Trait completeness | 88% |
Total data | 286 |
References | 47 |
Author: Fabrice Téletchéa
License: All rights reserved
Trait id | Trait | Primary data | Secondary Data | References |
---|---|---|---|---|
1 | Oocyte diameter | 1.5 | 1.5 mm | Bruslé and Quignard, 2001 |
1 | Oocyte diameter | 1.6-2 [Not precised] | 1.8 mm | Internet, 2005 |
1 | Oocyte diameter | 0.83-1.16 [First batch] to 0.53-0.73 [Second batch] | 0.99 mm | Sokolova, 1990 |
1 | Oocyte diameter | 1.5-2 | 1.75 mm | Olivier, 2001 |
1 | Oocyte diameter | 1.62-1.82 [Mature eggs] | 1.72 mm | Backiel and Zawiska, 1968 |
1 | Oocyte diameter | Ripe, freshly stripped eggs were yellow-gray in colour and their average size before the activation and swelling was 1.10 mm | 1.1 mm | Penaz and Gajdusek, 1979 |
1 | Oocyte diameter | Troploplasmatic growth oocytes laid on spawning grounds have a diameter of 0.8 to 1.60 mm and weight from 0.75 to 1.25 mg. Also said that mature oocytes, of diameter 0.95-1.60 mm and weight 0.61-0.93 mg are laid during the ovulation | 1.27 mm | Brylinska and Boron, 2004 |
2 | Egg size after water-hardening | Average 2.1 [After swelling] | 2.1 mm | Backiel and Zawiska, 1968 |
2 | Egg size after water-hardening | 1.64 ± 0.04, n=52 [Eggs stripped from mature females, fertilized and incubated in water: hydrated eggs] | 1.64 mm | Bonislawska et al, 2001 |
2 | Egg size after water-hardening | The formation of perivitelline space ended approximatively at the end of this step when the average egg diameter increased 1.64 times, i.e., to 1.80 mm | 1.8 mm | Penaz and Gajdusek, 1979 |
2 | Egg size after water-hardening | Perivitelline liquid of high osmotic pressure absorbs water very rapidly; the eggs becomes hard and attains its final shape and size, the diameter being 1.57 to 2.30 mm | 2.3 mm | Brylinska and Boron, 2004 |
3 | Egg Buoyancy | Demersal | Demersal | Bruslé and Quignard, 2001 |
3 | Egg Buoyancy | Demersal | Demersal | Kunz, 2004 |
4 | Egg adhesiveness | Due to their adhesive membrane, eggs stick to plants | Adhesive | Sidorova, 2005 |
4 | Egg adhesiveness | Eggs stick to plants | Adhesive | Bruslé and Quignard, 2001 |
4 | Egg adhesiveness | Adhesive [Macrophytes, roots] | Adhesive | Olivier, 2001 |
4 | Egg adhesiveness | Adhesive [Adhere and develop on plants] | Adhesive | Backiel and Zawiska, 1968 |
4 | Egg adhesiveness | Adhesive | Adhesive | Mann, 1996 |
4 | Egg adhesiveness | Adhesive | Adhesive | Kunz, 2004 |
4 | Egg adhesiveness | External layers became highly sticky | Adhesive | Penaz and Gajdusek, 1979 |
4 | Egg adhesiveness | Egg surface is covered with zona radiata with filaments of the follicular membrane, which breaks during the ovulation. They secrete a sticky fluid (villis) which attaches the egg to the substrate, most frequently on water plants, where they remain until hatching | Adhesive | Brylinska and Boron, 2004 |
4 | Egg adhesiveness | Fish eggs were fertilized artificially and incubated by being attached to glass plates put in containers | Adhesive | Gerasimov and Stolbunov, 2007 |
5 | Incubation time | 6-6.5 in natural conditions | 6.25 days | Sidorova, 2005 |
5 | Incubation time | 3-12 [9 at 20°C, 10 at 18°C] | 7.5 days | Bruslé and Quignard, 2001 |
5 | Incubation time | 9 [14.2°] | 9.0 days | Diamond, 1985 |
5 | Incubation time | 4-8 up to 11 [At 11°C] | 6.0 days | Backiel and Zawiska, 1968 |
5 | Incubation time | 8-12 [9.8°C] to 3.2 [16.2°C] | 10.0 days | Herzig and Winkler, 1986 |
5 | Incubation time | 64-78 hours at 20°C | 71.0 days | Penaz and Gajdusek, 1979 |
5 | Incubation time | Increase in temperature from 11.2 to 23°C reduces the number of days from 12.5 to 3 | 11.2 days | Brylinska and Boron, 2004 |
5 | Incubation time | The hatch took place after seven days of incubation (at 13-15°C) | 14.0 days | Gerasimov and Stolbunov, 2007 |
5 | Incubation time | Based on graph => 220 hours [at 15°C] and 100 hours [at 25°C]. Regression equation for 50% of hatched embryos was Y = 910.1 - 65.88X + 1.318 X² (R² = 0.994) | 220.0 days | Kucharczyk et al, 1997 |
6 | Temperature for incubation | 16-20 are the optimum temperature [Most eggs perish at a temperature below 6°C, and a temperature up to 25.6°C results in early hatching of undevelopped prelarvae] | 18.0 °C | Sidorova, 2005 |
6 | Temperature for incubation | 18-20 | 19.0 °C | Bruslé and Quignard, 2001 |
6 | Temperature for incubation | 20 | 20.0 °C | Kucharczyk et al, 1998 |
6 | Temperature for incubation | Optimum: 14-15, varie from 11-23 [At 6: considerable losses, and 28 is lethal] | 14.5 °C | Backiel and Zawiska, 1968 |
6 | Temperature for incubation | 12.6-18 for embryonic develoment, 6-26 range in which normal development occurs and < 4 lower lethal T°C and > 32 for upper lethal temperature | 15.3 °C | Herzig and Winkler, 1986 |
6 | Temperature for incubation | Incubated at 19-20°C | 19.5 °C | Kucharczyk et al, 1997 |
6 | Temperature for incubation | Reared at a constant temperature of 20°C | 20.0 °C | Penaz and Gajdusek, 1979 |
6 | Temperature for incubation | Embryos from female bream (both fertilized with males of bream and white bream) were kept at 10-15°C, and embryos from female wite bream (both fertilized with males of bream and white bream) at 15-17°C, which corresponded to the water temperature at their natural spawning grounds | 12.5 °C | Vetemaa et al, 2008 |
6 | Temperature for incubation | Water temperature corresponding to its value at the natural spawning grounds (13-15°C) | 14.0 °C | Gerasimov and Stolbunov, 2007 |
6 | Temperature for incubation | The upper lethal temperature of embryonic development is approximately >32°C in the common bream | 32.0 °C | Nzau Matondo et al, 2007 |
6 | Temperature for incubation | Hatching success higher than 90% for bream from Kortowskie Lake was observed at the temperature of 21.1°C, whereas for bream from Lake Mondsee (Austria) it was in the temperature range of 15.1 and 16.2 | 21.1 °C | Kucharczyk et al, 1997 |
6 | Temperature for incubation | At 20-21°C, which was found as an optimal temperature for bream embryonic development | 20.5 °C | Kucharczyk et al, 2005 |
7 | Degree-days for incubation | 180.0 | 180.0 °C * day | Bruslé and Quignard, 2001 |
7 | Degree-days for incubation | 130.0 | 130.0 °C * day | Diamond, 1985 |
7 | Degree-days for incubation | 110-120 [135-145 hours at 20°C] | 115.0 °C * day | Olivier, 2001 |
7 | Degree-days for incubation | 60-120 | 90.0 °C * day | Backiel and Zawiska, 1968 |
7 | Degree-days for incubation | 41-49 [Effective day-degrees] | 45.0 °C * day | Kamler, 2002 |
7 | Degree-days for incubation | The motility of embryos inside the shells increased and the first embryos hatched 64 hours from the beginning of development at a water temperature of 20°C, i.e. 1280 hours degree, within the following 14 hours most of the embryos hatched | 64.0 °C * day | Penaz and Gajdusek, 1979 |
7 | Degree-days for incubation | Increase in temperature from 11.2 to 23°C reduces the number of days from 12.5 to 3 and degree-days from 144 to 56 | 11.2 °C * day | Brylinska and Boron, 2004 |
7 | Degree-days for incubation | The hatch took place after seven days of incubation (at 13-15°C) | 14.0 °C * day | Gerasimov and Stolbunov, 2007 |
7 | Degree-days for incubation | The incubation time to mass hatching was 90-100 degree-days (D°) | 95.0 °C * day | Kucharczyk et al, 2005 |
Trait id | Trait | Primary Data | Secondary Data | References |
---|---|---|---|---|
8 | Initial larval size | 4.8 | 4.8 mm | Bruslé and Quignard, 2001 |
8 | Initial larval size | 6.3 | 6.3 mm | Olivier, 2001 |
8 | Initial larval size | 4.57-5.30 | 4.94 mm | Backiel and Zawiska, 1968 |
8 | Initial larval size | Their average total length at hatching was 4.55 | 4.55 mm | Penaz and Gajdusek, 1979 |
8 | Initial larval size | Size at hatching ranges from 4.5-5.2 | 4.85 mm | Brylinska and Boron, 2004 |
9 | Larvae behaviour | Remain fixed to plants until the full resorption of yolk sac | Demersal | Bruslé and Quignard, 2001 |
9 | Larvae behaviour | Remain fixed to plants until the full resorption of yolk sac [TL of 7.6-8.4] | Demersal | Olivier, 2001 |
9 | Larvae behaviour | Larvae motionless, attached to vegetation or resting on bottom. Feed only on yolk | Demersal | Backiel and Zawiska, 1968 |
9 | Larvae behaviour | The hatched embryos mostly rested in a passive way on the bottom and only some of them hung themselves by their sticky glands onto walls or onto submerged silon threads; under natural conditions, the embryos stuck themselves onto submerged plants | Demersal | Penaz and Gajdusek, 1979 |
9 | Larvae behaviour | Eleutheroembryos hangs attached to plants or lies on the bottom. | Demersal | Brylinska and Boron, 2004 |
10 | Reaction to light | Larvae are intially photophobic | Photophobic | Mann, 1996 |
10 | Reaction to light | At a size of 5.1 to 6.2 mm, the embryos remained passive and typical "hanging up" by means of sticky glands of walls and submerged objects reached its maximum in this step. From time to time, the embryos wriggled up to the surface and thereafter slowly sank in a passive way. They were indifferent to light and did not seek shade or cover | Photopositive | Penaz and Gajdusek, 1979 |
11 | Temperature during larval development | 16-25 | 20.5 °C | Sidorova, 2005 |
11 | Temperature during larval development | 13.5-34.0 without abnormalities | 23.75 °C | Kucharczyk et al, 1998 |
11 | Temperature during larval development | 17-20 | 18.5 °C | Backiel and Zawiska, 1968 |
11 | Temperature during larval development | 16°C [Reared conditions] | 16.0 °C | Mooij, 1989 |
11 | Temperature during larval development | 20.0 | 20.0 °C | Keckeis and Schiemer, 1992 |
11 | Temperature during larval development | Reared at 19.5-20.5 | 20.0 °C | Penaz and Gajdusek, 1979 |
11 | Temperature during larval development | Optimum temperatures for larval growth (expressed as Relative growth rate: RGR, %d): 22-31°C | 26.5 °C | Wolnicki, 2005 |
11 | Temperature during larval development | Water temperature of the lake varied from 17.1 to 21°C (19°C average) during the experimental period (in a lake) | 17.1 °C | Ziliukiene, 2005 |
11 | Temperature during larval development | Water temperature in nature 12-19°C for the first six days after hatching | 15.5 °C | Brylinska and Boron, 2004 |
11 | Temperature during larval development | In all aquaria constant temperatures of 20 ± 0.5°C | 20.0 °C | Gerasimov and Stolbunov, 2007 |
11 | Temperature during larval development | Fastest growth of bream larvae (weight and length) was observed at a temperature of 27.9°C; the slowest growth was at 13.5°C. Fish reared at the highest temperature (34.0°C) grew much more slowly than those at 27.9°C, showing high weight and length variation. Lowest mortality was observed at 27.9°C; the highest was as 34°C. | 27.9 °C | Kucharczyk et al, 1997 |
13 | Full yolk-sac resorption | 120-140 [6-8 days at 17-20°C] | 130.0 °C * day | Backiel and Zawiska, 1968 |
13 | Full yolk-sac resorption | A complete resorption of the yolk-sac characterizing the beginning of this step took place at the average length of larve L= 7.7 to 7.9 mm on the 7th to the 8 th of development, i.e. 4-5 after hatching | 4.5 °C * day | Penaz and Gajdusek, 1979 |
13 | Full yolk-sac resorption | Bream larvae, the TL of which was 8.2 mm, switched completely to exogenous food | 8.2 °C * day | Ziliukiene, 2005 |
13 | Full yolk-sac resorption | 8-10 days after hatching, reserves of the yolk sac have been used. | 9.0 °C * day | Brylinska and Boron, 2004 |
14 | Onset of exogeneous feeding | 120-140 [6-8 days at 17-20°C] | 130.0 °C * day | Backiel and Zawiska, 1968 |
14 | Onset of exogeneous feeding | During the 6th of development, i.e. the 3rd after hatching, most individuals began to ingest exogeneous food. Their average total length was 6.6 mm | 6.0 °C * day | Penaz and Gajdusek, 1979 |
14 | Onset of exogeneous feeding | The cages were stocked with 6-day-old bream larvae that had just graduated to the mixed feeding stage. Fish TL was 7.9-8.1 mm (average 8.0 mm) and the body weight 1.8 mh. Larvae of this length still retained the yolk sac | 8.0 °C * day | Ziliukiene, 2005 |
14 | Onset of exogeneous feeding | After 5-6 days at 12-19°C, noticeably diminished yolk sac. Feed on yolk and some rotifers | 5.5 °C * day | Brylinska and Boron, 2004 |
Trait id | Trait | Primary Data | Secondary Data | References |
---|---|---|---|---|
15 | Age at sexual maturity | 3-4 [Southern Europe], 6-10 [Nothern Europe] | 3.5 year | Backiel and Zawiska, 1968 |
15 | Age at sexual maturity | Fish of 4+ to 15+ took part in spawning. The bulk of spawning females was 9+ | 4.0 year | Shestopalova, 1978 |
15 | Age at sexual maturity | Female bream attain maturity in their sixth year of life (V+) | 6.0 year | Cowx,1983 |
15 | Age at sexual maturity | 3 [Rarely 2] | 3.0 year | Sokolova, 1990 |
15 | Age at sexual maturity | 4-6 [Both sex] | 5.0 year | Molls, 1999 |
15 | Age at sexual maturity | 3-4 [Southern Europe], 5-7 [Nothern Europe] | 3.5 year | Bruslé and Quignard, 2001 |
15 | Age at sexual maturity | Age of sexual maturation varies from 2 to 11 years to population. | 2.0 year | Brylinska and Boron, 2004 |
15 | Age at sexual maturity | 3-4 [Mass maturation, but rarely at 2] | 3.5 year | Sidorova, 2005 |
15 | Age at sexual maturity | 4-6 [Not specified] | 5.0 year | Environment agency, ??? |
15 | Age at sexual maturity | Female breams reach sexual maturity in Vortsjärv at (6)7-10(11) years old | 8.5 year | Noges and Järvet, 2005 |
15 | Age at sexual maturity | Bream females in Lake Sniardwy attain sexual maturity at the age of six, seven years […] It may be concluded that 6 and 7-years old females spawned for the first or second time in their life | 6.0 year | Kopiejewska, 1989 |
15 | Age at sexual maturity | Other studies: 50% of the females matured having attained TL = 39 cm (SL= 30.5 cm) at the age of 8 years. […] Bream inhabiting the Rybinsk reservoir on the Volga to be sexually mature when older than 7 years, when 9.3% of the individuals were mature, at the average length of 27.4 cm. At the age of 9 years, almost half (48.1%) of all the individuals were mature, at the average length of 32.0 cm. All the bream (100%) were mature as last as in their 13th year of life, having attained a mean length of 38.4 cm | 50.0 year | Neja and Kompowski, 2001 |
16 | Length at sexual maturity | 25-30 [Full range 12-30] | 27.5 cm | Backiel and Zawiska, 1968 |
16 | Length at sexual maturity | Above 31 | 31.0 cm | Shestopalova, 1978 |
16 | Length at sexual maturity | Mean of 26.4 [Fork length] | 26.4 cm | Cowx,1983 |
16 | Length at sexual maturity | 24.0-39.4 | 31.7 cm | Sokolova, 1990 |
16 | Length at sexual maturity | 32.9 ± 0.39 mean with n =122 [Vary from 25.0-43.0] | 32.9 cm | Poncin et al, 1996 |
16 | Length at sexual maturity | No mature bream ware found at Lt < 35 cm | 35.0 cm | Molls, 1999 |
16 | Length at sexual maturity | 18-24 [Sex not precised] | 21.0 cm | Bruslé and Quignard, 2001 |
16 | Length at sexual maturity | 24.5-27.7 [Rarely at 18-19] | 26.1 cm | Sidorova, 2005 |
16 | Length at sexual maturity | Female breams reach sexual maturity in Vortsjärv at 26-36 cm | 31.0 cm | Noges and Järvet, 2005 |
16 | Length at sexual maturity | All the individuals measuring up to 12 cm were immature (Maier gonad maturity scale stage I). The smallest length of mature bream (Maier scale stage II) was 13 cm. At the length of 20 cm, 50% of the population were mature. Thus that length should be regarded as the length at first maturity. All the individuals measuring 30 cm and more were mature. [...] Other studies, on average 26.0-33.5 cm in females | 29.75 cm | Neja and Kompowski, 2001 |
17 | Weight at sexual maturity | 0.25-0.4 [Both sex !] | 0.33 kg | Backiel and Zawiska, 1968 |
17 | Weight at sexual maturity | 0.335-1.590 | 0.96 kg | Sokolova, 1990 |
18 | Female sexual dimorphism | Compared to males, females have their breeding tubercles poorer developped, occupying a much smaller area | Present | Witkowski and Rogowska, 1991 |
19 | Relative fecundity | 30-40 | 35.0 thousand eggs/kg | Spillmann, 1961 |
19 | Relative fecundity | Mean range from 113-260 [Complete range of 97-200, not indicated for all populations] | 186.5 thousand eggs/kg | Backiel and Zawiska, 1968 |
19 | Relative fecundity | 381.3 is the mean [Range 94.0 to 600.3], calculated without viscera, i.e. IOP | 381.3 thousand eggs/kg | Sokolova, 1990 |
19 | Relative fecundity | 30-40 | 35.0 thousand eggs/kg | Bruslé and Quignard, 2001 |
19 | Relative fecundity | 50 | 50.0 thousand eggs/kg | Kunz, 2004 |
19 | Relative fecundity | It ranges in different bream populations from 12 to 352 thousands eggs per 1 kg of body weight. The highest variability of relative fecundity was found among the smallest females. The variability decreased with fish size approaching the average level of 150 to 200 thousand eggs per 1 kg of body weight. For example in lakes: 202.1-304.0 [Wierzchul],163.5-210.5 [Wenecja], 40.0-230.0 [Bershty] and in rivers 133.1-236.9 [Vistula], 79-183 [Volga] | 253.05 thousand eggs/kg | Brylinska and Boron, 2004 |
19 | Relative fecundity | 116-327 | 221.5 thousand eggs/kg | Sidorova, 2005 |
19 | Relative fecundity | 30-40 | 35.0 thousand eggs/kg | Internet, 2005 |
19 | Relative fecundity | 150-300 | 225.0 thousand eggs/kg | Environment agency, ??? |
20 | Absolute fecundity | Mean of 92-218 [2-941 are the highest variation] | 155.0 thousand eggs | Backiel and Zawiska, 1968 |
20 | Absolute fecundity | Range from 68.6 to 450.0 [Average of 218.3] | 68.6 thousand eggs | Shestopalova, 1978 |
20 | Absolute fecundity | Average 234.2 [Range 66 to 605.6] | 234.2 thousand eggs | Sokolova, 1990 |
20 | Absolute fecundity | 49-150 and up to 580 for larger female | 99.5 thousand eggs | Olivier, 2001 |
20 | Absolute fecundity | 300 [For a female of 70 cm] | 300.0 thousand eggs | Bruslé and Quignard, 2001 |
20 | Absolute fecundity | Number of ooctyes of trophoplasmatic growth maturing in a year is determined as individual fecundity, which varies from 5.3 to 782.2 000 eggs in different populations. For example in lakes: 80.2-583.4 [Wierzchul], 65.0-410.8 [Samozero], 76.0-293.0 [Ubinskoe] and in rivers 53.3-483.5 [Vistula], 76-651 [Volga] | 331.8 thousand eggs | Brylinska and Boron, 2004 |
20 | Absolute fecundity | Average is 120-130 [Vary from 317-503.7 for females ages 3-11 years] | 125.0 thousand eggs | Sidorova, 2005 |
20 | Absolute fecundity | Mean of 102.0 (range 20.8-309.6) n = 24 in Kortowski Lake and mean of 182.2 (range 46.4-321.3) n = 30 in Blanki Lake | 165.2 thousand eggs | Kopiejewska, 1993 |
21 | Oocyte development | Group-synchronous | Group-synchronous | Rinchard, 1996 |
21 | Oocyte development | In females with batch spawning asynchronous growth and maturation of the oocytes is noticeable early in ovary development and most frequently during ovaries stage IV. In various A. brama populations, 0.0 to 80.4 % of the females were characterized by asynchronous development of trophoplasmatic growth oocytes. Thefirst oocytes batch is larger, their diameter is 0.8-1.3 mm. The second batch (after 14 to 30 days) is smaller and oocyte diameter is 0.4-0.8 mm. The ratio of oocytenumbers in the second batch to their number in the first batch, ranges from 19.6 to 40.8%. In stunded A.brama from Lake Jaskhan (Turkmenia)three oocyte populations were observed in an ovary but because high water temperatures reaching 30-33°C and food deficiency these oocytes were resorbed. In the Aral Sea, a subspecies Abramis brama orientalis was, according to many authors, charactetised by an asynchronous oocyte development and batch feucndity, but changes in the environment of the Aral Sea have induced single batch spawning. The sub-species of A. brama, introduced into Siberian waters, maintained single -batch spawning. The proportion of females with batch spawning increases in A. brama population southwards in the range in comparison with centrally located waters. Northern A. brama spawn in one portion only | Asynchronous | Brylinska and Boron, 2004 |
22 | Onset of oogenesis | In autumn when water temperature drops below 12-10°C, part of oocytes enters further meiosis stages, and vacuolization commences in the cytoplams - stage III of ovaries endogenous vitellogenesis | ['October', 'November', 'December'] | Brylinska and Boron, 2004 |
22 | Onset of oogenesis | From August onwards there is a constant increase in the coefficient | ['August'] | Kompowski, 1982 |
22 | Onset of oogenesis | Vitellogenesis in the bream ovaries commenced in August in both lakes | ['August'] | Kopiejewska, 1989 |
23 | Intensifying oogenesis activity | Most stages of gonad maturation take place in spring | ['April', 'May', 'June'] | Fredrich et al, 2003 |
23 | Intensifying oogenesis activity | The coefficient attains its maximal values in April and May, directly before spawning | ['April', 'May'] | Kompowski, 1982 |
24 | Maximum GSI value | Mean of 16.8-21 [Up to 23.8] | 18.9 percent | Backiel and Zawiska, 1968 |
24 | Maximum GSI value | Up to 23.3 [Calculated without viscera] | 23.3 percent | Sokolova, 1990 |
24 | Maximum GSI value | GSI observed in different areas: 16.3 [Drukshya], 33-43 [Kama], 8.3-18.5 [Volga], 5.5-28.4 [Goczalkowice] | 38.0 percent | Brylinska and Boron, 2004 |
24 | Maximum GSI value | The lowest and highest mean coefficients in males were 2.141 (June 1976, Lake Dabie) and 24.532 (late May, 1976, Regalicia) | 2.14 percent | Kompowski, 1982 |
24 | Maximum GSI value | In spring, the ovaries accouned for 0.2-24.7% of the total body weight | 12.45 percent | Neja and Kompowski, 2001 |
26 | Resting period | About one month | No data | Witkowski et al, 1989 |
26 | Resting period | The minimum values are found in June and July, which corresponds to a resting period of gonads after spawning | 3.0 months | Kompowski, 1982 |
26 | Resting period | GSI decreases after spawning to 0.88-3.1% in females with single batch spawning, and to 4.6-6.2% in females spawning in batches. In the latter females, the ovary reaches 10-16.3% of body weight again within 14-30 days | 1.99 months | Brylinska and Boron, 2004 |
Trait id | Trait | Primary Data | Secondary Data | References |
---|---|---|---|---|
27 | Age at sexual maturity | 2-3 | 2.5 years | Sidorova, 2005 |
27 | Age at sexual maturity | 2-3 | 2.5 years | Sokolova, 1990 |
27 | Age at sexual maturity | 2-3 [Southern region] to 6-8 [Nothern region] | 2.5 years | Backiel and Zawiska, 1968 |
27 | Age at sexual maturity | Fish of 4+ to 15+ took part in spawning. The bulk of spawning males was 5+ to 8+ | 4.0 years | Shestopalova, 1978 |
27 | Age at sexual maturity | 4-6 [Both sex] | 5.0 years | Molls, 1999 |
27 | Age at sexual maturity | 4-6 [Not specified] | 5.0 years | Environment agency, ??? |
27 | Age at sexual maturity | Male attain maturity in their seventh year (VI+) | 7.0 years | Cowx,1983 |
27 | Age at sexual maturity | Males attain sexual maturity one to two years earlier than females | 1.0 years | Brylinska and Boron, 2004 |
27 | Age at sexual maturity | Male breams reach sexual maturity in Vortsjärv at the age of (6)7-9(10) years | 8.0 years | Noges and Järvet, 2005 |
27 | Age at sexual maturity | Other studies: 50% of the males matured having attained TL = 35.5 cm (SL= 27.7 cm) at the age of 7 years. […] Bream inhabiting the Rybinsk reservoir on the Volga to be sexually mature when older than 7 years, when 9.3% of the individuals were mature, at the average length of 27.4 cm. At the age of 9 years, almost half (48.1%) of all the individuals were mature, at the average length of 32.0 cm. All the bream (100%) were mature as last as in their 13th year of life, having attained a mean length of 38.4 cm | 50.0 years | Neja and Kompowski, 2001 |
28 | Length at sexual maturity | 23.0-35.6 | 29.3 cm | Sokolova, 1990 |
28 | Length at sexual maturity | 25-30 [Full range 9-30] | 27.5 cm | Backiel and Zawiska, 1968 |
28 | Length at sexual maturity | No mature bream ware found at Lt< 35 cm | 35.0 cm | Molls, 1999 |
28 | Length at sexual maturity | 27.7 [Fork length] | 27.7 cm | Cowx,1983 |
28 | Length at sexual maturity | Male breams reach sexual maturity in Vortsjärv 25-32 cm long | 28.5 cm | Noges and Järvet, 2005 |
28 | Length at sexual maturity | All the individuals measuring up to 12 cm were immature (Maier gonad maturity scale stage I). The smallest length of mature bream (Maier scale stage II) was 13 cm. At the length of 20 cm, 50% of the population were mature. Thus that length should be regarded as the length at first maturity. All the individuals measuring 30 cm and more were mature. | 12.0 cm | Neja and Kompowski, 2001 |
29 | Weight at sexual maturity | 0.260-1.104 | 0.68 kg | Sokolova, 1990 |
29 | Weight at sexual maturity | 0.25-0.4 [Full range 0.1-0.5] | 0.33 kg | Backiel and Zawiska, 1968 |
30 | Male sexual dimorphism | Nuptial tubercules on head, fins, and sides. Colors become brighter | Present | Spillmann, 1961 |
30 | Male sexual dimorphism | Territorial males are brown-yellow in colouration with tubercules | Absent | Poncin et al, 1996 |
30 | Male sexual dimorphism | Males have their breeding tubercles much more intensively developped, and larger individuals have distincly more numerous tubercles than smaller | Absent | Witkowski and Rogowska, 1991 |
30 | Male sexual dimorphism | Most authors revealed that there was no secondary sexual dimorphism or that is was very weak. Males have keratinized spawning tubercles. Tubercles appear 20-30 days before spawning, and in some males may last as long as to the autumn. Tubercles are more noticeable in older males and they extend from the fish head (large tubercles) to caudal region (small ones). They are most numerous over the head and dorsal part of the body. | Absent | Brylinska and Boron, 2004 |
33 | Maximum GSI value | Up to 6.1% [Calculated without viscera] | 6.1 percent | Sokolova, 1990 |
33 | Maximum GSI value | Mean of 2.8-3.4 [Up to 4.6] | 3.1 percent | Backiel and Zawiska, 1968 |
33 | Maximum GSI value | The lowest and highest mean coefficients in males were 0.867 (July 1976, Lake Dabie) and 4.411 (late May, 1976, Lake Dabie) | 0.87 percent | Kompowski, 1982 |
33 | Maximum GSI value | In spring, the testes accounted for up to 3.7% | 3.7 percent | Neja and Kompowski, 2001 |
Trait id | Trait | Primary Data | Secondary Data | References |
---|---|---|---|---|
36 | Spawning migration distance | Make migrations | No data | Olivier, 2001 |
36 | Spawning migration distance | Most of the population does not migrate for long distances | No data | Backiel and Zawiska, 1968 |
36 | Spawning migration distance | Localised migrations to spawning areas | No data | Environment agency, ??? |
36 | Spawning migration distance | Migrations of tagged A. brama have been observed in a number of freshwater bodies and brackish coastal waters. The longest recorded distance covered by tagged bream was 200 km from the place of release. | 200.0 km | Brylinska and Boron, 2004 |
36 | Spawning migration distance | Holobiotique migrations | No data | Agence de l'eau, |
37 | Spawning migration period | The peak run of spawners takes place through the second half of April- first ten days of May at water temperature 8-12°C | ['April', 'May'] | Sidorova, 2005 |
37 | Spawning migration period | The spring migration begins with the melting of ice on the sea, the first group strat their upstream migration at the begnning of April, while the second and larger run lasting for 15-30 days begins when the water of the river reaches 8°C | ['April', 'May', 'June'] | Backiel and Zawiska, 1968 |
37 | Spawning migration period | Bream had two distinct migration waves and at least two seperate spawning periods which resulted in distinct cohors on shore seine catches | No data | Molls, 1999 |
37 | Spawning migration period | In the spring, when water temperatue is about 10-14°C | ['April', 'May', 'June'] | Ciolac, 2004 |
37 | Spawning migration period | The bream exibited limited pre-spawning acitivty with a gradual increase of proportion of ripe individuals and low migration rate. This period was followed by the main spawning rung when the daily migration represented hundreds of individuals (13-14°C). in the same period, massive spawning of bream was recorded in the whole reservoir | No data | Hladik and Kubecka, 2003 |
37 | Spawning migration period | Semi-migratory species in some parts of its distribution in brackish waters. In the Caspian Sea, spring migrations to the Volga river delta commenced whith ice melting, but they were most intensive at a water temperature of 10-12°C | ['April', 'May', 'June'] | Brylinska and Boron, 2004 |
37 | Spawning migration period | During the upstream migration (March-June), mature roach, silver bream and common bream females were collected from natural populations in a fish pass at the Lixhe dam (Belgian River Meuse, 50°45'; 5°40'E) | ['March', 'June'] | Nzau Matondo et al, 2007 |
39 | Spawning season | May-July | ['May', 'July'] | Billard, 1997 |
39 | Spawning season | May-June | ['May', 'June'] | Spillmann, 1961 |
39 | Spawning season | Begins in early May and mass spawing occurs in mid-May | ['May'] | Sidorova, 2005 |
39 | Spawning season | Mid-May until Mid-June | ['May', 'June'] | Internet, 2005 |
39 | Spawning season | Usually May-June | ['May', 'June'] | Olivier, 2001 |
39 | Spawning season | April to June | ['April', 'May', 'June'] | Backiel and Zawiska, 1968 |
39 | Spawning season | May, 3 until June, 3 | ['May', 'June'] | Shestopalova, 1978 |
39 | Spawning season | May-June | ['May', 'June'] | Mann, 1996 |
39 | Spawning season | May-June | ['May', 'June'] | Environment agency, ??? |
39 | Spawning season | Spawning takes place during the first half of June | ['June'] | Herzig and Winkler, 1986 |
39 | Spawning season | Lake bream usually spawn in the beginning of June | ['June'] | Kucharczyk et al, 1997 |
39 | Spawning season | Spawns in spring. Spawning begins at the end of March and extends till the first half of June. In heated waters spawning may take place in winter and early spring | ['January', 'February', 'March', 'April', 'May', 'June'] | Brylinska and Boron, 2004 |
39 | Spawning season | The experiments with female bream eggs were started on 24 May (three females) and 29 May (three females) and with female white bream eggs on 5 June (four females) due to the earlier spawning of bream in Estonia […] The spawning of bream in south-east Estonia usually begins at the water temperature of c. 13°C, in most cases in the second half of May | ['May', 'June'] | Vetemaa et al, 2008 |
39 | Spawning season | Bream started to spawn 16-17 days later than roach, the median dates being 16 May for rivers and 22 May for lakes. One half of all measurements fell into a range of 16 days between 13 and 28 May. | ['May'] | Noges and Järvet, 2005 |
39 | Spawning season | Bream females in Lake Sniardwy commence spawning in May-June | ['May', 'June'] | Kopiejewska, 1989 |
39 | Spawning season | In the Trent, the main hatching period for bream occurred around the second week of June, with the majority of hatching complete by mid-July | ['June', 'July'] | Nunn et al, 2007 |
39 | Spawning season | May and June on bream spawning grounds in the Kortowskie Lake | ['May', 'June'] | Kucharczyk et al, 2005 |
40 | Spawning period duration | 3 to 40 days [During warm and calm weather, bream spawn in masses in a short time (2-3 days) but longer under bad conditions, males are ready to spawn first and remain longer on the spawning grounds] | 2.5 weeks | Backiel and Zawiska, 1968 |
40 | Spawning period duration | 4 [Spawning was at its height between May 10 and 20] | 4.0 weeks | Shestopalova, 1978 |
40 | Spawning period duration | Adult fish may remain in the river for several weeks or months and participate in multiple spawnings | No data | Hladik and Kubecka, 2003 |
40 | Spawning period duration | Spawning may take place in phases or extend over longer periods, from 3 to some tens of days. One to three even more spawning phases were observed in different populations | 3.0 weeks | Brylinska and Boron, 2004 |
40 | Spawning period duration | The duration of the spawning period may depend on the latitude; in the USSR for instance the bream spawning season varies from 58 to 60 days in the North to 16 days in the Volga delta. | 58.0 weeks | Billard, 1981-1982 |
40 | Spawning period duration | Median values (upper and lower quartiles in parenthesis) => 3 (2-6) in lakes and 2 (1-3) in rivers | 4.0 weeks | Noges and Järvet, 2005 |
41 | Spawning temperature | 8-25 | 16.5 °C | Sidorova, 2005 |
41 | Spawning temperature | 13-14 | 13.5 °C | Hladik and Kubecka, 2003 |
41 | Spawning temperature | 14-17.2 | 15.6 °C | Diamond, 1985 |
41 | Spawning temperature | Above 12°C | 12.0 °C | Billard, 1997 |
41 | Spawning temperature | 13-20 | 16.5 °C | Olivier, 2001 |
41 | Spawning temperature | Most common is 16-18 [12-13 is the lowest temperature, highest being 27°C] | 17.0 °C | Backiel and Zawiska, 1968 |
41 | Spawning temperature | 16-18, temperature observed for the peak of spawning | 17.0 °C | Shestopalova, 1978 |
41 | Spawning temperature | 12-20 | 16.0 °C | Mann, 1996 |
41 | Spawning temperature | About 15 | 15.0 °C | Kennedy, 1969 |
41 | Spawning temperature | 12-20 | 16.0 °C | Environment agency, ??? |
41 | Spawning temperature | When temperatures are between 15°C and 18°C | 15.0 °C | Herzig and Winkler, 1986 |
41 | Spawning temperature | Our five years observations showed that the temperature during the spawning time (May and June) of bream fluctuated on spawning grounds between 13.5 and 26.5°C. On the other hand, when temperatures decreased below 20°C bream discontinuted spawning and left the spawning grounds. [...] Bream spawn at different temperatures depending on location: in the Volga River, spawning occurs between 10.0 and 13.5°C, in the Don River between 23 and 24°C, in Finland between 18 and 19°C, and in Masurian Lakes, Poland, bream spawn at about 17°C. In Kortowskie Lake, where spawners were caught, bream spawn at 20-21°C | 20.5 °C | Kucharczyk et al, 1997 |
41 | Spawning temperature | Range of temperature is from 9 to 20.6°C, while during phase II and later from 13 to 27°C | 9.0 °C | Brylinska and Boron, 2004 |
41 | Spawning temperature | Above 13°C | 13.0 °C | Vetemaa et al, 2008 |
41 | Spawning temperature | For bream, the typical range is 12-20°C, while extremes may reach 8 and 24°C […] The median water temperature measured in large lakes at the beginning of spawning in bream in rivers respective of lakes (correspondinglyn 12.9 and 13.3°C) was not significantly different [...] Spawning starts at water temperature of 13-14°C and reaches its peak at 16-19°C | 16.0 °C | Noges and Järvet, 2005 |
41 | Spawning temperature | Our five years observations showed that the temperature during the spawning time (May and June) of bream fluctuated on spawning grounds between 13.5 and 26.5°C | 13.5 °C | Kucharczyk et al, 2005 |
42 | Spawning water type | In border of river [current about 30 cm/s] | Flowing or turbulent water | Bruslé and Quignard, 2001 |
42 | Spawning water type | Typical spawning sites are temporarily flooded water bodies, low-floodplains and lakes | Stagnant water | Sidorova, 2005 |
42 | Spawning water type | Near the shoreline | Stagnant water | Spillmann, 1961 |
42 | Spawning water type | Weed beds | Stagnant water | Internet, 2005 |
42 | Spawning water type | In border of river | No category | Olivier, 2001 |
42 | Spawning water type | Sheltered places, where the water is either still or the current is weak | Flowing or turbulent water | Backiel and Zawiska, 1968 |
42 | Spawning water type | Oxbows, with vegetation adults remain in that site after spawning | Stagnant water | Molls, 1999 |
42 | Spawning water type | Current velocity < 20 cm/s | Flowing or turbulent water | Mann, 1996 |
42 | Spawning water type | Some species seem to be strickly dependent on the tributary zone as they were never observed reproducing in the reservoir (asp, bleak, chub and white bream), while others are facultative tributary users (roach, bream, pike, perch, rudd). Generalists: fish spawning in suitable places both inthe tributary and the reservoir: bream, roach, perh, pike and ruffe | No category | Hladik and Kubecka, 2003 |
42 | Spawning water type | Consist of shallow areas, overgrown with vegetation and protected from winds, or old river beds connected with the main course, river mouths areas, lake shores. May also spawn on flooded meadows. | Stagnant water | Brylinska and Boron, 2004 |
42 | Spawning water type | Spawning grounds of bream in Estonia as relatively shallow places on water plants, e.g. dead Carex sp. | Stagnant water | Vetemaa et al, 2008 |
42 | Spawning water type | The spawning grounds of A. brama are the shallow waters of the lake where there is dense vegetation | Stagnant water | Herzig and Winkler, 1986 |
43 | Spawning depth | Shallow waters : 20-80 cm | 50.0 m | Bruslé and Quignard, 2001 |
43 | Spawning depth | Near the surface | No data | Spillmann, 1961 |
43 | Spawning depth | Shallow waters | No data | Internet, 2005 |
43 | Spawning depth | Water depth ranges between 25 and 50 cm | 0.375 m | Poncin et al, 1996 |
43 | Spawning depth | In shallow waters < 30 cm | 0.3 m | Diamond, 1985 |
43 | Spawning depth | 0.4-2 m | 1.2 m | Olivier, 2001 |
43 | Spawning depth | Most common is 20 to 80 cm [From 9 cm to 17 m] | 17.0 m | Backiel and Zawiska, 1968 |
43 | Spawning depth | Depth of spawning grounds are usually to 0.5-1.5 m. Besides shallow, shore areas, A. brama may also spawn on more deeper grounds, 1.5-5.0 m, or even on quite deep grounds , from 6 to 20 meters in depth at a pressure about 3 atm | 1.0 m | Brylinska and Boron, 2004 |
43 | Spawning depth | Spawning grounds of bream in Estonia as relatively shallow places | No data | Vetemaa et al, 2008 |
43 | Spawning depth | Shallow waters | No data | Herzig and Winkler, 1986 |
44 | Spawning substrate | Phytophilic : eggs are deposited on aquatic plants as well as drifting remains of aquatic vegetation | Phytophils | Sidorova, 2005 |
44 | Spawning substrate | On plants but also pebbles | Phytophils | Spillmann, 1961 |
44 | Spawning substrate | Aquatic plants : phytophil or phyto-lithophyl | Phytophils | Bruslé and Quignard, 2001 |
44 | Spawning substrate | Phytophilous : roots of alder, willow trees and aquatic plants | Phytophils | Poncin et al, 1996 |
44 | Spawning substrate | Only spawned on adventitious roots of willow | No category | Diamond, 1985 |
44 | Spawning substrate | Plants | Phytophils | Billard, 1997 |
44 | Spawning substrate | Litho-phytophil | Phytophils | Olivier, 2001 |
44 | Spawning substrate | Generally phytophilous: flooded land plants, remains of previous year's aquatic vegetation, tree leaves, stems, and roots of emergent plants, algae, submerged macophytes | Phytophils | Backiel and Zawiska, 1968 |
44 | Spawning substrate | Eggs adhere to sumerged plants, bit other substrata are utilised if suitable plants are absent | Phytophils | Mann, 1996 |
44 | Spawning substrate | Deposit their eggs on plants | Phytophils | Kennedy, 1969 |
44 | Spawning substrate | Dense weed, rarely on gravel | Lithophils | Environment agency, ??? |
44 | Spawning substrate | Phytolithophil | Lithophils | Wolter and Vilcinskas, 1997 |
44 | Spawning substrate | Phyto-lithophils | Lithophils | Balon, 1975 |
44 | Spawning substrate | Under natural conditions of bream spawning, when the bottom is covered with mud and oxygen content is decreased, this adapatation enables an ecologically favourable incubation because the eggs stick to aquatic plants and others substrates | Phytophils | Penaz and Gajdusek, 1979 |
44 | Spawning substrate | It is a non-obligatory phytophilic plant spawner | Phytophils | Brylinska and Boron, 2004 |
44 | Spawning substrate | On water plants, e.g. dead Carex sp. | Phytophils | Vetemaa et al, 2008 |
45 | Spawning site preparation | No nest, but some males are territorial and very aggressive and others are non-territorial | Open water/substratum scatter | Poncin et al, 1996 |
45 | Spawning site preparation | Males are territorial | No category | Olivier, 2001 |
45 | Spawning site preparation | No, eggs are deposited on plants nut male defends its teritory and when another male appears there is intensive slashing | Susbtrate chooser | Backiel and Zawiska, 1968 |
45 | Spawning site preparation | Open substratum spawners | Open water/substratum scatter | Mann, 1996 |
45 | Spawning site preparation | Open substratum spawner | Open water/substratum scatter | Balon, 1975 |
45 | Spawning site preparation | Territorial males | No category | Ah-King et al, 2004 |
46 | Nycthemeral period of oviposition | Night | Night | Spillmann, 1961 |
46 | Nycthemeral period of oviposition | During the day but decrease slighy during the afternoon | Day | Poncin et al, 1996 |
46 | Nycthemeral period of oviposition | Day and night, becoming more intensive at night [Most intensive spawning last from 10.00 to 11.00 and after a break at noon from 16.00 to 17.00] | Day | Backiel and Zawiska, 1968 |
46 | Nycthemeral period of oviposition | Mass spawning has been observed in the evening, at sunset, during windless weather. In the case of strong winds, spawning occurs at night. After a break, it continues before sunrise. Also observed intensive spawning in shallow areas of the Vistula River mostly at night, another authors at high water temperatures in the afternoon or else later and hot and windless days | Day | Brylinska and Boron, 2004 |
47 | Mating system | May be considered polygamous : each male can mate successively with several females, and each female can mate simultaneously and successively with several males [One female followed by two to eight males] | Polyandry | Poncin et al, 1996 |
47 | Mating system | Male and female spawn repeatedly with different partners. Mating is therefore promiscuous | Promiscuity | Backiel and Zawiska, 1968 |
47 | Mating system | Group, communal spawning. One female and two to eight males released eggs and sperm. | Promiscuity | Ah-King et al, 2004 |
47 | Mating system | Fish pairs move around each other. A. brama females remain over a limited territory and defend it against other fish. Some authors state the A. brama spawn in small groups (few fish), over a limited area, and the fish taking part in spawning move from one place to another. Yet, also described that the reproductive behavior of common bream is polyandrous, mating tactics is territoarial and sneaking. | Promiscuity | Brylinska and Boron, 2004 |
48 | Spawning release | Once | Total | Rinchard, 1996 |
48 | Spawning release | Once or repeated spawning | Total | Backiel and Zawiska, 1968 |
48 | Spawning release | Several batches of eggs are released and fertilized by different males | Multiple | Poncin et al, 1996 |
48 | Spawning release | At least two batches of eggs per female | Multiple | Sokolova, 1990 |
48 | Spawning release | In most water bodies, female spawn only once a year, but there are popualtions in which females spawn twice or even three times | Total | Backiel and Zawiska, 1968 |
48 | Spawning release | In most cases, spawns once per breeding season, but it is known to spawn twice or three times especially in southern water bodies | Total | Fredrich et al, 2003 |
48 | Spawning release | Clement weather and increased temperature stimulated further spawning of this fractionally spawning species | Fractional | Hladik and Kubecka, 2003 |
48 | Spawning release | Only some females in thermally polluted waters show a tendency for batch spawning and due to en ecological stress in dam reservoirs in the first years after flooding . The proportion of females with batch spawning increases in A. brama populations southwards in the range in comparison with centrally located waters. Northern A. brama spawn in one portion only | Multiple | Brylinska and Boron, 2004 |
48 | Spawning release | Bream is a single spawner in the sense the in one individual all eggs mature synchronously […] In lake Peipsi, breams lay their eggs usully in 2-3 groups during the spawning period | Total | Noges and Järvet, 2005 |
48 | Spawning release | Adopt multiple spawning strategies, with up to three batches of eggs produced by individual fish | Multiple | Nunn et al, 2007 |
49 | Parity | Iteroparous : spawn every year [During its life cycle, it can spawn 8-9 times] | Iteroparous | Sidorova, 2005 |
49 | Parity | The spawning populations included up to height age classes | No category | Sokolova, 1990 |
49 | Parity | Many bream returned back to the reservoir after spawning while another part stayed every season in the river pools above the traps for a longer time and returned after subsequent spawning | No category | Hladik and Kubecka, 2003 |
49 | Parity | In June, July, and August, that is after spawning, the fish moved back to deeper parts or deeper water bodies, where they feed intensively. Abramis brama is a long-lived species in northern area of distribution.Age of A. brama un its southern area of distribution rarely exceeds 10 to 12 years | Semelparous | Brylinska and Boron, 2004 |
50 | Parental care | Never described in the FAO Fisheries Synopsis | No category | Backiel and Zawiska, 1968 |
50 | Parental care | Non-guarders | No care | Mann, 1996 |
50 | Parental care | None | No care | Ah-King et al, 2004 |