Scientific Cooperation to Support Responsible Fisheries in the Adriatic Sea

SPECIES LIST

Eledone cirrhosa
Eledone moschata
Loligo vulgaris
Lophius budegassa
Lophius piscatorius
Merlangius merlangus
Merluccius merluccius
Mullus barbatus
Nephrops norvegicus
Pagellus erythrinus
Parapenaeus longirostris
Sepia officinalis
Solea vulgaris

 

 

 

 

 

 

 

 

 



 

Merluccius merluccius (Linnaeus, 1758) - (Sin. Merluccius vulgaris Fleming, 1818)

SPECIES DESCRIPTION

DISTRIBUTION

BIOLOGICAL DATA

EVALUATION AND EXPLOITATION

ESSENTIAL FISH HABITAT

FISHERIES MANAGEMENT

GENETICS

LEGISLATION

REFERENCES

 
Class:  Actinopterygii
Order:  Gadiformes
Family:  Merlucciidae
English name:  European hake
   
Local Name: 

SQ:

 Merluci

HR:

 Oslić, mol

IT:

 Nasello, merluzzo

SR:

 Oslić, Luc

SL:

 Oslić

Source: Food and Agriculture Organization of the United Nations, Original Scientific Illustrations Archive

SPECIES DESCRIPTION

The body of European hake is long and cylindrical. The widest part is behind the head. The mouth is large. There are two dorsal fins. The first one is short and triangular and the second one is long. The anal fin is similar in shape and size to the second dorsal fin. The ventral fins are placed before the pectoral ones. The caudal fin is cut in a straight line.

Morphology data:
The number of rays in particular fins is as follows: D1: 8-10, D2: 35-40, A: 36-40, P: 12-14, V: 7 (Fisher et al., 1987; Jardas, 1996). The colour is slate grey above and lighter on sides, the belly is whitish (Relini et al., 1999).

DISTRIBUTION

World:
European hake inhabit the north-eastern Atlantic from Norway to Mauritania and the entire Mediterranean; in the Black Sea the species lives only along the southern coasts (Jardas, 1996, Relini et al., 1999).

Adriatic Sea:
According to available data, European hakes are distributed throughout the Adriatic. It is a distinctively euritopic species. Bathymetric distribution of the species in the Adriatic is from only several meters in the coastal area to 800 m in the South Adriatic Pit (Kirinčić and Lepetić, 1955; Županović and Jardas, 1986; Ungaro et al., 1993; Jukić et al., 1999). There are only limited areas to the north of the Po delta in which it is not caught (Jukić and Arneri, 1984; Frattini and Paolini, 1995; Frattini and Casali, 1998).

Habitat:
This nectobenthonic species is most abundant at depths between 100 and 200 m, where the catches are mainly composed of juveniles (Ghirardelli, 1959b; Županović, 1968; Jukić and Arneri, 1984; Flamigni, 1983; Giovanardi and Rizzoli, 1984 Bello et al., 1986; Županović and Jardas, 1989; Ungaro et al., 1993; Vrgoč, 2000).

In daylight, the European hake stay on the bottom and move vertically to higher strata at night (Jardas, 1996). In addition to circadian migrations, there are also horizontal migrations as a consequence of searching for food.

Seasonal migration:
Spring:
In the spring months, there are local movements of sexually immature adolescent hakes into the more shallow channel waters of the central Adriatic between Croatian islands. Adult European hake are mainly caught at depths of 100 to 150 m. In the spring, adult hakes migrate to more shallow coastal waters for spawning. The juveniles display migration patterns in search of food.
Winter:
In the winter period, after spawning, adult fish migrate towards the deeper water, wintering with the juveniles (Županović and Jardas, 1989). In the southern Adriatic the largest individuals are caught in waters deeper than 200 m, whereas medium-sized fish appear in the stratum not deeper than 100 m (Ungaro et al., 1993).

Bottom preferences:
European hake prefer muddy bottoms, but are well distributed on other types of bottom as well (muddy-sandy and sandy bottoms). It is most abundant in the open central Adriatic (the Pomo/Jabuka Pit) and further southwards (Županović, 1961a, Županović and Jardas, 1986).

Distribution map of Merluccius merluccius in the Adriatic Sea: indicator kriging representation (Sabatella and Piccinetti, 2005).
Data: Medits Programme (CLICK TO ENLARGE):

Click here to enlarge

Some examples on the distribution of the total stock, recruits and spawner fractions in the GSA N° 18

Abundance data coming from Medits survey 1996-2004 in the GSA 18 were processed by means of geostatistic techniques.
The Indicator Kriging procedure was utilised in order to best manage all the available data. The indicator kriging permits to correct the effect of spatial clustering of sample points that sometimes occurs in the theoretical random sampling design. Several threshold were used to best fit the probability that value at any location exceed the limit value (e.g. number per Km2>1) and resulting maps were combined to better describe the spatial distribution of the abundance index values. In order to perform semivariogram analysis and subsequent Kriging Interpolation, GSTAT Software was used. Map representations for the GSA 18 were obtained by means of ESRI ArcView GIS.
The examples are related to the total stocks, recruits and spawner fractions. The cut-off values and R/ Tot – A/Tot ratio weren’t considered.

 

 

 

 

 

 

 

 

 


 

 

 

 
 

Abundance data coming from Medits survey 1996-2004 in the GSA 18 were processed by means of geostatistic techniques.
The Indicator Kriging procedure was utilised in order to best manage all the available data. The indicator kriging permits to correct the effect of spatial clustering of sample points that sometimes occurs in the theoretical random sampling design. Several threshold were used to best fit the probability that value at any location exceed the limit value (e.g. number per Km2>1) and resulting maps were combined to better describe the spatial distribution of the abundance index values. In order to perform semivariogram analysis and subsequent Kriging Interpolation, GSTAT Software was used. Map representations for the GSA 18 were obtained by means of ESRI ArcView GIS.
The examples are related to the total stocks, recruits and spawner fractions. The cut-off values and R/ Tot – A/Tot ratio weren’t considered.

BIOLOGICAL DATA

Size:
According to Jardas (1996), European hake can grow to 130 cm of total length. However, its usual length in trawl catches is from 10 to 60 cm. This is a long-lived species, it can live more than 20 years. In the Adriatic, however, the exploited stock is mainly composed in number of 0+, 1+ and 2+ year-old individuals. On the basis of the vertebral counts of European hake from the northern and central Adriatic, Piccinetti and Piccinetti Manfrin (1971b) found that all specimens analysed belonged to the same population. Similarly, the Adriatic population has the same number of vertebrae as the European hake from the rest of the Mediterranean (Maurin, 1965).

Length-weight relationship:
The data about the length-weight relationship are summarised in the table Jardas (1976) found out that the length-weight relationship could be divided into three phases according to the coefficient b: juvenile, adolescent and adult.

Total Length (TL, cm) – weight (g) relationship.

Author Sex a b

Matta, 1954

M - 2.80
F - 3.01

Jardas (1976)

M (juven.-adult) - 2.625-3.235
F (juven.-adult) - 3.033-2.862

Flamigni, 1983

M (May) 0.0043 3.16
F (May) 0.0035 3.26
M+F (May) 0.0032 3.27
M (November) 0.0025 3.35
F (November) 0.0029 3.32
M+F (November) 0.0035 3.25

Marano, 1993

M+F 0.00257 3.29

Ungaro et al., 1993

M 0.00217 3.35
F 0.00328 3.22
M+F 0.00257 3.29

Marano, 1996

M+F 0.0055 3.07

Regner and Joksimovic, 2001

- 0.0035 3.155

Reproduction:
In the Adriatic, European hake spawn throughout the year, but with different intensities. The spawning peaks are in the summer and winter periods (Karlovac, 1965; Županović, 1968; Županović and Jardas, 1986, Županović and Jardas, 1989; Jukić and Piccinetti, 1981; Ungaro et al., 1993). Hake are partial spawners. Females spawn usually four or five times without ovarian rests. In females in the pre-spawning stage, fish 70 cm long can contain more than 400 000 oocytes (Sarano, 1986). The earliest spawning in the Pomo/Jabuka Pit occurs in winter in deeper water, (up to 200 m). As the season progresses into the spring-summer period, spawning occurs in more shallow water. The recruitment of young individuals into the breeding stock has two different maxima. The first one is in the spring and the second one in the autumn.

In the Pomo/Jabuka Pit, both of these maxima can be linked to hake's more intense summer and winter spawning period in the central Adriatic (Županović and Jardas, 1989). The recruitment peaks are in the spring and autumn (Karlovac, 1965). Recruitment does not seem to be related to the parental stock size (Alegria Hernandez and Jukić, 1992). Nursery areas are located close to the Pomo/Jabuka Pit, between 150 and 200 m, on the upper part of the slope, and off the Gargano Cape (Županović, 1968; Jukić and Arneri, 1984; Županović and Jardas, 1986, Županović and Jardas, 1989; Frattini and Paolini, 1995; Frattini and Casali, 1998). Karlovac (1965) recorded young hake larvae from October to June, the highest numbers were recorded in January and February. Larvae and postlarvae were mainly distributed between 40 and 200 m; the highest number of individuals was caught mainly between 50 and 100 m.

Length at the first sexual maturity:
Different data about the size at first sexual maturity of European hake in the Adriatic Sea, given by different authors, are shown in table.

Total Length (Lm, cm) at the first sexual maturity.

Author Sex

(Lm, cm)

Zei, 1949

M 22.30

Županović, 1968

M 20.28
F 26-33

Županović and Jardas, 1986

M 20-28
F 23-33

Ungaro et al., 1993

M+F 25-30

Cetinić et al., 1999

M+F (Velebit Channel) 24

Differences in the growth dynamics between males and females can be seen in the following Tables. Females attain larger size than males, who grow more slowly after maturation at the age of three or four years. Consequently, the proportion of males in the population is higher in lower length classes and proportion of females is higher at greater lengths. In the central and northern Adriatic, females already start dominating the population at lengths of about 30 to 33 cm. In trawl catches over 38 to 40 cm, almost all the specimens are females (Vrgoč, 2000).

Total Length and age data:

Total Length (TL, cm) and age (year) data.

Author Sex

Age (yr)

1 2 3 4 5 6 7 8

Ghirardelli, 1959b

M+F 18.8 23.0 28.8 38.0 - - - -

Županović, 1968

M+F 9 19 28 35 40 44 49 57

Flamigni, 1983

M+F (May) 14.3 21.3 29.0 35.0 - - - -
M+F (Nov.) 19.0 26.2 33.3 39.0 - - - -

Von Bertalanffy Growth Function (VBGF).
Parameters of the Von Bertalanffy Growth Function (VBGF).

Author

Sex L(cm) K(yr-1) t0(yr) Φ’

Flamigni, 1983

M+F 85 0.12 - 6.77

Alegria Hernandez and Jukić, 1990

M+F 92.83 0.097 -0.629 6.73

Bolje, 1992

M+F 75 0.12 - 6.52

Vrgoč, 1995 (“Hvar”)

M+F 83.27 0.125 -0.73 6.76

Ungaro et al., 1993

M+F 75.68 0.153 0.14 6.78
F 82.63 0.126 -0.312 6.76

Marano, 1996

M 57 0.17 -0.83 6.31
F 67.5 0.159 -0.436 6.59
M+F 67.5 0.144 -0.807 6.49
M+F (Bhatt) 81 0.25 - 7.40

Marano et al., 1998b

Marano et al., 1998c

M 72 0.15 0.005 6.66
F 84 0.13 0.102 6.82
M+F 84 0.12 -0.14 6.74
M+F( Bhatt) 62.2 0.23 - 6.79
M+F (Surf.) 68 0.25 - 7.05

Vrgoč, 2000

M+F 77.95 0.130 - 6.67

EC XIV/298/96-EN, Ionian and Southern Adriatic

M+F 68.19 0.157 - 6.59

EC XIV/298/96-EN, Adriatic Sea

M+F 85 0.12 - 6.77

Feeding behaviour:
Until they are about 16 cm long (first year of life), European hake feed mostly on crustaceans (Euphasiacea, Mysidacea and Amphipoda). During that period, they live predominantly in the Pomo/Jabuka Pit and in the southern Adriatic pit region.

Their migration to the channel regions of the eastern Adriatic coast is linked to the changes of feeding patterns as they start feeding on fish, primarily Sardina pilchardus, Sprattus sprattus and Engraulis encrasicolus. Other fish prey of European hake are Scomber scomber, Trachurus spp. and Merluccius merluccius. Cephalopods were also found in hake stomachs (Kirinčić and Lepetić, 1955, Karlovac, 1959; Županović, 1968; Piccinetti and Piccinetti Manfrin, 1971a; Jukić, 1972; Froglia 1973; Jardas, 1976; Ungaro et al., 1993).

 EVALUATION AND EXPLOITATION

By comparing the catch of European hake during the expeditions “Hvar” and “Pipeta” (1982), in the northern and central Adriatic, Jukić and Arneri (1984) found that the highest catches were during the “Hvar” expedition in depths over 200 m (6.05 kg/hr).

CPUE:
During the “Pipeta” expedition, the highest catches were in the 50 to 100 m stratum (2.96 kg/hr).
Jukić and Piccinetti (1981) found that, in the 1970s, catches were about 6 kg/hr. In the southern Adriatic, the CPUE varied from 1985 to 1997 in the range of 1.4 to 9.9 kg/hr (Marano et al., 1998b Marano et al., 1998c).

Biomass/Abundance Indexes:
During the MEDITS expedition (1996-98), in the central and northern Adriatic, the European hake's biomass index was 47.45 kg/km2 (the average value for the entire region). The highest catches were in the 100 to 200 m stratum (71.80 kg/km2) and the smallest in the 50 m stratum (14.65 kg/km2). The proportion of hake in the total demersal fish catch was 16.41% (Vrgoč, 2000).

In the Adriatic, small specimens dominate the catches. Most specimens are under 20 cm TL (Županović, 1968; Jukić and Piccinetti, 1981; Flamigni and Giovanardi, 1984; Jukić and Arneri, 1984; Bello et al., 1986; Giovanardi et al., 1986; Županović and Jardas, 1986 Županović and Jardas, 1989; Alegria Hernandez and Jukić, 1992; Ungaro et al., 1993; Marano et al., 1998b Marano et al., 1998c; Ungaro et al., 1998, Vrgoč, 2000). The proportion of juveniles in the catch of European hake in the Adriatic during the expedition “Hvar” was 72.3% and during the MEDITS expedition, 81.52% (Vrgoč, 2000). In 1972-73, a maximum production (MSY) of 3000-4000 tonnes/year was estimated for the Adriatic Sea (Jukić and Piccinetti, 1981). From the management point of view, an increase of the mesh size at first capture will increase the hake yield (Giovanardi et al., 1986; Jukić and Piccinetti, 1987). Kirinčić and Lepetić (1955) and De Zio et al. (1998) investigated the catch size structure from the bottom long-line fishery in the Southern Adriatic. The average total length of the European hake was 58.6 cm (Kirinčić and Lepetić, 1955), while De Zio et al. (1998) found a median total length of 70 cm. The average catch was 5.6 specimens per 100 hooks.

In the Adriatic, the species is mainly fished with bottom trawl nets, but long-lines and trammel-net are also used. According to the FAO statistics, in the 1980s and 1990s the annual European hake landings in the Adriatic were estimated at 2000 – 4000 tonnes, and this species was the most abundant within the demersal fish group.

Results from global models underlined the overexploitation of the European hake stock since the 1960s (Levi and Giannetti, 1972, Alegria Hernandez et al., 1982).

Mortality:
The mortality parameters of the European hake population in the Adriatic are shown in the following table.

Mortality rate coefficients for European hake in the Adriatic.

Author M(yr-1)

F(yr-1)

Z(yr-1)

Županović, 1967

- - 0.90

Granić and Jukić, 1982

- - 0.77

Alegria Hernandez et al., 1982

0.408 0.382 0.790

Flamigni and Giovanardi, 1984

0.25 0.75 0.92-1.05

Giovanardi et al., 1986

- - 0.88-1.37

Jukić and Piccinetti, 1988

- - 1.12

Marano, G., (ed.) AA.VV. (1993); Ungaro et al., 1993

0.29 0.81-1.40 1.11-1.69

Marano, 1996

0.38

1.14
Fmax=0.23-0.27

1.52(1.22-1.82)

GMS-GRUND, 1998

- - 1.23

Marano et al., 1998b

0.31

0.92
Fmax=0.23

1.23(1.02-1.43)

Vrgoč, 2000

0.25 0.80 1.05

EC XIV/298/96-EN (Ionian Sea and Southern Adriatic Sea)

-

0.46-0.68

-

0.32 (Pauly)

F(0,1)=0.18

-

0.25 (Djabali)

F(0,1)=0.14-0.15

-

EC XIV/298/96-EN (Adriatic Sea)

-

0.78-1.08

-

0.25 (Pauly)

F(0,1)=0.14-0.17

-

0.21 (Djabali)

F(0,1)=0.11-0.14

-

Recent time-series studies carried out in the southern and central Adriatic showed an apparent increasing trend of the survey catch rates from 1985 to 1995 and a decreasing trend during the second half of the 1990s (Piccinetti and Piccinetti Manfrin, 1994, Manfrin et al., 1998). In the southern Adriatic, recent time-series showed an apparent increasing trend from 1985 to 1993, and a decreasing trend from 1994 to 1997. Italian landings reached the maximum in the first half of the 1990s. In the eastern Adriatic, where the demersal fishery appeared to have developed quickly during the 1990s, a positive yield trend could be observed starting from the 1980s. However, in general a marked decrease could be observed after the relatively high landing of 1993 (Mannini and Massa, 2000).

ESSENTIAL FISH HABITAT: Those waters and substrate necessary for fish to spawn, breed, feed and grow to maturity (Magnuson-Stevens Act, 1996)

Summary Table of European hake (Merluccius merluccius) life history for the Mediterranean Sea and North East Atlantic Ocean. Associations and interactions with environmental and habitat variables are listed in the 2 following tables:

TABLE A:

Life Stage Season Location Temp (°C) Salinity (ppt) Oxygen Depth (m)
Eggs

Eggs are found all year round but concentrate after spawning peaks (summer and winter in the Adriatic sea)

Offshore, on the shelf edge 10.5-13.0 - - Eggs produced after spawning at the shelf edge or upper 150m
Citation  1 ,  2 ,  3 ,  4 ,  5 ,  6 ,  7 ,  8 ,  9 ,  10 ,  11 ,  12  13*  1 ,  2 ,  3  6 ,  7 ,  8 ,  9 ,  10 ,  11 ,  12*  1 ,  2 ,  3 ,  4 ,  5 ,  6 ,  7 ,  8 ,  9 ,  10 ,  11   - -  1 ,  2 ,  3 ,  6 ,  8 ,  10 ,  11*
Larvae All year round with peaks which follows the fluctuation in spawning activity Adriatic sea: October-June with peak in January and February Continental shelf waters, the larger they are, the shallower they leave < 10.8*
10-13*
12.8-13.8
38 - Adriatic: 40-200,
peak 50-100
50-60*
50-150*
Citation  1 ,  6 ,  7 ,  18*  1 ,  2 ,  3 ,  6 ,  7 ,  8 ,  9 ,  10 ,  11 ,  12  18 ,  19 ,  20* ,  21  9 ,  10 ,  22   22  -  6 ,  7 ,  9* ,  20*
Early Juveniles Adriatic sea: Spring and Autumn
Thyrrenian sea: summer
Ligurian sea: spring and autumn
Greek waters: november-dicember late summer - late autumn
Close to the bottom with daily vertical migration: closer to the bottom during daylight and more in the water column at night 12.6-15.6
13.5-14
11.5-13*
- - 50-250, 70-200*
Citation  6 ,  7 ,  24 ,  25 ,  26 ,  27   6 ,  7 ,  24 ,  25 ,  26 ,  27 ,  28  29 ,  30 ,  31 ,  32*  ,  33 ,  34 ,  35  29 ,  31 ,  33* - -  6 ,  7 ,  24 ,  25 ,  26 ,  27 ,  28  29 ,  30 ,  31 ,  32*  ,  33 ,  34 ,  35 
Adults Taken all year round Taken offshore, on the shelf and on part of the slope Taken from bottoms temperature ranges from 12 to 16.5°C

-

-

40-800 m but they are cought mainly between 100 and 300 m

Citation  7 ,  18 ,  27 ,  28  29 ,  34 ,  35 ,  40 ,  41   7 ,  18 ,  27 ,  28  29 ,  34 ,  35 ,  40 ,  41   29 ,  31 - -  7 ,  18 ,  27 ,  28  29 ,  34 ,  35 ,  40 ,  41 
Spawning Adults All year round with peaks
Adriatic sea: winter and summer;
Western Mediterranean: a major peak in Autumn and a minor peak in summer;
Northern Tyrenian sea: winter e <spr/sum;
North Eastern Atlantic: Jan-March
Shelf break and upper slope, mainly in canyons and rocky bottoms 10 - 13

-

-

150-300
Adriatic sea: 180-250

Citation  1 ,  3  6 ,  7 ,  8 ,  18 ,  19  ,  20 ,  21 ,  25 ,  29 ,  40 ,  41  43   7 ,  14 ,  18 ,  27 ,  28  29 ,  34 ,  35 ,  40 ,  41 ,  42 ,  43   9 ,  10 ,  19* - -  1 ,  3  6 ,  7 ,  8 ,  18 ,  19  ,  20 ,  21 ,  25 ,  29 ,  40 ,  41  43 

 

TABLE B:

  Tropic Relationship Habitat Associations and Interactions  
Life Stage Food Predators Habitat Selection Growth Mortality Production
Eggs - - Pelagics/water column, spawned in canyons and partially rocky bottoms - - -
Citation - -  1 ,  2 ,  3 ,  4 ,  5 ,  6 ,  7 ,  8 ,  9 ,  10 ,  11 ,  12  13*,  14 ,  15 ,  16  - - -
Larvae Feed on rotifers in captivity - Water column
deeper during daylight, shallower at night
0.15-0.19 mm d-1
0.15-0.14* mm d-1
- -
Citation  23   -  1 ,  2 ,  3 ,  6 ,  7 ,  9 ,  10 ,  18 ,  19* ,  20 ,  21 ,  22  19* ,  21 - -
Early Juveniles Euphausiids and mysids, were the most commen preys, with decapods as secondary prey, few pishes Some cephalopods (e.g. Illex coindetii and Eledone moschata) have been found to feed on small Merluccius merluccius Close to the bottom, mostly sandy and muddy bottoms 0.35-0.61 mm day-1
0.71-0.74* mm day-1
1.2-2.5 cm month-1
Fishing activity (mainly bottom otter trawl) is the main source of mortality -
Citation  3 ,  36 ,  37 ,  38 ,  39   44 ,  45 in press  6 ,  7 ,  24 ,  25 ,  26 ,  27 ,  28  29 ,  30 ,  31 ,  33 ,  34   6 ,  25 ,  30 ,  32 ,  33*  6 ,  7 ,  24 ,  25 ,  26 ,  27 ,  28  29 ,  30 ,  31 ,  32 ,  33 ,  34 ,  35   6 ,  7 ,  24 ,  25 ,  26 ,  27 ,  28  29 ,  30 ,  31 ,  32* ,  33 ,  34 ,  35 
Adults Mostly (90%) fishes (Clupeiformes) but also decapoda and cephalopods - Mainly taken from sandy and muddy bottoms

European hake can live up to 20 years and growth up to 130 cm TL
Estimated maximum size: females 82.6 cm TL;
males 75.7 cm TL
Atlantic maximum size 140 cm TL

Fishing activity is the main source of mortality;
it is taken both by bottom trawlers and long liners

Commercial harvest has declined from 52 Mtons in 1990s to 21Mt tons in early 2000s in the Mediterranean;
from 5900 in 1990s tons to 1300 tons in early 2000s (3750 tons in 2005) in the Adriatic sea

Citation  36 ,  37 ,  38 ,  39  -  7 ,  18 ,  27 ,  28  29 ,  34 ,  35 ,  40 ,  41   7 ,  40 ,  41   7 ,  40 ,  41 ,  42  -
Spawning Adults Mostly fishes (96%) (Centracanthidae), 2 - 3 species of decapods, no cephalopods or mysids, cannibalism can occur - Taken from sandy bottoms but most of hakes spawn on canyons and partially rocky bottoms

-

Fishing activity is the main source of mortality, they are taken mainly from long liners, but bottom trawlers also contributed to the fishing mortality

EGGS PRODUCTION: approximately
400 000 oocytes,
spawning generally every 10 days,
spawning every 7 days during peak,
985 eggs day-1
445 eggs day-1

Citation  36 ,  37 ,  38 ,  39  -  14  -  7 ,  40 ,  41 ,  42   7 ,  8 

 Citation = papers reporting the information.

          *  = North Eastern Atlantic.

FISHERIES MANAGEMENT

Gear:
In the Adriatic, the species is mainly fished with bottom trawl nets, but long-lines and trammel-net are also used.

Fisheries Statistics:
According to the FAO statistics, in the 1980s and 1990s the annual European hake landings in the Adriatic were estimated at 2000 – 4000 tonnes, and this species was the most abundant within the demersal fish group.

Merluccius merluccius capture fishery production (Adriatic Sea*). Data: FAO-FISHSTAT (GFCM (Mediterranean and Black Sea) capture production 1970-2003 (Release date: May 2005) Regional dataset available at ftp://ftp.fao.org/fi/stat/windows/fishplus/gfcm.zip.

*According to GFCM definition of statistical sub-areas the Adriatic Sea falls within the area 2.1, thus including only the Northern and Central basins, while the Southern Adriatic basin and consequently the coast of South-eastern Italy and of Albania are included in the Ionian Sea (area 2.2). In order to have as comprehensive a picture as possible of all Adriatic Sea fishery production, Albanian data originally classified as from the Ionian Sea have been included in the Adriatic data set used. Unfortunately, this was not feasible for South-western Italy (Apulia Region).

Selectivity:
Selectivity of trawl towards European hake.

Author

Mesh size stretched (mm)

L50% (cm)

SF SR  L25%-L75%

Levi et. al., 1971

35.5 9.5 2.67 7.7-11.1

Ferretti e Froglia, 1975

35.5 9.0 2.8 7.7–11.1
42.0 11 2.6 9.5-12.5

Jukić, 1975

40 10.5 2.6 -
41.4 13.2 3.2 -
55.2 19.3 3.5 -
60 21.4 3.6 -
64.6 30.2 4.7 -

Jukić and Piccinetti, 1987

41 13.9 3.4 -
55 19.7 3.6 -
65 26.8 4.1 -
40 12.4 3.1 -
40 12.0 3.0 -

Marano et al., 1998b

Marano et al., 1998c

36 8.4 2.09 -

GENETICS

 

Scientific name

Common name

Project framework

Sampling (Survey) Development of genetic marker (type & number of markers) Genetic structure (analysed samples, geographic areas) Population units in the Adriatic shared stock Reference associated

Merluccius merluccius

European haket GenPopAdr, MiPAF
(GRUND 2001, 2002)

(microsatellites, 5 optimised loci)

(6; NA,MA,SA)

Single panmictic unit
Final report of GenPopAdr project , MiPAF
Cili et al., in preparation

LEGISLATION

Minimum size:

Species (local or common name)

Species (scientific name)

Minimum size in cm or
minimum weight in kg

ALB:
It is strictly prohibited to fish and sell any aquatic species less than the minimum regulatory size as set out in Article 48.1 of Fisheries Regulations No.1 of 1997.

Merluc

Merluccius merluccius

20cm

CRO:
The Order of 1998 (145/98) and amended by the Order 101/02 on the Protection of Fish and Other Marine Organisms was adopted to determine the minimum sizes of certain species of fish.

Oslić

Merluccius merluccius

16 cm

ITA:
The self-executing rules of Reg. EC 1626/1994 establish the minimum size to protect juveniles

Nasello, Merluzzo

Merluccius merluccius

20 cm

SCG:
The minimum size is laid down (Table 7) as follows: (2. Decree on prohibition of capture and trade in fish juveniles, undersized fish and other marine organisms no. 10/2004).

Oslić luc

Merluccius merluccius

20 cm

SLO:
n.a.

Oslić

-

-

REFERENCES click to enlarge

Abella, A.J., Serena, F. (1998) Stato di sfruttamento del nasello nei compartimenti di pesca di Livorno e Viareggio. Biol. Mar. Medit., 5(2): 136-150.

AdriaMed. (2000) Priority topics related to shared demersal fishery resources of the Adriatic Sea. Report of the first meeting of the AdriaMed Working Group on shared demersal resources. FAO-MiPAF Scientific Cooperation to Support Responsible Fisheries in the Adriatic Sea. GCP/RER/010/ITA/TD-02: 21 pp.

Alegria Hernandez, V., Granić, V., Jukić, S. (1982) The protection of the hake (Merluccius merluccius L.) in the Adriatic Sea by regulation of the level of exploitation. Acta Adriat., 23 (1/2): 431-440.

Alegria Hernandez, V., Jukić, S. (1990) Some aspects of biology and population dynamics of Hake (Merluccius merluccius) from the Adriatic Sea. Rapp. Comm. Int. Mer. Medit., 32 (1): 265.

Alegria Hernandez, V., Jukić, S. (1992) Abundance dynamics of the hake (Merluccius merluccius L.) from the middle Adriatic Sea. Bull. Inst. Oceanogr., Monaco, n. special 11: 161pp.

Alfirević, S., Crnković, D., Gamulin Brida, H. (1969) Problem racionalne eksploatacije škampa (Nephrops norvegicus L.). Thalassia Jugosl., 5: 5-12.

Ardizzone, G.D. (1998) Un tentativo di valutazione delle condizioni di Merluccius merluccius e Mullus barbatus nei mari italiani. Biol. Mar. Medit., 5(2): 151-168.

Arneri, E. (1996) Fisheries resources assessment and management in Adriatic and Ionian Seas. FAO Fish. Rep., 533: 7-20.

Arneri, E., Jukić, S. (1986) Some preliminary observations on the biology and dynamics of Mullus barbatus in the Adriatic Sea. FAO Fish. Rep., 345: 79-86.

Bello, G., Marano, G., Rizzi., Jukić, S., Piccinetti, C. (1986) Preliminary survey on the Adriatic hake, Merluccius merluccius, within the Demersal Resources Assessment Programme, Spring 1985 survey. FAO Fish. Rep., 345: 200-204.

Bertrand, J. (1995) Campagnes internationales de chalutage demersal en Mediteranee (MEDITS). Campagne 1994. Manuel des protocoles. Rapp. de Contract EC-IFREMER-IEO-SIBM-NCMR (MED93: 020-018 006004): 27 pp.

Bertrand, J., Gil de Sola, L., Papaconstatinou, C., Relini, G. and Souplet, A. (1997) An international bottom trawl survey in the Mediterranean: the MEDITS programme. ICES CM 1997-03: 16 pp.

Beverton, R.J.H. and S.J. Holt (1956) A rewiev of methods for estimating martality rates in expoited fish populations, with special references to sources of bias in catch sampling. Rapp. P.-v. Reun. CIEM, 140: 67-83.

Bini, G. (1968-70) Atlante dei pesci delle coste italiane. 1-10. Mondo Sommerso Roma.

Bolje, A. (1992) Kvantitativna i kvalitativna analiza kočarskih naselja u tršćanskom zaljevu. Master thesis. Sveučilište u Zagrebu., 64 pp.

Bombace, G. (1972) Considerazioni sulla distribuzione delle populazioni di livelo batiale con particolare riferimento quelle bentoniche. Quad. Lab. Tecnol. Pesca. 1(4): 65-82.

Bombace, G., Cingolani, N. (1986) Résultats pratique du programme de recherche “Étude de faisabilité pour un system d’echantillonnage des statistiques de pęche” (programme PESTAT). FAO Fish. Rep., 345: 57-59.

Bombace, G., Cingolani, N. (1988) Distribution de l’effort de pęches dans les pęcheries des mers italiennes, densité (CV/n mi2) et CPUE (KG/CV) pour les différents métiers de pęche. In: Caddy, J.F. and Savini, M. (eds). Report of the fifth technical Consultation of the General Fisheries Council for the Mediterranean on stock assessment in the Adriatic and Ionian Seas. Bari, Italy, 1-5 june 1987. FAO Fish. Rep., 394: 234-244.

Bougis, P., Mužinić, R. (1958) Sur la croissance de Mullus barbatus (L.) dans les eaux de Split. Acta Adriat., 8(9):14 pp.

Buljan, M., Zore-Armanda, M. (1971) Osnovi oceanografije i pomorske meteorologije. Institut za oceanografiju i ribarstvo, Split, 424 p.

Caddy, J.F. (1993) Some future perspectives for assessment and management of Mediterranean fisheries. Scientia Marina, 57(2-3): 121-130.

Casali, G. Manfrin Piccinetti, S. Soro, (1998) Distribuzione di cefalopodi in Alto e Medio Adriatico. Biol. Mar. Medit., 5(2): 307-318.

Cetinić, P., (Coordinator). (1999) Istraživanje kompetitivnih odnosa između ribolova pridnenim povlačnom povlačnom mrežom (koćom), vršama za lov škampa i jednostrukim mrežema stajačicama za lov oslića u velebitskom kanalu, s posebnim osvrtom na populaciju škampa i oslića. IOF, Split, 53 pp.

Coppola, S.R., Cingolani, N. (1992) Assessment of catch and effort of Italian fleet by fishing areas based on “PESTAT” data. FAO Fish. Rep., 468: 36-68.

Cristo, M., Cartes, J.E. (1998) A comparative study of the feeding ecology of Nephrops norvegicus (L) in the bathyal Mediterranean and adjacent Atlantic. Scientia Marina, 62 (Suppl.1), 81-90.

Crnković, D. (1959) Contribution to the study of economically valuable benthonic species of the channels of the north-eastern Adriatic. Rapp. P.-v. Reun. Comm.int. Explor. scient. Mer Medit., 5: 355-363.

Crnković, D. (1964) Utjecaj koćarenja na bentoska naselja u kanalskom području sjeveroistočnog Jadrana. 11(5): 47-57.

Crnković, D. (1965) Ispitivanje ekologije i mogućnosti racionalnog unaprijeđenja eksploatacije raka Nephrops norvegicus (L) u kanalskom području sjeveroistočnog Jadrana. Disertacija, PMF Sveučilišta u Zagrebu.

Crnković, D. (1970) Prilog biološkoj i ekonomskoj problematici koćarenja u kanalskom području sjeveroistočnog Jadrana. Thalassia Jugosl., 6: 5-90.

D'Ancona, U. (1949) Il differenziamento della gonade e l'inversione sessuale degli Sparidi. Arch. Oceanogr. Limnol., 6(2/3): 97-139.

De Zio V., Ungaro, N., Vlora, A., Strippoli, G. (1998) Lo stock di nasello del basso Adriatico: Struttura demografica e rendimenti di pesca della frazione catturata con palangaro di fondo. Biol. Mar. Medit., 5 (2): 128-135.
EC XIV/298/96-EN (1996) Report of the Group of independent Experts to Advise the European Commission on the Fourth Generation of Multi-annual Guidance Programmes.

Fabi, G. (2001) Sepia officinalis: impact of three set of fishing techniques in the Adriatic and the Ligurian Sea. Study contract No. 98/069. IRPEM-C.I.B.M. 119 pp.

Ferretti, M., Froglia, C. (1975) Results of selectivity experiments, made with different trawls, on more important Adriatic demersal fish. Quad. Lab. Tecnol. Pesca., 2(1): 3-16.

Fiorentini, L., Dremiere, P.Y. (1999) ESMED Efficacy and selectivity of trawl used for the MEDITS project. Study Proposal, No. 95/29:118 pp.

Fisher, W., Schneider, M., Bauchot, M.L. (eds.) (1987) Fishes FAO d’identification des espčces pour les besoins de la pęche. Mediterranée et mer Noire. Vol. I – II., Rome, FAO. 1-2: 760 p.

Flamigni, C. (1983) Preliminary utilization of trawl surwey data for hake (Merluccius merluccius L.) population dynamics in the Adriatic Sea. FAO Rapp. Pechs / FAO Fish.Rep., (290): 109-115.

Flamigni, C., Giovanardi, O. (1984) Biological data, collected during the Pipeta expeditions, on the squid Loligo vulgaris Lam. FAO, Fish. Rep., 290: 143-146.

Fonda Umani, S., Franco, P., Ghirardelli, E., Malej, A. (1990) Outline of oceanography and phytoplankton of the Adriatic Sea. 'The Adriatic Sea': Papers presented at the 25th European marine Biology Symposium, University of Ferrara: 25-43.

Frattini, C., Casali, P. (1998) Distribuzione di Gadiformi in Alto e Medio Adriatico. Biol. Mar. Medit., 5(2): 82-98.

Frattini, C., Paolini, M. (1995) Ruolo delle acque profonde quale nursery per Merluccius merluccius (L.). Biol. Mar. Medit., 2(2): 281-286.

Froglia, C. (1972) Osservazioni sulle variazioni di cattura dello scampo, Nephrops norvegicus (L.) in riferimento all’etologia ed alla biologia della specie. Quad. Lab. Tecnol. Pesca., 1(4): 83-100.

Froglia, C. (1973) Osservazioni sull’alimentazione del merluzzo (Merluccius merluccius L.) del medio Adriatico. Atti V. Congr. Naz.Coc. It. Biol. Mar., Ed. Salentina nardo, 327-341.

Froglia, C. (1982) Contribution to the knowledge of the biology of Parapenaeus longirostris (Lucas) (Decapoda, Penaeoidea). Quad. Lab. Tecnol. Pesca., 3(2-5): 163-168.

Froglia, C. (1988) Food preferences of juvenile Red mullet Mullus barbatus in Western Adriatic nursery ground (Osteichthyes: Mullidae) Rapp. Comm. int. Mer Medit., 31(2): 263.

Froglia, C., Atkinson, R.J., Tuck, I.D., Arneri, E. (1997) Underwater television survey, a tool to estimate Nephrops stock biomass on the Adriatic trawling grounds. In: Tisuću godina prvog spomena ribarstva u Hrvata. Finka B. (Ed.), HAZU, Zagreb, 657-667.

Froglia, C., Galli, B. (1970) Selettivitŕ e capacitŕ di cattura di una rete a strascico di tipo italiano su popolazioni di Mullus barbatus L. Quad. Lab. Tecnol. Pesca, Ancona, 1(1): 1-20.

Froglia, C., Giannetti, G. (1985) Growth of common sole Solea vulgaris Quensel in the Adriatic Sea. Rapp. Comm. int. Mer Medit., 29 (8): 91-93.

Froglia, C., Giannetti, G. (1986) Remarks on rings formation in otoliths of Solea vulgaris and other flatfishes from the Adriatic Sea. FAO Fish. Rep., 345: 121-122.

Froglia, C., Gramitto, M. E. (1981) Summary of biological parameters on the Norway lobster, Nephrops norvegicus (L.), in the Adriatic. FAO Fish. Rep., (253): 165 – 178.

Froglia, C., Gramitto, M.E. (1979) An estimate of the fecundity of Norway lobster (Nephrops norvegicus) in the Adriatic Sea. Rapp. Comm. int. Mer Medit., 25/26 (4): 227-229.

Froglia, C., Gramitto, M.E. (1982) Effetti della crisi di ossigeno del 1977 sulla pesca degli scampi in Adriatico. Bollettino dei Musei e degli Istituti Biologici dell’ Universitŕ di Genoa, 50 (Suppl.): 195-201.

Froglia, C., Gramitto, M.E. (1986) Diurnal changes in fishery resources catchabillity by bottom trawl in the Adriatic Sea. FAO Fish. Rep., 345: 111-118.

Froglia, C., Gramitto, M.E. (1988) An estimate of growth and mortality parameters for Norway lobster (Nephrops norvegicus) in the Central Adriatic Sea. FAO Fish. Rep., 394: 189-203.

Froglia, C., Magistrelli, F. (1976) Considerazioni sulla pesca delle seppie con attrezzature selettive nell’alto e medio Adriatico. Gazzettino della pesca, 23(5): 1-2.

Gamulin-Brida, H., Ilijanić, V. (1972) Contribution ŕla connaissance des Cephalopodes de l’Adriatique. Acta Adriat., 14 (6): 3-12.

Garoia, Flavio, Guarniero, Ilaria & Tinti, Fausto (2003). Polymorphic dinucleotide microsatellites for the Mediterranean angler species (Lophiidae). Molecular Ecology Notes 3 (2), 294-296.

Garoia, F., Guarniero I., Ramšak, A., Ungaro N., Landi M., Piccinetti, C., Mannini, P., & Tinti, F. (2004) Microsatellite DNA variation reveals high gene flow and panmictic populations in the Adriatic shared stocks of the European squid and cuttlefish (Cephalopoda). Heredity 93(2): 1–9.

Garoia F., Guarniero, I., Piccinetti, C. & Tinti, F. (2004) First Microsatellite Loci of Red Mullet (Mullus barbatus) and their Application to Genetic Structure Analysis of Adriatic Shared Stock. Marine Biotechnology, 6 (5):446-452.

General Fisheries Commission for the Mediterranean (GFCM). (2001) Report of the twenty-six session. Lacco Ameno, Ischia, Italy, 10-13 September 2001. GFCM Report. No 26. Rome, FAO, 27 pp.

Ghirardelli, E. (1959a) Contribution ŕ l’étude de la biologie des soles (Solea solea) en moyenne Adriatique. Proc. gen. Fish. Coun. Medit., 5: 481-487.

Ghirardelli, E. (1959b) Contribution ŕ la connaissance de la biologie du merlu (Merluccius merluccius L.) eu moyenne Adriatique. Proc. gen. Fish. Coun. Medit., 5: 489-494.

Giovanardi, O., Rizzoli, M. (1984) Biological data, collected during expeditions Pipeta, on the whiting, Merlangius merlangius (L.) in the Adriatic Sea. FAO, Fish. Rep., 290: 149-153.

Giovanardi, O., Rizzoli, M., Jukić, S. (1986) Preliminary consideration on the fishery management of the hake (Merluccius merluccius L.) stock in the Adriatic Sea. FAO Fish. Rep., (345): 71-77.

GMS-GRUND (Gruppo Metodologie Statistiche – GRU.N.D). (1998) Valutazioni preliminari relative all’introduzione della taglia minima di 20 cm per il nasello nella realtŕ della pesca a strascico italiana. Biol. Mar. Medit., 5(3): 140-155.

Gramitto, M.E. (1998) Molt pattern Identification through gastrolith examination on Nephrops norvegicus (L.) in the Mediterranean Sea. Scientia Marina, 62 (Suppl.1), 17-23.

Gramitto, M.E., Froglia, C. (1980) Osservazioni sul potenziale reproduttivo dello scampo (Nephrops norvegicus) in Adriatico. Memorie di Biologia Marina e di Oceanografia, 10 (Suppl.): 213-218.

Granić, B., Jukić, S. (1982) Selektivnost i zaštita demerzalnih resursa Jadranskoga mora s posebnim osvrtom na populaciju oslića, Merluccius merluccius (L.), pravilnim izborom veličine okca na saki dubinske povlačne mreže (koće). Ichtyologia. 14 (1): 1-11.

Grubišić, F. (1980) Prilozi za poznavanje sezona mriještenja nekih jadranskih riba u području srednje Dalmacije. Morsko Ribarstvo 32 (4): 151-152.

Grubišić, F. (1982) Ribe, rakovi i školjke Jadrana. Liburnija – Naprijed, Rijeka – Zagreb, 239 pp.

Guarniero, I., Garoia, F., Di Placido, R., Ramšak, A., Mannini, P., Tinti, F. 2003. Species-specific microsatellite loci for the European squid (Loligo vulgaris). Molecular Ecology Notes 3(2): 312-313.

Guarniero I. (2004) Identification of population units of Mediterranean fishery resources by genetic structure analysis. PhD Thesis in Environmental Sciences, University of Bologna, Ravenna.

Guescini, A., Piccinetti Manfrin, G., Piccinetti, C. (1983) Distribution des larves de Mullus barbatus L. en Adriatique. Rapp. Comm. int. Mer. Medit., 28(5): 155-158.

Gulland, J.A. (1968) Manual of methods for fish stock assessment. Part I. Fish population analysis. FAO Fisheries Technical Papers (Revision 2) 40: 97 pp.

Haidar, Z. (1970) L’oecologie du rouget (Mullus barbatus L.) en Adriatique orientale. Acta Adriat., 14 (1): 1-94.

Heldt, H. (1938) La reproduction chez les crustacés Decapodes de la famillie des peneides. Ins. Oceanogr., 18: 31-206.

Hrvatski hidrografski institut. (1999) Peljar. Jadransko more – istočna obala. Hrvatski hidrografski institut, Split. 331 pp.

IMBC, UMBSM, IRPEM (1994) Nephrops norvegicus: stock variability and assessment in relation to fishing pressure and environmental factors. Final Report to the Commission Of the European Communities, Contract XIV.1/MED/91/003, 84 p + figures and appendicies.

Jardas, I. (1976) Contribution to the knowledge of the biology of hake in the Adriatic Sea. Rev. Trav. Inst. Peches marit., 40 (3 et 4): 615-618.

Jardas, I. (1987) On the biology and ecology of Lophius species (Teleostei, Lophiidae) in the Adriatic Sea. Proc. V Congr. europ. Ichthyol., Stockholm 1985, 181-185.

Jardas, I. (1996) Jadranska ihtiofauna. Školska knjiga, Zagreb, 536 pp.

Joksimović, A. 1999. Length-weight relationship of pandora, Pagellus erythrinus (Linnaeus, 1758), from the Montenegrin shelf. Acta Biologica Iugoslavica- Ichthyologia, 31(1): 9-21.

Joksimović, A. 1999. State, Structure and Exploitation Level of Red Pandora, Pagellus erythrinus (Linnaeus, 1758), Population in the Montenegrin Coastal Waters. M. Sc. Thesis, Faculty of Sciences, University of Kragujevac: 73p.

Joksimović, A. 2000. Biomass estimate and maximum sustainable yield of pandora Pagellus erythrinus (Linnaeus, 1758) in trawling fisheries at Montenegrin shelf. Acta Biologica Iugoslavica-Ichthyologia, 32(1): 17-29.

Joksimović, A., 2001. Growth of pandora, Pagellus erythrinus in Montenegrin shelf (South Adriatic). 36th Congress Commision Internationale pour l’Exploration Scientifique de la mer Mediterranee, CIESM,Septembre 24-28. 2001. Monte-Carlo. Conference proceedings.

Joksimović, A., 2004. Mortality of pandora, Pagellus erythrinus in Montenegrin shelf (South Adriatic). 37th Congress Commision Internationale pour l’Exploration Scientifique de la mer Mediterranee, CIESM, June 7-11. 2004. Barcelona. Conference proceedings.

Joksimovic, A. 2005. Population Dynamic of Red mullet Mullus barbatus, Linnaeus, 1758 in the Montenegrin shelf. Doctoral dissertation. Faculty of Biology, University of Belgrade: 93p.

Jukić, S. (1971) Studies on the population and catchabilltiy of Norway lobster in the central Adriatic. FAO Stud. Rev., 48: 27-52.

Jukić, S. (1972) Ishrana oslića (Merluccius merluccius), bukve (Boops boops) trlje (Mullus barbatus) i arbuna (Pagellus erythrinus) u Kaštelanskom zaljevu. Acta Adriat., 14 (4): 1-40

Jukić, S. (1974) The Yugoslav Nephrops fishery. Acta Adriat., 15 (8):1-18.

Jukić, S. (1975) Koćarska područja u srednjem Jadranu. Acta Adriat., 17 (1): 1-86.

Jukić, S., Arneri, E. (1984) Distribution of hake (Merluccius merluccius L.), Red mullet (Mullus barbatus L.) and Pandora (Pagellus erythrinus L.) in the Adriatic sea. FAO, Fish. Rep., 290: 85-91.

Jukić, S., Crnković, D. (1974) Stanje naselja pridnenih jestivih vrsta u Jadranu. Acta Adriat., 16 (8): 137-156.

Jukić, S., Piccinetti, C. (1974) Influence des facteurs biologiques, technologiques, sociaux et économiques sur la pęche en Adraitique. FAO; CGPM (Resume). Varna, Bulgaria, 7-9 Mars 1974.

Jukić, S., Piccinetti, C. (1979) Standing stock estimation and yield per exploitable biomass (YEB) forecast of the Adriatic edible demersal resources. Inv. Pesq., 43 (1): 273-288.

Jukić, S., Piccinetti, C. (1981) Quantitative and qualitative characteristics of demersal resources in the Adriatic sea with some population dynamic estimates. FAO, Fish. Rep., 253: 73-91.

Jukić, S., Piccinetti, C. (1987) Biological and economic aspects of mesh size regulation in the multispecies demersal fishery of the Adriatic Sea. Acta Adriat. 28(1/2): 199-219.

Jukić, S., Piccinetti, C. (1988) Contribution to the knowledge on the short and long-term effects of the application of 40 mm codend mesh size in Adriatic trawl fishery – Eastern Adriatic coast. FAO Fish. Rep. 394: 282-290.

Jukić, S., Županović, Š. (1965) Relations entre la température et l’intensité de l'alimentation chez Mullus barbatus L. et Pagellus erythrinus L. dans Baie de Kaštela. FAO Proc. gen. Fish. Coun. Medit., 8: 173-177.

Jukić-Peladić, S., Vrgoč, N., Dadić, V., Krstulović-Šifner, S., Piccinetti, C., Marčeta, B. (1999) Spatial and temporal distribution of some demersal fish populations in the Adriatic Sea described by GIS technique. Acta Adriat. 40: 55-66.

Karlovac, J. (1965) Contribution ŕ la conaissance de l’oecologie du merlu, Merluccius merluccius L., dans le stade planctonique de vie en Adriatique. Rapp. Comm. int. mer Medit., 18 (2): 461-464.

Karlovac, J., Karlovac, O. (1968) Lophius piscatorius L. dans les eaux de la haute Adriatique, dans toutes les phases de sa vie (Note preliminaire). Rapp. Comm. int. Mer Medit., 19(3): 537-540.

Karlovac, O. (1949) Le Parapenaeus longirostris (H. Lucas) de la haute Adriatique. Acta Adriat., 3(12): 407-418.

Karlovac, O. (1953) An ecolocical study of Nephrops norvegicus (L) of the high Adriatic. Izv. rep. Rib.biol. Eksp.”Hvar” 1948-49, 5(2C): 1-50.

Karlovac, O. (1959) La nourriture du merlu (Merluccius merluccius L.) de la haute Adriatique. FAO Proc. Gen. Fish. Coun. Medit., 5: 333-339.

Kirinčić, J., Lepetić, V. (1955) Recherches sur l’ichthyobentos dans les profondeurs de l’Adriatique méridionale et possibilité d’exploitation au moyen des palangres. Acta Adriat., 7 (1): 1-113.

Krstulović Šifner, S. (2000) Prilog poznavanju biologije i ekologije lignje, Loligo vulgaris (Lamarck, 1798) u Jadranu. Master Thesis. Sveučilište u Zagrebu. 98 pp.

Lepetić, V. (1965) Sastav i sezonska dinamika ihtiobentosa i jestivih avertebrata u Bokokotorskom zaljevu i mogućnost njihove eksploatacije. Studia Marina, Kotor, 1: 1-161.

Levi, D., Andreoli, M.G., Arneri, E., Giannetti, G., Rizzo, P. (1994) Otolith reading as a tool for stock identification. Fisheries Research, 20: 97-107.

Levi, D., Froglia, C., Scorcelletti, R. (1971) Selettivitŕ di una rete di tipo relingato (chalut a grande ouverture verticale). Quad. Lab. Tecnol. Pesca, Ancona 1(2): 23-35.

Levi, D., Giannetti, G. (1972) Analisi sullo stato di sfruttamento di una popolazione ittica mediante un modello matematico di cattura e sforzo. Quad. Lab. Tecnol. Pesca, Ancona. 1 (4): 101-114.

Mandić, S. (1984) Cefalopoda južnog Jadrana. Studia Marina, Kotor. 15-16: 3-77.

Mandić, S., Stjepčević, J. (1981) Mouvements migratories de quelques espčces de cephalopodes économiquement importantes dans l’Adriatique meridionale. Rapp. Comm.int. Mer Medit., 27 (5): 213-216.

Manfrin Piccinetti, G., Giovanardi, O. (1984) Données sur la biologie de Sepia officinalis L. dans l’Adriatique obtenues lors de expéditions Pipeta. FAO, Fish. Rep., 290: 135-138.

Manfrin Piccinetti, G., Rizzoli, M. (1984) Données recueilles au cours des expéditions Pipeta sur la biologie de Eledone moschata (Lam.) en Adriatique. FAO, Fish. Rep., 290: 139-141.

Mannini, P., Massa, F. (2000) Brief overview of Adriatic fisheries landing trends (1972-97). In: F. Massa and P. Mannini (eds), Report of First Meeting of the Adriamed Coordination Committee. FAO-MiPAF Scientific Cooperation to Support responsible Fisheries in the Adriatic sea. GCP/RER/010/ITA/TD-01: 31-49.

Mantovani, B., Scali, V. (1992) Allozyme characterization of the Norway lobster, Nephrops norvegicus, of two Adriatic trawling grounds. Acta Adriat., 33(1/2): 209-213.

Marano, G., (ed.) (1985) Valutazione delle risorse ittiche demersali del Basso Adriatico (Anno 1985). Min. Mar. Mer., Roma.

Marano, G., (ed.) (1987) Valutazione delle risorse demersali dell’Adriatico meridionale dal promotorio del Gargano al capo d’Otranto: proseguimento indagine ’87-’88. Min. Mar. Mer., Roma.

Marano, G., (ed.) AA.VV. (1993) Valutazione delle risorse demersali dell’Adriatico meridionale dal promotorio del Gargano al capo d’Otranto: Relazione finale triennio ’90-’93. Min. Mar. Mer., Roma

Marano, G., (ed.) AA.VV. (1996) Valutazione delle risorse demersali dell’Adriatico meridionale dal promotorio del Gargano al Capo d’Otranto: relazione finale triennio ’94-‘96. M. R. A. A. F., Roma

Marano, G., Casavola, N., Vaccarella, R., Paganelli, A., (1977) Osservazioni sulla pesca a strascico lungo il litorale di Bari. Oebalia III: 17-31.

Marano, G., De Zio, V., Pastorelli, A., Rizzi, E., Ungaro, N., Vaccarella, R. (1994) Considerazioni sullo stato di sfruttamento delle risorse demersali (Basso Adriatico). Atti Sem. sulla Regolaz. Sforzo Pesca. Biol. Mar. Medit. 1 (2): 89-94.

Marano, G., De Zio, V., Pastorelli, A., Rizzi E., Ungaro, N., Vaccarella, R., (1993) La valutazione delle risorse demersali dei mari italiani: sintesi dell’attivitŕ operativa “A9” (Basso Adriatico). N.T.R.I.T.P.P., Special Publication, 2:169-171.

Marano, G., Marsan, R., Pastorelli, A.M., Vaccarella, R. (1998a) Areale di distribuzione e pesca dello scampo, Nephrops norvegicus (L.), nelle acque del basso Adriatico. Biol. Mar. Medit., 5 (2): 284-292.

Marano, G., Ungaro, N., Marano, C.A., Marsan, R. (1998b) La ricerca sulle risorse demersali del bacino Adriatico sud-occidentale (anni 1985-97): sintesi dei risultati. Biol. Mar. Medit., 5 (3): 109-119.

Marano, G., Ungaro, N., Marzano, M.C., Marsan, R. (1998c) Le risorse demersali dell’Adriatico pugliese: Analisi di una serie storica (‘85-’95) relativa ai dati di cattura e demografia degli stock. Biol.Mar. Medit., 5 (2): 52-67.

Marčeta, B. (1996) Pojavljanja nekaterih vrst rib in glavonožcev v slovenskem morju. Annales (Koper), 6(9): 17-30.

Marrs, S.J., Tuck, I.D., Arneri, E., Atkinson, R.J.A., Santojanni, A., Stevenson, T.D.I. (2000) Improvement of Nephrops stock assessment by use micro-scale mapping of effort and landings. Final Report EC Study Contract 97/0100.

Matta, F. (1954) Il merluzzo del Mediterraneo II. Biol. Pesca Piscicolt. Idrobiol. 9(1): 2-29.

Maurin, C. (1965) Les merlus des mers européennes et nord-ouest africanes. Rapp. Comm. int. Mer Medit., 18 (2):215-220.

Merker, K., Ninčić, T. (1973) Sastav i gustina bentoskih ihtio-naselja u južnom Jadranu. Studia Marina, Kotor, 6:75-117.

Mortera, J., Levi, D., Cingolani, N. (1984) Progress Report on the PESTAT programme: A simple survey system for the quality check of fisheries statistics. FAO Fish. Rep. 290: 175-177.

Mytilineou, C.H., Castro, M., Gancho, P., Fourtouni, A. (1998a) Growth studies on Norway lobster, Nephrops norvegicus (L.) in different areas of Mediterranean Sea and adjacent Atlantic. Scientia Marina, 62 (Suppl.1), 43-60.

Mytilineou, C.H., Politou, C.-Y., Fourtouni, A. (1998b) Trawl selectivity studies on Nephrops norvegicus (L.) in the eastern Mediterranean Sea. Scientia Marina, 62 (Suppl.1), 107-116.

Orsi Relini, L., Zamboni, A., Fiorentino, F., Massi, D. (1998) Reproductive patterns in Norway lobster Nephrops norvegicus (L.) of different Mediterranean areas. Scientia Marina, 62 (Suppl.1), 25-41.

Pagotto, G., Piccinetti, C. (1982) Censimento della popolazione di Solea vulgaris Quensel 1814. in Adriatico mediante marcatura. Atti del I Seminario Italiano sui Censimenti Faunistici. Metodi e applicabilitŕ alla gestione territoriale, Urbino, 21-22 settembre ’82: 345-359.

Pagotto, G., Piccinetti, C., Specchi, M. (1979) Premičres résultats des campagnes de marquage des soles en Adriatique: déplacements. Rapp. Comm. int. Mer. Medit., 25/26 (10): 111-112.

Pastorelli A.M., Vaccarella, R., Marano, G., Ungaro, N. (1996) I crostacei dei fondi strascicabili del basso Adriatico. Nova Thalassia, 12: 27-35.

Pastorelli, A.M., Vaccarella, R., Marsan, R., Marzano, M.C. (1998) Valutazione delle risorse demersali nel basso Adriatico pugliese (1990-1995): Cefalopodi. Biol. Mar. Medit., 5 (2): 326-335.

Pastorelli, A.M., Vaccarella, R., de Zio, V. (1995) Distribuzione dei cefalopodi commerciali nel basso Adriatico. Biol. Mar. Medit., 2 (2): 501-502.

Pauly, D. (1984) Fish population dynamics in tropical waters: a manual for use with programmable calculators. ICLARM Studies and Rewiev 8, 325 pp.

Peres, J.M., Gamulin-Brida, H. (1973) Biološka oceanografija: Bentos, Bentoska bionomija Jadranskog mora. Školska knjiga, Zagreb, 493 pp.

Piccinetti, C. (1967) Studio delle variazioni della produzione delle sogliole nell’Adriatico occidentale in rapporto agli attrezzi di pesca utilizzati. Note Lab. Biol. Mar. Fano, 2(4): 57-68.

Piccinetti, C., Giovanardi, O. (1984) Données biologiques sur Solea vulgaris Quensel en Adriatique. FAO, Fish. Rep., 290: 117-121.

Piccinetti, C., Jukić, S. (1984) Considération sur les premiers resultats de la campagne de chalutage Pipeta. FAO Fish. Rep., (290): 181-185.

Piccinetti, C., Jukić, S. (1988) Élaboration des donnés sur les ressources demersales de la haute et moyenne Adriatique. FAO Fish. Rep., 394: 172-173.

Piccinetti, C., Piccinetti Manfrin, G. (1971a) Osservazioni sull’alimentazione del merluzzo (Merluccius merluccius L.) in Alto e Medio Adriatico. Note Lab. Biol. Mar. Fano, 4(3): 41-64.

Piccinetti, C., Piccinetti Manfrin, G. (1971b) Osservazioni sulla media vertebrale di merluzzi dell’Alto e Medio Adriatico. Note Lab. Biol. Mar. Fano, 4(4): 65-84.

Piccinetti, C., Piccinetti Manfrin, G. (1994) Considerazioni sullo stato di sfruttamento delle risorse demersali (Alto e Medio Adriatico). Biol. Mar. Medit., 1(2): 77-87.

Ramšak, Andreja, Garoia, Flavio, Guarniero, Ilaria, Mannini, Piero & Tinti, Fausto (2003) Novel polymorphic microsatellite markers for the common pandora (Pagellus erythrinus). Molecular Ecology Notes 3 (4), 553-555.

Relini, G. (1998) I progressi della ricerca italiana sulla pesca a strascico. Biol. Mar. Medit., 5(2): 3-21.

Relini, G., Bertrand, J., Zamboni, A. (eds.) (1999) Synthesis of the knowledge on bottom fishery resources in Central Mediterranean (Italy and Corsica). Biol. Mar. Medit., 6 (suppl. 1).

Rijavec, L. (1975) Biologija i dinamika populacije Pagellus erythrinus (L.) u Bokokotorskom zalivu i otvorenom području južnog Jadrana. Studia Marina, 8: 3-109.

Rijavec, L., Županović, Š. (1965) A contribution to the knowledge of biology of Pagellus erythrinus L. in the middle Adriatic. Rapp. P.-v. Reun. Comm. int. Explor. scient. Mer Medit., 18 (2): 195-200.

Sarano, F. (1986) Cycle ovarien du merlu, Merluccius merluccius, poisson a ponte fractionee. Rev. Trav. Pechea Marit. 48(1-2): 65-76.

Sardŕ, F. (1998a) Nephrops norvegicus (L). Comparative biology and fishery in the Mediterranean Sea. Introduction, conclusion and recommendation. Scientia Marina, 62 (Suppl.1): 5-15.

Sardŕ, F. (1998b) Comparative technical aspects of the Nephrops norvegicus (L.) fishery in the northern Mediterranean Sea. Scientia Marina, 62(Suppl. 1): 101-106.

Sardŕ, F., Lleonart, J., Cartes, J.E. (1998) An analysis of the population dynamics of Nephrops norvegicus (L.) in the Mediterranean Sea. Scientia Marina, 62 (Suppl.1): 135-143.

Scaccini, A. (1947a) Contributo alla conoscenza della biologia dei Mullidi nell’Adriatico medio occidentale. Note Lab. Biol. Mar. Fano, 1(1): 1-8

Scaccini, A. (1947b) L’accrescimento e la proporzione dei sessi nella popolazione adriatica di Mullus barbatus Rond. . Note Lab. Biol. Mar. Fano, 1(3):17-24

Scaccini, A., Furlani, F. (1965) Variations des captures de soles dans l'Adriatique occidentale en function des engins utilisés. Proc. gen. Fish. Coun. Medit., 8: 385-386.

Soro, S., Piccinetti Manfrin, G. (1989) Biologia e pesca di Cefalopodi in Adriatico. Nova Thalassia, 10(1): 493-498.

Šarčević, M. (1992) Ocjena obimnosti i biološke razine dopuštenog iskorištavanja populacije škampa (Nephrops norvegicus) u Jabučkoj kotlini. Master thesis. Sveučilište u Zagrebu. 72 p.

Šoljan, T. (1948) Ribe Jadrana. Fauna i flora Jadrana, 1. Inst. Oceanogr. Ribar., Split, 437 p.

Šoljan, T. (1977) Ribarstveno-biološka ekspedicija m/b “Hvar” u otvorenom Jadranu (1948-1949). Acta Adriat. 1(1-2): 1-22.

Štirn, J., Bolje, A. (1989) Fondi pridnenih rib in drugih užitnih organizmov obalnih vod SFRJ v Tržaškem zalivu. Zaključno poročilo. Raziskovalna naloga, Droga Portorož in IBU, MBP, Ljubljana, Piran, 243 p.

Tanaka, S. (1960) Studies on the dynamics and the management of fish populations. Bull. Tokai. Reg. Fish. Res. Lab., 28: 1-200.

Tortonese, E. (1975) Fauna d'Italia. Osteichthyes. Calderni Ed. Bologna. 11: 636 p.

Ungaro, N., Marano, G., Marsan, R., Pastorelli, A.M., (1999) On the reproduction of Nephrops norvegicus (L.) in the Southern Adriatic Sea (Mediterranean Sea): sex ratio, maturity length and potential fecundity. Crustacean Issues, 12: 553-561.

Ungaro, N., Marano, C. A., D’Uggento, A. (1998) Relazioni tra specie demersali del bacino Adriatico sud-occidentale: Analisi statistica di serie storiche. Biol. Mar. Medit., 5 (1): 196-202.

Ungaro, N., Marano, G., Marsan, R. (1996) The use of swept area method for the estimate of biomass: a first attempt relative to three demersal finfishes (hake, red mullet, four spotted megrim) in South-Western Adriatic Sea. FAO Fish. Rep. 533 (suppl.): 101-104.

Ungaro, N., Marano, G., Piccinetti, C. (1995a) Adriatic, Black Sea: the whiting doubt. Cybium, 19 (3): 311-315.

Ungaro, N., Marano, G., Vaccarella, R. (1995b) Comparazione tra aree batiali strascicabili del basso Adriatico mediante l’utilizzo dell’analisi fattoriale delle corrispondenze. Biol. Mar. Medit. 2 (2): 185-189.

Ungaro, N., Rizzi, E., Marano, G. (1993) Note sulla biologia e pesca di Merluccius merluccius (L.) nell’Adriatico pugliese. Biologia Marina, suppl., 1: 329-334.

Ungaro, N., Rizzi, E., Marzano, M.C. (1994) Utilizzo del modello di Beverton e Holt, “rendimento per recluta (Y/R)”, per la risorsa Mullus barbatus L., nell’Adriatico pugliese. Biol. Mar. Medit., 1 (1): 317-318.

Vallisneri, M., Piccinetti, C., Stagni, A.M., Colombari, A., Tinti, F. (2000) Dinamica di popolazione, accrescimento, riproduzione di Solea vulgaris (Quensel 1806) nell’alto Adriatico. Biol. Mar. Medit., 7 (1): 65-70.

Vrgoč, N. (1995) Obilježja rasta populacije oslića (Merluccius merluccius), trlje blatarice (Mullus barbatus), arbuna (Pagellus erythrinus) i škampa (Nephrops norvegicus) Jadranskog mora. Master Thesis. Sveučilište u Zagrebu, 101 pp.

Vrgoč, N. (2000) Struktura i dinamika pridnenih zajednica riba Jadranskog mora. Disertacija. Sveučilište u Zagrebu. 198 pp.

Zei, M. (1940) Pregled rezultata dosadašnjeg ribarstveno-biološkog istraživanja Oceanografskog instituta u kanalima Hrvatskog primorja. God. Oceanogr. inst. Kralj. Jugosl., 2:137-147.

Zei, M. (1949) Typical sex-reversal in Teleosts. Proc. Zool. Soc., 119 (4): 917-920.

Zei, M., Sabioncello, I. (1940) Prilog poznavanju naselja bentoskih riba u kanalima srednje Dalmacije. God. Oceanogr. inst. Kralj. Jugosl., 2:103-115.

Zei, M., Županović, Š. (1961) Contribution to the sexual cycle and sex reversal in Pagellus erythrinus (L.). Rapp. P.-v. Reun. Comm. int. Explor. scient. Mer Medit., 17 (2): 263-267.

Zore-Armanda, M. (1967) O sezonskim promjenama površinskog strujanja u Jadranu, Hidrografski godišnjak, Split, 32 pp.

Županović, Š. (1961a) Contribution ŕ la conaissance de la biologie de Merluccius merluccius L. dans l’Adriatique moyenne. FAO Proc. Gen. Fish. Coun. Medit. 6: 145-150.

Županović, Š. (1961b) Kvantitativno-kvalitativna analiza ribljih naselja kanala sednjeg Jadrana. Acta Adriat. 9(3):151 pp.

Županović, Š. (1963) Contribution a la conaissance de la biologie du Mullus barbatus (L) dans l'Adriatique moyene. Rapp. Com. int. Mer Medit., 17(2): 346-362.

Županović, Š. (1968) Study of hake (Merluccius merluccius) biology and population dynamics in the Central Adriatic. Stud. Rev. Gen. Fish. Coun. Medit., 32: 24 pp.

Županović, Š., Jardas, I. (1986) A contribution to the study of biology and population dynamics of the Adriatic hake, Merluccius merluccius (L). Acta Adriat. 27(1/2): 97-146

Županović, Š., Jardas, I. (1989) Fauna i flora Jadrana. Logos Split. 526 pp.

Županović, Š., Rijavec, L. (1980) Biology and population dynamics of Pagellus erythrinus (L) in the insular zone of the middle Adriatic. Acta Adriat. 21(2): 203-226.

 

 

 

© FAO-AdriaMed project  - Food and Agriculture Organization of the United Nations Fisheries and Aquaculture Department
(room C353)  Viale delle Terme di Caracalla - 00153 Rome -Italy- ::: tel  +39 06 570 56092/55467 ::: fax +39 06 570 55188 - 

[online]. Rome. Updated. [Cited ].