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INTERNATIONAL COUNCIL FOR CM 2001/ J:44
THE EXPLORATION OF THE SEA Living Resources. Session J
AGE AND GROWTH OF NORTHEAST ATLANTIC MACKEREL
(SCOMBER SCOMBRUS) IN WATERS OF THE NORTH AND
NORTHWEST OF SPAIN (ICES DIVISIONS VIIIC AND IXA NORTH),
1990-2000 By
Begoña Villamor1, Pablo Abaunza1 and Celso Fariña2
1 Instituto Español de Oceanografía. P.O. 240. 39080 Santander. Spain 2 Instituto Español de Oceanografía. P.O. 130. 15080 A Coruña. Spain
e.mail:[email protected]; [email protected]; [email protected]
ABSTRACT
This paper analyses the growth of Northeast Atlantic mackerel (Scomber scombrus
Linnaeus, 1758) in waters of the North and Northwest of Spain (ICES Divisions VIIIc and
IXa North), in the period 1990-2000.
Age was determined by means of the interpretation and counting of growth rings on the
otoliths (sagitta) of 7732 individuals caught during the spawning season by the commercial
fleet and on fisheries research surveys.
Length distributions by age group were compared by applying non-parametric tests
(Kruskal-Wallis and Kolgomorov-Smirnov). Significant differences were found (p<0.05)
among the years analysed, with high variability to age 7.
The parameters of the von Bertalanffy growth curve were estimated for the whole period
studied (Linf= 44.3 cm, k= 0.228 years -1, t0= -2.70 years) and for each year. The results
obtained were compared with those of other mackerel growth studies in different areas of
the Northeast Atlantic.
INTRODUCTION
Northeast Atlantic mackerel (Scomber scombrus Linnaeus, 1758) is a highly abundant
pelagic species. It supports fisheries of great importance to several European countries, with
annual mean landings of 660,000 t from 1988-1999 (ICES, 2001).
For the purposes of assessment Northeast Atlantic mackerel was, until 1995, considered to
belong to three different stocks, the North Sea stock, the Western stock and the Southern
stock. As a result of tag-recovery surveys carried out in 1994 (Uriarte, 1995; Uriarte and
Lucio, 2001), the term Northeast Atlantic mackerel is now applied in the area which extends
from the south of the Iberian Peninsula (ICES Division IXa) to the north of Norway
(Division IIa), including the North Sea and Skagerrak (Division IIIa) (Fig. 1). It is now
considered to be a single stock divided into three components: the Western component,
made up of individuals that spawn in Western European waters (ICES Areas VI, VII and
VIIIabde), the Southern component, which includes individuals spawning in Southern
European waters (VIIIc and IXa) and the North Sea component, those whose spawning areas
are in the North Sea and Skagerrak (IIIa and IV) (ICES, 1996; 2000).
Mackerel is a migratory species. The pattern of migration in the Northeast Atlantic is well
documented by ichthyoplanktonic surveys (ICES, 1990; ICES, 1999b; Reid, 2001), spatial
and temporal distribution of the fishery (Walsh, 1994; Walsh and Martin, 1986; Lockwood,
1988; Villamor et al., 1994; 1997) and tag-recovery experiments (Walsh, 1981; Rankine and
Walsh, 1982; Bakken and Westgard, 1986; Iversen and Skagen, 1989; Uriarte, 1995; Uriarte
et al., 1999; Uriarte and Lucio, 2001). From these, it was determined that after spawning,
adults of the Southern and Western components migrate to the Norwegian Sea and North
Sea to feed during the second half of each year, returning to the spawning areas at the
beginning of the following year.
Several fleets and gears exploit the mackerel fishery in Southern European waters: handline,
purse seine, trawl and gillnet. This fishery is seasonal. In the first half of the year handline
targets mackerel and lands the bulk of catches from Division VIIIc, consisting of adult fish.
In the second half of the year, catches consist of juveniles coming mainly from Division IXa
(Villamor et al., 1997). Catches have increased in recent years, and in 1998 and 1999
reached a maximum of 44.000 t, 38.000 t of which were in Division VIIIc (ICES, 2001).
Due to its economic importance, the biology of the Northeast Atlantic mackerel is well
studied. Studies of growth are many: the growth of North Sea and Skagerrak mackerel was
studied by Aker (1961), Castelló and Hamre (1969), Kändler (1957), Nedelec (1960),
Postuma (1972) and Skagen (1989), that of Western mackerel by Bolster (1974), Corten and
Van de Kamp (1978), Eltink and Gerritsen (1982), Kästner (1977), Lockwood and Johnson
(1976), Molloy (1964), Skagen (1989) and Steven (1952), and that of the South by Cort
(1982), Cort et al. (1986), De la Hoz and Villegas (1987), Gordo et al. (1982), Gordo and
Martins (1984), Lucio (1997) and Martins (1998). Nevertheless, none of the above carried
out a comparative analysis of growth taking the year factor into account.
The aim of this paper is to examine the growth pattern of Southern component mackerel and
its interannual variability taking into account a wider geographical area and a greater
number of years than the studies previously cited for this component. The growth
parameters obtained are compared with those referred to for other areas of the Northeast
Atlantic.
MATERIAL AND METHODS
Sampling and ageing
During the period 1990 to 2000 biological sampling was carried out on 7732 mackerel
individuals obtained from commercial catches and annual acoustic and bottom trawl surveys
in the N and NW of Spain (Divisions VIIIc and IXa North). Due to the seasonality of the
fishery, samplings were mainly performed in the first half of each year. Most mackerel
samples were analysed fresh.
Fish were measured (total length to the lower cm), weighed (wet weight, g), and their sex
was determined by macroscopic examination of the gonads. Sagitta otolith pairs were
removed for age assignation.
Age was determined by the interpretation and counting of growth rings on otoliths (sagittae).
For the preparation and examination of otoliths, the procedures and criteria described in
Anon. (1987) and ICES (1995) were followed. Whole otoliths were mounted on a blackened
background, covered with resin (Eukit), and illuminated by reflected light. A binocular
microscope was used to observe the banding pattern (20x or 40x magnifications, depending
on otolith size).
The following were assumed in determining age: 1) the date of birth was considered to be 1
January, and 2) each year a translucent and an opaque growth band are deposited on the
otolith. The translucent rings were counted, preferably the anterior part (rostrum) and
posterior part (post-rostrum) of the otolith. When different ages were recorded in the two
areas of the otolith, the greater age was considered, since this is more consistent with the
history of the fish (Anon., 1987; ICES, 1995).
Data analysis
With the results of otolith readings, an annual length-age key was elaborated (ALK, 1990-
2000) and a synoptic ALK for the period studied. Ages up to 14 years were considered, and
those which were greater were accumulated in one group (15+). To estimate the annual
growth rate and explore differences in the growth pattern between males and females in the
period of study, mean weight, mean length and standard deviation were calculated by age
class for each year and sexes combined, and the mean length by age class and sex for the
whole period.
Length distributions at age were compared between years by using non-parametric tests of
Kruskal-Wallis and Kolmogorov-Smirnov, and between sexes and the whole period by
using Kolmogorov-Smirnov test, since conditions for ANOVA were not fulfilled. The
analysis of length distributions at age is one of the best methods to compare growth studies
(Zivkov et al., 1999). In these studies it is common to find the application of non-parametric
tests (Overholthz, 1989; Landa and Piñeiro, 2000). For the comparison between years, firstly
the Kruskall-Wallis test was applied to the length distributions by age groups for all years.
When significant differences were found in certain age groups, the Kolmogorov-Smirnov
test was applied by pairs of years to find the years in which the differences were found
(Sprent, 1993; Heath, 1995).
The mean lengths by age class were fitted to the von Bertalanffy equation, Lt = L∞ [1-exp(-
k(t-t0))], for the estimate of the growth curves. Von Bertalanffy growth curve parameters
were determined by Marquardt non-linear iterative least-squares regression analysis using
SPSS 9.0. Growth parameters were calculated for sexes combined and each year 1990-2000,
and for individual sexes and set period. Index of length growth performance φ’ was
calculated by the equation φ’ = 2 log Linf + log k (Munro and Pauly, 1983) to compare
growth among years and between sexes. To compare growth among areas, the index φ’ was
estimated from growth parameters reported by other authors.
RESULTS
The Northeast Atlantic mackerel otolith sagittae has a pattern of wide opaque bands
alternating with thin translucent bands, and the first opaque bands are notably wider. In
total, 7732 whole otoliths were examined (3596 males, 3850 females and 286
undetermined). Fish ranged in size from 20 to 48 cm, and the oldest fish aged were 18 years.
Mean length by age group in each year (1990-2000) estimated from data pooled (Table 1)
indicated that the growth rate was high in the first two years of the life of the fish before
slowing down in the third. From the fourth year of age a significant inhibition in growth was
observed. There were slight differences in the mean length and mean weight by age class
among years, although no trends were observed throughout the period studied (Table1, Fig.
2).
Length distributions by age group presented interannual variability (Kruskal-Wallis,
p<0.001 in age groups 1 to 7; p<0.01 in age groups 8 to 10. Kolgomorov-Smirnov between
pairs of years, p<0.05 in 33% of cases up to age 7, p<0.05 in 5 % of cases in ages 8 to 10,
Table 2).
Mean length by age group from data pooled for the years 1990-2000 differed slightly
between the sexes (Table 3). Females were greater than males (except in the 15+ group)
with differences ranging from 0.1-1.2 cm. There were significant differences between sexes
in some length distributions at age (Kolgomorov-Smirnov, p<0.05, ages 4 to 7, 9 and 11,
Table 2).
The von Bertalanffy equations fitted well to the data observed (R2≥0.97 in all cases, Table 4,
Figure 3). The growth parameters of the von Bertalanffy model estimated for the sexes
combined and the whole period were Linf = 44.3 cm, k = 0.228 year –1 y t0 = -2.70 year. L∞
(44.3) was slightly higher than the mean length of the oldest individuals (15+ group = 43.8
cm). In the time series, the lowest values of Linf (43.1 cm) and the highest of k (0.277 year-
1) came in 1999, and the highest Linf (46.0 cm) in 1991, corresponding to a relatively low
value of k (0.164).
The parameters estimated for the data set for 1990-2000 were Linf = 44.0 cm, k = 0.226
year –1 and t0 = -2.78 year for males and Linf = 44.4 cm, k = 0.232 year –1 and t0 = -2.63 year
for females (Table 4). The respective growth curves are shown in Figure 4.
The index φ’ for sexes combined ranged from 2.42 to 2.71 during 1990-2000. The index
was very similar between males and females (2.63 and 2.65 respectively) (Figure 5).
DISCUSSION
The first studies of Northeast Atlantic mackerel age determination were controversial for
ages over 5 years. Steven (1952) stated that 25% of age readings using otoliths
corresponding to fish of more than 6 years were not reliable. For Postuma (1972) age
determination in fish of up to 5 years was reliable, while in older fish it was not. For Hamre
(1978) age determination was only reliable up to 7 years. Later, with the aim of unifying
mackerel age determination criteria several international otolith exchanges and workshops
were held (Dawson, 1986; Anon., 1987; Villamor and Meixide, 1995), but the difficulties in
defining the growth pattern of older fish were not solved. In 1995 (ICES, 1995) growth to
age 8 was validated for the first time, reading otoliths of fish of known age obtained from
Norwegian tag-recovery experiments. In this workshop the oldest ages could not be
validated by this method and the modal age of the ages assigned was assumed to be the
actual age. One of the recommendations suggested was that for the assessment of the
Northeast Atlantic mackerel stock the matrix of catches should range up to age 11 with a
12+ group. The validation of the methods used to determine age are of great relevance
(Beamish and McFarlane, 1983) as the use of incorrect growth rates can lead to large errors
in the estimates of stock production (Ricker, 1989). In this paper the age determination
criteria established by ICES (1995) were followed and ages of up to 18 years were assigned
(considering the 15+ group) with the aim of determining the growth parameters.
During the period of study (1990-2000) a significant interannual variability was detected
between the length distributions by age group, although when viewed graphically the
differences are not very appreciable. The length distribution of an age class is partly
determined by the temporal difference (during the spawning season) of the moment when
the larvae hatch, food availability, environmental conditions, etc. All these factors may
give rise to different growth rates (Wooton, 1990). In the area of study, primary production
is, to a great extent, determined by upwelling processes (Blanton et al., 1984; Lavin et al.,
1998) which may have a great influence on juvenile growth (Cushing, 1995). During their
migration, adults are subject to highly variable environmental conditions, which influence
their growth and spawning potential (Lam, 1983; Weatherley and Gill, 1989).
Due to the variability in the length range by age group among years, mean length was
estimated in order to calculate the growth parameters of the set of all years, to obtain an
indicator of the mean growth of mackerel in the area. The indices φ’ estimated for each year
are fairly similar, those of 1991 and 1992 being the lowest and having the greatest
confidence interval. The calculation of growth parameters was performed without age group
1 in 1992 and with a reduced number of individuals in 1991, which is probably the cause of
these differences.
Despite numerous references to Northeast Atlantic mackerel growth, few indicate
differential growth between males and females. Eltink (1987) found differences in length
and mean weight of males and spawning females but attributed them to temporal differences
in maturity. In the present paper the growth rate of females was significantly greater than
that of males from age 4, and no significant differences were found up to age 3. For certain
geographical areas included in our study area, different growth between males and females
has already been indicated (De la Hoz and Villegas, 1987; Lucio 1997). Differences in
growth between sexes have also been cited in Northwest Atlantic mackerel (Neja,1990).
The mackerel growth curves of the southern area estimated by other authors show quite a lot
of similarity (Table 5, Fig. 6). The greatest lengths at age were estimated by Gordo et al.,
(1984). This is probably due to differences in age interpretation with respect to other authors
(Table 5).
Unlike other authors who studied the Southern mackerel component, the growth curve
calculated in this paper was based on data with a greater coverage of the area of distribution
of this component and over a longer period of years. If we compare the curve we obtained
with those cited for the Western and Northern components (Table 5, Fig. 7), noteworthy
differences appear with that estimated by Kästner (1977) in waters of the West of Scotland
(Division VIa).
In general, from age 6 mackerel growth is observed to be faster in the southern area. Kästner
(1977) described two groups of mackerel in the West of Scotland based on growth rates,
one group of rapid growth and another of slow growth. Corten and Van de Kamp (1978)
also described differences in the growth pattern in the Celtic Sea, indicating that western
mackerel from the British Isles did not constitute a homogeneous stock.
The rapid growth group follows the pattern of growth described for mackerel in the North
Sea (Nedelec, 1960; Aker, 1961) and the slow growth group follows that proposed by
Steven (1952), Nedeler (1960), Molloy (1964), and Lockwood and Johnson (1976) in the
Celtic Sea, Northwest of Ireland and the English Channel. Nevertheless, Eltink and
Gerritsen (1982) and Eltink (1987) discard the hypothesis that there are two sub-populations
in the Western area and postulate an alternative explanation, that the growth differences are
due to gradual spatial temporal changes in the length at age during migration. The largest
fish of a certain age reach spawning areas earlier and also leave for feeding areas earlier than
smaller ones, which leads to successive changes in length and weight at age. Eltink and
Gerritsen (1982) calculated a growth curve for mackerel of the Western area in Divisions
VIa and VIIbj, which was intermediate between the two groups described by Kästner
(1977). For this reason they considered that it represented mackerel growth in the Western
area. Skagen (1989) estimated a growth curve using a modified von Bertalanffy equation.
Using data of Norwegian catches, he concluded that mackerel caught in the North Sea are
generally larger than those of the Western area. The values of the index φ’ referred to for the
different areas also show considerable similarity, with the exception of the slow growth
observed by Kästner (Fig. 8).
Fish growth is characterised by its variability and the same species can show different
growth patterns. The factors causing this variability are many and may be exogenic (i.e.
environmental, density-dependent) or endogenic (i.e. genetic), (Wooton, 1990). Parrish et
al., (1985) analysed the variability of anchovy growth, attributing the causes to the variation
in spawning periods, the composition at age, migration of specific lengths or a combination
of these factors. The growth of Northeast Atlantic mackerel may be influenced by this kind
of factor. The spawning season occurs earlier in the south of Europe than in the north
(Iversen, 1981; Lockwood et al., 1981; Jorge et al., 1982; Solá et al., 1990; 1994). Dawson
(1991), referring to the spawning season, found that the radius of the first otolith ring was
greater in mackerel from the south of the Bay of Biscay. The catch composition at age also
varies in the different areas of the Northeast Atlantic (ICES, 1996, 1997, 1998, 1999a, 2000,
2001). As previously stated, Eltink (1982, 1987) related differences in growth with gradual
changes in length at age in time and space during migration by Northeast Atantic mackerel
in European waters.
Another cause of variability in mackerel growth may be the effect of population density, as
found by Mackay (1973), Overholtz (1989) and Neja (1995) in the Northwest Atlantic,
above all in the youngest ages. In the Northeast Atlantic, Agnalt (1989) also found a
negative correlation between mean fish length at 1 and 2 years of age and North Sea
mackerel stock biomass in the 1970’s. Northeast Atlantic mackerel has not shown great
variations in annual classes in the last fifteen years (ICES, 2001) and these effects are more
difficult to investigate.
The whole of these factors makes the pattern of Northeast Atlantic mackerel growth variable
in time and space. Therefore, the use of length distributions for age assignation is
questionable (Skagen, 1989) and it would be appropriate to make more effort in age
determination through the analysis of hard structures such as otoliths.
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Table 1: Mean length at age (TL, cm) and standard deviation (SD) determined from mackerel otolith readings (n: number of samples,
sexes combined) from ICES Divisions VIIIc and IXa, sampled from 1990 to 2000.
Age TL SD n TL SD n TL SD n TL SD n TL SD n TL SD n1 25.2 1.50 73 25.5 1.41 7 25.1 1.18 43 25.4 0.98 44 26.1 1.40 312 29.2 1.88 46 30.3 0.83 13 31.9 0.98 7 30.3 2.99 9 28.8 1.57 49 30.8 1.79 443 33.1 1.89 47 32.2 1.11 46 33.3 1.77 94 34.1 1.29 11 32.2 2.03 55 33.6 1.40 764 34.9 1.59 62 34.6 1.68 55 34.5 1.57 83 35.6 1.44 113 36.3 2.19 75 35.6 1.67 495 36.6 1.94 86 35.4 1.28 42 36.2 1.59 87 36.5 1.68 61 37.3 1.87 148 36.8 1.74 286 38.0 1.76 99 37.4 1.94 24 37.5 1.59 40 37.6 1.65 81 38.5 1.69 110 38.0 2.32 407 40.2 1.42 23 38.6 1.36 8 38.3 1.54 22 39.2 1.80 46 39.4 1.74 83 39.3 1.76 368 40.5 1.93 57 38.8 1.49 8 39.2 1.99 22 39.8 2.05 22 40.1 1.46 39 40.1 1.83 439 41.2 1.65 55 39.6 1.96 9 39.7 1.72 9 41.4 1.32 23 40.7 1.48 30 40.5 2.22 1610 41.0 1.59 17 41.5 1.60 8 40.1 1.14 5 40.4 2.08 18 40.9 1.86 16 41.9 1.58 1711 41.9 2.07 5 42.5 2.00 3 40.4 1.83 9 41.3 1.19 12 42.3 2.12 12 41.4 2.25 1812 42.2 1.89 7 44.5 1.41 2 42.1 1.82 5 43.5 1.51 8 42.9 1.14 5 43.1 2.01 1013 46.5 1.41 2 0 40.0 0.71 2 43.3 1.09 13 41.8 1.53 3 44.1 1.52 514 42.5 1 43.5 1.41 2 0 43.4 1.64 8 43.0 1.76 6 44.0 1.64 6
15+ 45.5 1 43.5 1 45.8 2.52 3 43.8 1.97 12 44.5 1 43.9 1.99 7Total 581 228 388 480 676 426
Age TL SD n TL SD n TL SD n TL SD n TL SD n TL SD n1 24.5 1.31 57 24.3 1.36 300 25.4 1.18 170 23.4 1.03 75 24.4 1.53 290 24.6 1.47 10902 32.2 1.37 6 28.7 1.57 160 29.8 1.00 141 30.0 1.10 53 29.0 2.22 75 29.5 1.74 6033 33.2 1.26 58 32.9 2.34 46 32.3 1.57 167 32.2 1.41 46 32.4 1.63 289 32.7 1.71 9354 35.2 1.56 129 35.0 1.62 254 34.7 2.05 82 34.7 1.81 132 35.2 1.92 127 35.1 1.78 11615 37.2 1.86 39 36.9 1.61 168 36.8 1.64 155 37.3 1.98 68 36.4 2.12 232 36.7 1.86 11146 39.2 2.06 22 38.1 1.78 55 37.7 1.55 128 38.1 1.63 101 38.5 1.63 103 38.0 1.75 8037 39.7 1.84 61 39.7 1.54 69 38.5 1.73 62 38.7 1.51 65 39.1 1.36 141 39.2 1.66 6168 40.5 1.87 35 40.1 1.63 71 40.3 1.42 36 39.7 1.99 25 39.7 1.38 66 40.0 1.74 4249 41.1 1.83 41 41.2 1.40 75 40.2 1.73 41 41.1 2.01 19 39.5 2.03 18 40.8 1.74 33610 41.9 2.52 20 42.0 1.50 55 41.3 1.75 38 41.8 1.29 26 41.8 2.11 17 41.5 1.80 23711 41.9 2.06 17 42.8 2.02 33 41.6 1.68 17 42.3 1.35 18 41.9 1.50 11 42.0 1.91 15512 42.9 2.55 10 43.5 1.64 33 41.9 1.70 20 41.8 1.36 12 42.3 1.23 10 42.7 1.80 12213 45.5 0.00 2 43.6 1.55 8 43.2 1.15 3 43.6 1.07 7 41.7 1.30 5 43.3 1.69 5014 43.0 0.71 2 44.3 1.10 5 43.5 2.00 3 41.5 1 42.3 0.84 5 43.3 1.48 39
15+ 44.5 1.41 5 44.7 1.55 10 43.0 2.12 2 43.2 1.15 3 44.5 2.83 2 44.2 1.78 47Total 504 1342 1065 651 1391 7732
1994 19951990 1991 1992 1993
2000 Total 1990-20001996 1997 1998 1999
.
Table 2: Comparisons of length distributions by age group of mackerel, 1990-2000. (K-
W:Kruskal-Wallis test; K-S: Kolmogorov-Smirnov test;(p<0.05*;p<0.01**
;p<0.001***; ns: not significant)
Table 3: Mean length at age (TL, cm) and standard deviation (SD) for male and female
determined from mackerel otolith readings (n: number of samples) from ICES
Divisions VIIIc and IXa, sampled during 1990-2000.
Age TL SD n TL SD n1 24.6 1.47 487 24.7 1.48 4912 29.4 1.79 255 29.7 1.64 2983 32.6 1.68 462 32.7 1.71 4304 35.0 1.74 619 35.3 1.81 5235 36.5 1.87 549 37.0 1.84 5546 37.8 1.73 354 38.3 1.75 4367 39.0 1.72 275 39.3 1.60 3368 39.8 1.79 197 40.2 1.76 2239 40.5 1.66 141 41.2 1.72 18910 41.3 1.95 93 41.7 1.70 13811 41.4 1.94 72 42.5 1.72 7712 42.4 1.54 41 43.0 1.83 7613 42.4 1.30 21 43.6 1.69 3114 43.3 1.47 17 43.4 1.55 20
15+ 44.3 2.03 13 44.2 1.63 28Total 34.7 5.34 3596 35.4 5.61 3850
Male Female
Table 4: Von Bertalanffy growth parameters of mackerel (Linf, k, and t0) and their standard
error (SE), calculated for sexes combined from data of annual mean lengths at age and
pooled data 1990-2000, and for each sex from pooled data (R2: correlation coefficient,
n: number of samples).
Linf SE K SE t0 SE R2 n
1990 45.4 1.129 0.204 0.035 -3.09 0.741 0.97 581
1991 46.0 1.213 0.164 0.025 -4.20 0.757 0.98 228
1992 45.2 1.601 0.130 0.028 -7.38 1.505 0.99 388
1993 44.0 0.693 0.227 0.029 -2.96 0.542 0.98 480
1994 43.7 0.510 0.250 0.024 -2.45 0.378 0.99 676
1995 44.9 0.635 0.198 0.021 -3.64 0.498 0.99 426
1996 44.5 0.830 0.239 0.036 -2.68 0.620 0.97 504
1997 45.2 0.376 0.220 0.013 -2.62 0.233 1.00 1342
1998 44.0 0.384 0.217 0.014 -3.07 0.291 0.99 1065
1999 43.1 0.474 0.277 0.026 -1.98 0.333 0.98 651
2000 43.4 0.530 0.250 0.025 -2.38 0.384 0.98 1391
1990-2000 44.3 0.334 0.228 0.013 -2.70 0.233 1.00 7732*
Male 44.0 0.437 0.226 0.017 -2.78 0.313 0.99 3596
Female 44.4 0.299 0.232 0.012 -2.63 0.208 1.00 3850
* indeterminate included
Table 5: Von Bertalanffy growth parameters, index φ’ and expected length at age of the mackerel from different Eastern Atlantic areas
(ICES Divisions).
Period of studiesICES Area (months) 0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15+ Linf K t0
(1) Division VIa 1973-1976 23.3 25.1 26.5 27.6 28.6 29.3 29.9 30.4 30.7 31.0 32.27 0.221 -4.767 2.36(IV-VI)
(2) Division VIa 1973-1976 30.5 32.7 34.5 35.8 36.8 37.5 38.1 38.5 38.9 39.1 39.96 0.272 -4.293 2.64(VII-VIII)
(3) Divisions VIa, 1981 25.1 28.5 31.1 33.1 34.7 35.9 36.8 37.5 38.0 38.5 39.90 0.259 -2.840 2.62 VIIb - VIIj (III-VII)
(4) North Sea and 1960-1985 23.1 29.0 32.2 34.0 35.3 36.3 37.1 37.8 38.5 39.2 39.9 40.6 41.3 42.0 0.750 -0.600 - Western Area
(5) Division IXa 1981 21.1 26.5 30.6 33.8 36.2 38.1 39.5 40.5 41.3 42.0 42.4 43.94 0.272 -2.404 2.72 (Portugal coast)
(6) Division IXa 1981-1983 23.8 28.7 32.4 35.2 37.3 39.0 40.3 41.2 42.0 42.5 43.0 43.3 43.5 43.7 43.9 44.0 44.36 0.268 -2.874 2.72 (Portugal coast)
(7) Division VIIIc 1982-1983 23.7 28.1 31.5 34.1 36.2 37.7 38.9 39.9 40.6 41.2 41.6 41.9 42.2 42.4 42.5 43.07 0.258 -2.095 2.68 (Cantabrian Sea) (II-VI)
(8) Division VIIIc 1985-1986 25.1 28.6 31.5 33.8 35.8 37.3 38.6 39.7 40.6 41.3 44.50 0.199 -3.180 2.60 (Asturian coast)
(9) Divisions VIIIabc 1987-1993 25.0 28.7 31.8 34.3 36.4 38.1 39.5 40.6 41.5 42.3 42.9 43.5 43.9 44.2 44.5 45.88 0.196 -3.026 2.62 (Basque Country) (II-V)
(10) Division IXa 1990-1996 21.4 26.0 29.7 32.7 35.0 36.9 38.4 39.6 40.6 41.3 41.9 42.4 42.8 43.1 43.3 43.5 44.30 0.227 -2.900 2.65 (Portugal coast)
(11) Divisions VIIIc-IXa North 1990-2000 25.2 29.1 32.2 34.7 36.6 38.2 39.4 40.4 41.2 41.8 42.3 42.7 43.0 43.3 43.5 44.28 0.228 -2.700 2.65 (Spanish coast) (I-VI)
Age (years) ParametersΦ
(1) (2) Kästner, 1977 (5) Gordo et al., 1982 (8) De la Hoz and Villegas, 1987 (11) Present work
(3) Eltink and Gerritsen, 1982 (6) Gordo and Martins, 1984 (9) Lucio, 1997
(4) Skagen, 1989 (7) Cort et al., 1986 (10) Martins, 1998
VaIIa
Vb
IVa
IVb
IVc
VIb VIa
XIIVIIc
VIIkVIIg
VIIhVIIe
VIIIdVIIIe
X
IXb IXa
VIIIa
VIIIb
VIId
VIIaVIIb
IIIa
VIIj
VIIIc
IXaNorth
60º N
55º N
50º N
45º N
40º N
STUDY AREA
Figure 1: Location of the study area and ICES Areas .
400
450
500
550
600
650
700
750
800
1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000
Years
Mea
n w
eigh
t (g)
8 9 10 11 12 13 14 15+
10
110
210
310
410
510
610
1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000
Years
Mea
n w
eigh
t (g)
1 2 3 4 5 6 7
Figure 2: Mean weight at age (g) of mackerel from ICES Divisions VIIIc and IXa, 1990-2000.
Upper figure, ages 1 to 7 and lower figure, ages 8 to 15+.
0
5
10
15
20
25
30
35
40
45
50
0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15
Age (years)
Tota
l Len
gth
(cm
)
Observed Mean Length Growth curve
Figure 3: Von Bertalanffy growth curve fitted to mean length at age data for sexes combined and
the whole period 1990-2000, and observed mean length at age (+/- SD).
0
5
10
15
20
25
30
35
40
45
50
0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15
Age (years)
Tota
l Len
gth
(cm
)
Female Male
Figure 4: Von Bertalanffy growth curve fitted to mean length at age data for males and females
and the whole period 1990-2000.
1.80
2.00
2.20
2.40
2.60
2.80
3.00
3.20
1990 1991 1992 1993 1994 1995 1996 1997 1998 1999 2000
Gro
wth
Per
form
ance
Inde
x
1.80
2.00
2.20
2.40
2.60
2.80
3.00
3.20
Male Female
Gro
wth
Per
form
ance
Inde
x
Figure 5: Values of Growth Performance Index (φ’) and confidence intervals. Upper graph
shows annual values (1990-2000) for sexes combined and lower graph shows values for males
and females for the whole period.
0
10
20
30
40
50
0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15+
Age (years)
Tota
l Len
gth
(cm
)
1 2 3 4 5 6 7
Southern Area
Figure 6: Theoretical growth rate of the southern component of Northeast Atlantic mackerel,
according to the von Bertalanffy equation calculated by different authors: 1. Gordo et al.
1982 (Division IXa, Portuguese waters); 2. Gordo et al., 1984 (Division IXa, Portuguese
waters); 3. Cort et al., 1986 (Division VIIIc, Cantabrian Sea); 4. De la Hoz et al., 1987
(Division VIIIc, coast of Asturias); 5. Lucio, 1997 (Divisions VIIIbc, Basque country
coast); 6. Martins, 1998 (Division IXa, Portuguese waters); 7. Present work (Division
VIIIc and IXa north).
0
10
20
30
40
50
0 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15+
Age (years)
Tota
l Len
gth
(cm
)
1 2 3 4 5
Southern, Western and North Sea Area
Figure 7: Theoretical growth rate of Northeast Atlantic mackerel in different areas, according to
the von Bertalanffy equation calculated by different authors: 1. Southern Area (Division
VIIIc and IXa north) (present work); 2. Western Area (Division VIa) (Kästner, 1977); 3.
Western Area (Division VIa) (Kästner, 1977); 4. Western Area (Division VIIb and VIIj)
(Eltink & Gerritsen, 1982); 5. Northern and Western Area (Skagen, 1989).
1.80
2.00
2.20
2.40
2.60
2.80
3.00
3.20
(1) VIa
(2) VIa
(3) VIa,
VIIbj
(5) IX
a
(6) IX
a
(7) VIIIc
(8) VIIIc
(9) VIIIa
bc
(10) IX
a
(11) V
IIIc- IX
aN
Gro
wth
Per
form
ance
Inde
x
ICES Areas
Figure 8: Values of Index φ’ in different areas of the Northeast Atlantic. See Table 5 for
corresponding Divisions and authors.