) Daily krill migrations may vary according to area, however they mainly depend on the length of day and night. In February (short night), night concentrations come close to the surface and as the season progresses and nights lengthen they move in deeper waters. In April, May and June, they do not migrate to the upper layers, but remain scattered at the same depths, or even deeper, than the day concentrations.
(iii) The density of night concentrations of krill is several times lower than the density of day concentrations.
(iv) The average density of krill concentrations increases between February and April–May and then decreases, which is probably re-lated to krill reproductive activity.
(v) The krill sizes varied depending on area and season. The largest krill specimens were found in the Elephant Island area and the smallest in the South Georgia area.
(vi) No relationship was found between krill size and its vertical distribution.
REFERENCES
CCAMLR. 2001a. Statistical Bulletin, Vol. 13 (1991–2000). CCAMLR, Hobart, Australia: 153 pp.
93
Distribution and size of krill in Polish commercial catches, 1997–1999
CCAMLR. 2001b. Nautical dawn and dusk refer-ence table. In: CCAMLR Scheme of International Scientifi c Observation: Scientifi c Observers Man-ual, Part IV, Section 4. CCAMLR, Hobart, Australia.
Everson, I. and C. Goss. 1991. Krill fi shing activity in the southwest Atlantic. Ant. Sci., 3 (4): 351–358.
Fischer, W. 1976. Tagesperiodische Wanderun-gen des Antarktischen Krill. Inf. Fischwirtsch., Hamburg, 3: 90–92.
Gutt, J. and V. Siegel. 1994. Benthopelagic aggregations of krill (Euphausia superba) on the deeper shelf of the Weddell Sea (Antarctica). Deep-Sea Res., 41: 169–178.
Hamner, W.M., P.P. Hamner, S.W. Strand and R.W. Gilmer. 1983. Behaviour of Antarctic krill, Euphausia superba: chemoreception, feeding, schooling and moulting. Science, 220: 433–435.
Hardy, A.C. and E.R. Günther. 1935. The plankton of the South Georgia whaling grounds and adjacent waters, 1926–1927. Discovery Rep., 11: 1–456.
Ichii, T. 1990. Distribution of Antarctic krill con-centrations exploited by Japanese krill trawlers and minke whales. NIPR Symposium on Polar Biology, 3: 36–56.
Jazdzewski, K., J. Dzik, J. Porebski, S. Rakusa-Suszczewski, Z. Witek and N. Wolnomiejski. 1978. Biological and populational studies on krill near South Shetlands, Scotia Sea and South Georgia in the summer 1976. Pol. Arch. Hydrobiol., 25 (3): 607–631.
Kalinowski, J. 1978. Vertical migration of krill in the region of South Georgia, February–March 1976. Pol. Arch. Hydrobiol., 25 (3): 573–583.
Kalinowski, J. and Z. Witek. 1980. Diurnal vertical distribution of krill aggregations in the Western Atlantic. Pol. Polar Res., 1 (4): 127–146.
Kalinowski, J. and Z. Witek. 1982. Forms of Antarctic krill aggregations. ICES Biological Oceanography Committee. Mimeo CM L:60: 8 pp.
Kalinowski, J. and Z. Witek. 1985a. Elementy biologii i formy grupowego wystepowania kryli. Studia i Materialy, Seria B, 52: 162 pp. (in Polish).
Kalinowski, J. and Z. Witek. 1985b. Scheme for classifying aggregations of Antarctic krill. BIOMASS Handbook, 27: 9 pp.
Kawaguchi, S., T. Ichii and M. Naganobu. 1997. Catch per unit effort and proportional recruitment indices from Japanese krill fi shery data in Subarea 48.1. CCAMLR Science, 4: 47–63.
Litvinov, F.F., V.A. Sushin, G.A. Chernega and O.A. Berezhinskiy. 2001. Soviet krill fi shery in 1977–1992, Part 1. Distribution, fi shing ef-fort interannual situation patterns. Document WG-EMM-01/57. CCAMLR, Hobart, Australia.
Loeb, V. and V. Siegel. 1994. Status of the krill stock around Elephant Island in 1991/92 and 1992/93. CCAMLR Science, 1: 7–33.
Macaulay, M.C., T.S. English and O.A. Mathisen. 1984. Acoustic characterisation of Antarctic krill (Euphausia superba) from Elephant Island and Bransfi eld Strait. J. Crust. Biol., 4 (Spec. No. 1): 16–44.
Mackintosh, N.A. 1973. Distribution of post-larvae krill in the Antarctic. Discovery Rep., 36: 1–94.
Makarov, R.R., A.G. Naumov and V.V. Shevtsov. 1970. The biology and distribution of the An-tarctic krill. In: Holdgate, M.W. (Ed.). Antarctic Ecology, Vol. 1. Academic Press, London and New York: 173–176.
Marr, J.W.S. 1962. The natural history and geo-graphy of the Antarctic krill (Euphausia superba Dana). Discovery Rep., 32: 33–464.
Martin, J., R. Hewitt and R. Holt. 1997. The US Antarctic Marine Living Resources (AMLR) program: 1996–1997 fi eld season activities. US Antarctic Journ., 32 (5).
Mohr, M. 1976. Tageszeitlich bedingte rhytmik im verhalten von halbwuchsigen krill (Euphau-sia superba). Inf. Fischwirtsch. Hamburg, 4/5: 132–134.
Pavlov, V. 1974. O kharaktere svyazi mezhdu pitaniem i niekotorymi osobennostyami pove-deniya Euphausia superba Dana. Trudy VNIRO, 99: 104–116.
Rakusa-Suszczewski, S. and M. Lipski. 1985. Report on the RV Profesor Siedlecki expedition during the BIOMASS-SIBEX in 1983/1984. Pol. Polar Res., 6 (1/2): 7–19.
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Shevtsov, V.V. and R.R. Makarov. 1969. K biologii antarkticheskogo krilya. Trudy VNIRO, 66: 177–206.
Siegel, V. 1988. A concept of seasonal variation of krill (Euphausia superba) distribution and abundance west of the Antarctic Peninsula. In: Sahrhage, D. (Ed.). Antarctic Ocean and Resources Variability. Springer-Verlag, Berlin Heidelberg: 219–230.
Siegel, V. 1989. Winter and spring distribution and status of the krill stock in Antarctic Peninsula waters. Arch. FischWiss., 39: 45–72
Siegel, V. and J. Kalinowski. 1994. Krill demog-raphy and small-scale processes: a review. In: El-Sayed, S.Z. (Ed.). Southern Ocean Ecology: the BIOMASS Perspective. Cambridge University Press: 145–163.
Siegel, V., B. Bergström, J.O. Strömberg and P.H. Schalk. 1990. Distribution, size frequencies and maturity stages of krill, Euphausia superba, in relation to sea-ice in the northern Weddell Sea. Polar Biol., 15: 161–174.
Siegel, V., W. de la Mare and V. Loeb. 1997. Long-term monitoring of krill recruitment and abundance indices in the Elephant Island area (Antarctic Peninsula). CCAMLR Science, 4: 19–35.
Sushin, V.A. and K.E. Shulgovsky. 1999. Krill distribution in the western Atlantic sector of the Southern Ocean during 1983/84, 1984/85 and 1987/88 based on the results of Soviet mesoscale surveys conducted using an Isaacs-Kidd midwater trawl. CCAMLR Science, 6: 59–70.
Vagin, A.V., R.R. Makarov and L.L. Meshenina. 1992. Diurnal variations in biological charac-teristics of krill, Euphausia superba Dana, to the west of the South Orkney Islands, 24 March to 18 June 1990 – based on data reported by a bioligist–observer. In: Selected Scientifi c Papers, 1992 (SC-CAMLR-SSP/9). CCAMLR, Hobart, Australia: 201–222.
Watkins, J.L. 1986. Variations in the size of An-tarctic krill Euphausia superba Dana, in small swarms. Mar. Ecol. Prog. Ser., 31: 67–73.
Watkins, J.L. 1999. A composite recruitment in-dex to describe interannual changes in the population structure of Antarctic krill at South Georgia. CCAMLR Science, 6: 71–84.
Watkins, J.L., D.J. Morris, C. Ricketts and A.W.A. Murray. 1990. Sampling biological characteristics of krill: effect of heterogeneous nature of swarms. Mar. Biol., 107 (3): 409–415.
Witek, Z., J. Kalinowski, A. Grelowski and N. Wolnomiejski. 1981. Studies of aggregations of krill (Euphausia superba). Meeresforschung, 28: 228–243.
Wolnomiejski, N., Z.Witek and H. Czykieta. 1980. Metody i kryteria biologicznej oceny przemyslowych skupien kryla antarktycznego. (Methods and biological criteria for com-mercial krill aggregation assessment). In: Rozmieszczenie i charakterystyka skupien kryla w rejonie Polwyspu Antarktycznego w sezonie letnim 1997 r. Studia i Materialy, Seria A, 25. Sea Fisheries Institute, Gdynia: 27–63 (in Polish).
95
Distribution and size of krill in Polish commercial catches, 1997–1999
Figure 1: Areas of the Polish krill fi shery where data were collected from 1997 to 1999.
60°W 50°W 40°W
55°S
60°S
Figure 2: Periods of Polish commercial krill fi shing in various areas of the Southwest Atlantic sector of the Southern Ocean, from 1997 to 1999.
Elephant
South Shetlands
South Orkneys
South Georgia
Jan Feb Mar Apr May Jun
1997 1998 1999
Jackowski
96
Figure 3: Mean krill density in various areas of the Southwest Atlantic sector of the Southern Ocean, from 1997 to 1999.
0
400
800
1200
1600
Elephant 1997 Elephant 1998 South Shetland1997
South Shetland1998
South Shetland1999
South Georgia1997
South Orkney1999
Den
sity
(spe
cim
ens/
1 00
0 m
3 )
Elephant Elephant Sth Shetlands Sth Shetlands Sth Shetlands Sth Georgia Sth Orkneys 1997 1998 1997 1998 1999 1997 1999
Figure 4: Mean krill density during the day and night in various areas of the Southwest Atlantic sector of the Southern Ocean, from 1997 to 1999.
0
500
1000
1500
2000
2500
3000
Elephant 1997 Elephant 1998 South Shetland1997
South Shetland1998
South Shetland1999
South Georgia1997
South Orkney1999
Den
sity
(spe
cim
ens/
1 00
0 m
3 )
Day
Night
Elephant Elephant Sth Shetlands Sth Shetlands Sth Shetlands Sth Georgia Sth Orkneys 1997 1998 1997 1998 1999 1997 1999
97
Distribution and size of krill in Polish commercial catches, 1997–1999
Figure 5: Krill length-frequency distributions in Polish commercial catches taken in the areas of Elephant, South Shetland, South Georgia and South Orkney Islands, from 1997 to 1999.
1997
0
5
10
15
25 30 35 40 45 50 55 60
Freq
uenc
y (%
)
Elephant South Shetland South Georgia
1998
0
5
10
15
25 30 35 40 45 50 55 60
Freq
uenc
y (%
)
Elephant South Shetland
1999
0
5
10
15
20
25 30 35 40 45 50 55 60
Length (mm)
Freq
uenc
y (%
)
Elephant South Shetland South Orkney
Jackowski
98
Figu
re 6
: M
onth
ly k
rill
leng
th-f
requ
ency
dis
trib
utio
ns fr
om P
olis
h co
mm
erci
al c
atch
es ta
ken
in th
e va
riou
s ar
eas
of th
e So
uthw
est A
tlan
tic
sect
or o
f the
So
uthe
rn O
cean
, fro
m 1
997
to 1
999.
0481216
2530
3540
4550
5560
Frequency (%)
May
June
Sout
h Sh
etla
nds,
199
7
0481216
2530
3540
4550
5560
Frequency (%)
Mar
chAp
rilM
ayJu
ne
048121620
2530
3540
4550
5560
Leng
th (m
m)
Frequency (%)
Febr
uary
Mar
chAp
ril
Sout
h Sh
etla
nds,
199
8
0481216
2530
3540
4550
5560
Frequency (%)
Febr
uary
Mar
chAp
ril
0481216
2530
3540
4550
5560
Frequency (%)
Febr
uary
Mar
ch
0481216
2530
3540
4550
5560
Leng
th (m
m)
Frequency (%)
April
May
June
Sout
h O
rkne
ys, 1
999
Elep
hant
, 199
7
Sout
h Sh
etla
nds,
199
9
Elep
hant
, 199
8
99
Distribution and size of krill in Polish commercial catches, 1997–1999
Figure 7: Mean length of krill caught in 1997 during the day by depth strata in: the Elephant Island area in (a) February, (b) March, and (c) April; (d) the South Shetlands area in May; and (e) the South Georgia area in June.
42
44
46
48
50
52
40
44
48
52
40
41
42
43
44
40
41
42
43
44
35
37
39
41
43
25-49 50-74 75-99 100-124 125-149 150-174 175-199
Depth (m)
Leng
th (m
m)
(a)
(b)
(c)
(d)
(e)
6/742
12/1513
7/914 6/791
3/369
4/602
3/365
2/274
5/623 6/741
5/615
6/629 6/631
6/616
3/370
4/489 5/6073/365
2/254 2/261
(a)
(e)
(d)
(c)
(b)
Jackowski
100
Figure 8: Mean length of krill caught in 1998 during the day by depth strata in: (a) the Elephant Island area in February; and the South Shetlands area in (b) March, (c) April, (d) May and (e) June.
40.0
41.0
42.0
43.0
44.0
[ mm
]
30.0
34.0
38.0
42.0
[ mm
]
40.0
41.0
42.0
43.0
[ mm
]
39.5
40.0
40.5
41.0
[ mm
]
39.5
40.0
40.5
25-49 50-74 75-99 100-124 125-149 150-174 175-199Depth [m]
[ mm
]
A
B
C
D
E
5/62511/1315 9/1194
6/792
5/636
7/843
6/741 6/739
5/628
11/13816/2051
6/776
12/1617
Leng
th (m
m)
44.0
43.0
42.0
41.0
40.5
40.0
39.5
41.0
40.5
40.0
43.0
42.0
41.0
42.0
38.0
34.0
30.0
5/625
11/1315 9/11946/792
5/636
7/843
6/7416/739
5/628
11/138
16/2051
12/1617
6/776
25-49 50-74 75-99 100-124 125-149 150-174 175-199
Depth (m)
(a)
(e)
(d)
(c)
(b)
101
Distribution and size of krill in Polish commercial catches, 1997–1999
Figure 9: Mean length of krill caught in 1999 during the day by depth strata in: the South Shetlands area in (a) February, (b) March, (c) April; and the South Orkneys area in (d) May and (e) June.
44
45
46
[ mm
]
42
44
46
[ mm
]
40
42
44
46
[ mm
]
45464748
[ mm
]
44
45
46
47
48
25-49 50-74 75-99 100-124 125-149 150-174 175-199
Depth [m]
[ mm
]
(a)
B
C
D
E
6/605
5/597
4/496
5/6176/746
5/599 3/3793/380
4/496
3/371
4/4903/369
4/486 4/492
5/6156/738 6/742
5/598
4/492
4/487
5/6186/736
5/605
4/477
46
45
46
44
46
44
42
48
47
46
45
48
47
46
45
44 25-49 50-74 75-99 100-124 125-149 150-174 175-199
Depth (m)
6/605
4/496
3/3803/3795/5996/746
5/617
4/496
5/597
3/3714/4924/486
3/3694/490
5/6156/738 6/742
5/598
6/7365/618
4/487
4/492
4/477
Leng
th (m
m)
5/605
(b)
(a)
(d)
(e)
(c)
Jackowski
102
Figure 11: Mean krill density relative to the duration of daylight.
0
1000
2000
3000
4000
5000
Elephant 1997 Elephant 1998 South Shetland1997
South Shetland1998
South Shetland1999
South Orkney1999
Den
sity
(spe
cim
ens/
1 00
0 m
3 )
25121314
Hour
Elephant Elephant Sth Shetlands Sth Shetlands Sth Shetlands Sth Orkneys 1997 1998 1997 1998 1999 1999
Figure 10: Mean length of krill caught in 1999 at night by depth strata in: the South Shetlands area in (a) May and (b) June; and (c) the South Orkneys area in June.
39
40
41
42[ m
m ]
3939404041
[ mm
]
4344454647
>24 25-49 50-74 75-99 100-124 125-149 150-174 175-199Depth [m]
[ mm
]A
B
C
2/261
3/3822/270
2/2532/249
3/383
4/4924/483
4/473
>24 25-49 50-74 75-99 100-124 125-149 150-174 175-199
Depth (m)
42
41
40
2/261
3/3822/270
Leng
th (m
m)
47
46
45
44
43
40.5
40.0
39.5
39.0
2/2492/253
3/383
4/492
4/483
4/473
(a)
(c)
(b)
103
Distribution and size of krill in Polish commercial catches, 1997–1999
Liste des tableaux
Tableau 1: Densité du krill dans des régions du secteur atlantique du sud-ouest de l’océan Austral, de 1997 à 1999. La densité est exprimée en nombres moyens par 1 000 m3.
Tableau 2: Abondance du krill le jour et la nuit (spécimens/1 000 m3) dans diverses régions du secteur atlantique du sud-ouest de l’océan Austral, de 1997 à 1999.
Tableau 3: Distribution verticale de l’abondance du krill (spécimens/1 000 m3) le jour dans diverses régions du secteur atlantique du sud-ouest de l’océan Austral, de 1997 à 1999.
Tableau 4: Distribution verticale de l’abondance du krill (spécimens/1 000 m3) la nuit dans diverses régions du secteur atlantique du sud-ouest de l’océan Austral, de 1997 à 1999.
Tableau 5: Valeurs mensuelles et interannuelles de la longueur moyenne du krill (mm) dans diverses régions du secteur atlantique du sud-ouest de l’océan Austral, de 1997 à 1999.
Liste des fi gures
Figure 1: Secteurs de la pêcherie polonaise de krill où les données ont été collectées de 1997 à 1999.
Figure 2: Périodes de la pêche commerciale au krill menée par la Pologne dans diverses zones du secteur atlantique du sud-ouest de l’océan Austral, de 1997 à 1999.
Figure 3: Densité moyenne du krill dans diverses zones du secteur atlantique du sud-ouest de l’océan Austral, de 1997 à 1999.
Figure 4: Densité moyenne du krill le jour et la nuit dans diverses zones du secteur atlantique du sud-ouest de l’océan Austral, de 1997 à 1999.
Figure 5: Distributions des fréquences de longueurs de krill dans les captures commerciales effectuées par la Pologne dans les secteurs des îles Éléphant, Shetland du Sud, de la Géorgie du Sud et des Orcades du Sud de 1997 à 1999.
Figure 6: Distributions mensuelles des fréquences des longueurs de krill dans les captures commerciales effectuées par la Pologne dans les diverses zones du secteur atlantique du sud-ouest de l’océan Austral, de 1997 à 1999.
Figure 7: Longueur moyenne du krill capturé en 1997 de jour par strate de profondeur dans les secteurs de l’île Éléphant en (a) février, (b) mars, et (c) avril, (d) des îles Shetland du Sud en mai et (e) de la Géorgie du Sud en juin.
Figure 8: Longueur moyenne du krill capturé en 1998 de jour par strate de profondeur dans les secteurs de (a) l’île Éléphant en février et des îles Shetland du Sud en (b) mars, (c) avril, (d) mai et (e) juin.
Figure 9: Longueur moyenne du krill capturé en 1999 de jour par strate de profondeur dans les secteurs des îles Shetland du Sud en (a) février, (b) mars, (c) avril et des Orcades du Sud en (d) mai et (e) juin.
Figure 10: Longueur moyenne du krill capturé en 1999 la nuit par strate de profondeur dans les secteurs des îles Shetland du Sud en (a) mai et (b) juin et (c) des Orcades du Sud en juin.
Figure 11: Densité moyenne du krill en fonction de la durée du jour.
Список таблиц
Табл. 1: Плотность криля в различных районах юго-западной части атлантического сектора Южного океана, 1997–1999 гг. Плотность выражена как средняя численность на 1000 м3.
Табл. 2: Численность криля днем и ночью (особи/1000 м3) в различных районах юго-западной части атлантического сектора Южного океана, 1997–1999 гг.
Jackowski
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Табл. 3: Вертикальное распределение численности криля (особи/1000 м3) днем в различных районах юго-западной части атлантического сектора Южного океана, 1997–1999 гг.
Табл. 4: Вертикальное распределение численности криля (особи/1000 м3) ночью в различных районах юго-западной части атлантического сектора Южного океана, 1997–1999 гг.
Табл. 5: Ежемесячные и межгодовые значения средней длины криля (мм) в различных районах юго-западной части атлантического сектора Южного океана, 1997–1999 гг.
Список рисунков
Рис. 1: Районы сбора данных по польскому промыслу криля, 1997–1999 гг.
Рис. 2: Периоды ведения Польшей коммерческого промысла криля в различных районах юго-западной части атлантического сектора Южного океана, 1997–1999 гг.
Рис. 3: Средняя плотность криля в различных районах юго-западной части атлантического сектора Южного океана, 1997–1999 гг.
Рис. 4: Средняя плотность криля днем и ночью в различных районах юго-западной части атлантического сектора Южного океана, 1997–1999 гг.
Рис. 5: Частотное распределение длин криля в польских коммерческих уловах, полученных в районах о-ва Элефант, Южных Шетландских и Южных Оркнейских о-вов и Южной Георгии в 1997–1999 гг.
Рис. 6: Частотное распределение длин криля по месяцам в польских коммерческих уловах, полученных в различных районах юго-западной части атлантического сектора Южного океана в 1997–1999 гг.
Рис. 7: Средняя длина криля, выловленного в 1997 г. днем, по горизонтам глубин в районе о-ва Элефант в (a) феврале, (b) марте, и (c) апреле; в районах (d) Южных Шетландских о-вов в мае; и (e) Южной Георгии в июне.
Рис. 8: Средняя длина криля, выловленного в 1998 г. днем, по горизонтам глубин в районе (a) о-ва Элефант в феврале, и у Южных Шетландских о-вов в (b) марте, (c) апреле, (d) мае и (e) июне.
Рис. 9: Средняя длина криля, выловленного в 1999 г. днем, по горизонтам глубин в районах: Южных Шетландских о-вов в (a) феврале, (b) марте, (c) апреле; и Южных Оркнейских о-вов в (d) мае и (e) июне.
Рис. 10: Средняя длина криля, выловленного в 1999 г. ночью, по горизонтам глубин в районах: Южных Шетландских о-вов в (a) мае (b) июне, и (c) Южных Оркнейских о-вов в июне.
Рис. 11: Средняя плотность криля относительно продолжительности дневного освещения.
Lista de las tablas
Tabla 1: Densidad de kril en zonas del sector atlántico suroccidental del Océano Austral, de 1997 a 1999. El valor de densidad se expresa en un promedio por 1 000 m3.
Tabla 2: Abundancia diurna y nocturna de kril (número/1 000 m3) en diversas zonas del sector del atlántico suroccidental del Océano Austral, de 1997 a 1999.
Tabla 3: Distribución vertical de la abundancia de kril (número/1 000 m3) durante el día en diversas zonas del sector atlántico suroccidental del Océano Austral, de 1997 a 1999.
Tabla 4: Distribución vertical de la abundancia de kril (número/1 000 m3) durante la noche en diversas zonas del sector atlántico suroccidental del Océano Austral, de 1997 a 1999.
Tabla 5: Promedios mensuales e interanuales de la talla de kril (mm) en diversas zonas del sector atlántico suroccidental del Océano Austral, de 1997 a 1999.
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Distribution and size of krill in Polish commercial catches, 1997–1999
Lista de las fi guras
Figura 1: Zonas donde operó la pesquería comercial polaca de kril de donde se recopilaron datos de 1997 a 1999.
Figura 2: Períodos cuando operó la fl ota de pesca comercial polaca de kril en diversas zonas del sector atlántico suroccidental del Océano Austral, de 1997 a 1999.
Figura 3: Densidad promedio de kril en diversas zonas del sector atlántico suroccidental del Océano Austral, de 1997 a 1999.
Figura 4: Densidad promedio de kril en el día y en la noche en diversas zonas del sector atlántico suroccidental del Océano Austral, de 1997 a 1999.
Figura 5: Distribuciones de la frecuencia de tallas de kril en las capturas comerciales polacas realizadas en las islas Elefante, Shetland del Sur, Georgia del Sur y Orcadas del Sur de 1997 a 1999.
Figura 6: Distribuciones mensuales de la frecuencia de tallas de kril en las capturas comerciales polacas en diversas zonas del sector atlántico suroccidental del Océano Austral, de 1997 a 1999.
Figura 7: Talla promedio del kril capturado en 1997 durante el día por intervalo de profundidad en: la zona de la isla Elefante en (a) febrero, (b) marzo, y (c) abril; (d) en la zona de las Shetland del Sur en mayo; y (e) en la zona de Georgia del Sur en junio.
Figura 8: Talla promedio del kril capturado en 1998 durante el día por intervalo de profundidad en: (a) la zona de la isla Elefante en febrero; y en la zona de las Shetland del Sur en (b) marzo, (c) abril, (d) mayo y (e) junio.
Figura 9: Talla promedio del kril capturado en 1999 durante el día por intervalo de profundidad en: la zona de las Shetland del Sur en (a) febrero, (b) marzo, (c) abril; y en la zona de las Orcadas del Sur en (d) mayo y (e) junio.
Figura 10: Talla promedio del kril capturado en 1999 durante la noche por intervalo de profundidad en: la zona de las Shetland del Sur en (a) mayo y (b) junio; y (c) en la zona de las Orcadas del Sur en junio.
Figura 11: Densidad promedio del kril en función de las horas de luz diurna.