Trait completeness | 96% |
Total data | 349 |
References | 77 |
Author: Fabrice Téletchéa
License: All rights reserved
Trait id | Trait | Primary data | Secondary Data | References |
---|---|---|---|---|
1 | Oocyte diameter | 3.5-5 | 4.25 mm | Groot, 1996 |
1 | Oocyte diameter | 3-5 | 4.0 mm | Bruslé and Quignard, 2001 |
1 | Oocyte diameter | 3.5-4.0 [The size of the mature ova] | 3.75 mm | Henderson, 1963 |
1 | Oocyte diameter | 4 [Ovule] | 4.0 mm | Rivier, 2001 |
1 | Oocyte diameter | 3.5-5 | 4.25 mm | Fishbase, 2006 |
1 | Oocyte diameter | 3.5-5 | 4.25 mm | Scott and Crossman, 1973 |
1 | Oocyte diameter | 4.8-4.9 | 4.85 mm | Fraser, 1985 |
1 | Oocyte diameter | 3.5-5.0 [Not specified, seems to be unswollen] | 4.25 mm | Mittelbach and Persson, 1998 |
1 | Oocyte diameter | 5 [Not specified] | 5.0 mm | Coad, 2006 |
1 | Oocyte diameter | Mean 4.58 ± 0.254, range 4.1-4.9 | 4.58 mm | Bascinar and Okumus, 2004 |
1 | Oocyte diameter | 4.3 [Mean diameter of mature, fully yolked, ovarian oocyte] | 4.3 mm | Olden et al, 2006 |
1 | Oocyte diameter | The common size of mature eggs, ready to be shed, varies from 4.0 to 4.6 mm | 4.6 mm | Vladykov, 1956 |
1 | Oocyte diameter | The mean diameter of ripe ova was 4.05 | 4.05 mm | Wydoski and Cooper, 1966 |
1 | Oocyte diameter | Range: 3.59-5.46, mean 4.67 | 4.53 mm | Purtscher and Humpesch, 2006 |
1 | Oocyte diameter | Diameter of oocytes in September, mean of 3.2 for aicd lakes and 2.9 for non-acid lakes | 3.2 mm | St-Pierre and Moreau, 1986 |
2 | Egg size after water-hardening | 3.69-5.95 [Fully swollen egg, measured 1 hour after water contact] | 4.82 mm | Dlaboga et al, 1998 |
2 | Egg size after water-hardening | Ripe eggs from individual females varied in mean diameter from 3.35 to 5.0 | 3.35 mm | Wydoski and Cooper, 1966 |
2 | Egg size after water-hardening | 4.6 [Fully hardened eggs] | 4.6 mm | Penaz, 1981 |
2 | Egg size after water-hardening | Means of diameter range from 4.65 +/-0.5 to 4.80 +/-0.04 | 4.65 mm | Roche-Mayzaud et al, 1998 |
3 | Egg Buoyancy | Demersal [Deposited into a nest] | Demersal | Scott and Crossman, 1973 |
3 | Egg Buoyancy | The eggs of Salmonidae are buried in unguarded nests called 'redds' and are demersal-nonadheive | Demersal | Kunz, 2004 |
3 | Egg Buoyancy | Eggs incubate under gravel and sand in redd | Demersal | Goodyear et al, 1982 |
4 | Egg adhesiveness | Adhesive for a short period after extrusion which serves to prevent those not lodged in gravel from being washed away | Adhesive | Scott and Crossman, 1973 |
4 | Egg adhesiveness | Initially the eggs are adhesive which helps them to stick to the gravel and not be carried downstream before they are covered by the female. After they become water-hardened, the eggs lose their adhesive qaulity | Adhesive | Kerr and Grant, 1999 |
4 | Egg adhesiveness | The eggs of Salmonidae are buried in unguarded nests called 'redds' and are demersal-nonadheive | Non-Adhesive | Kunz, 2004 |
4 | Egg adhesiveness | Salmonidae, whose eggs are not sticky | Non-Adhesive | Woynarovich, 1962 |
5 | Incubation time | 75 days at 9.4°C until emergence | 75.0 days | Mirza et al, 2001 |
5 | Incubation time | 100 days at 5°C | 100.0 days | Fishbase, 2006 |
5 | Incubation time | 100 [5°C], 75 [6.1°C], 50 [10°C] | 100.0 days | Scott and Crossman, 1973 |
5 | Incubation time | About 100 in natural conditions | 100.0 days | Fraser, 1985 |
5 | Incubation time | 47 [10°C] to 165 [2.8°C] | 47.0 days | Coad, 2006 |
5 | Incubation time | 50 [Uniform temperature of 10°C], 100 days [4°C] | 50.0 days | Kerr and Grant, 1999 |
5 | Incubation time | 91.7 [5°C], 64.2 [7.5°C], 46.5 [10°C] and 34.5 [12.5°C] for 50% hatch | 91.7 days | Jensen, 1997 |
5 | Incubation time | 52 days at 7.98°C | 52.0 days | Bascinar and Okumus, 2004 |
5 | Incubation time | Hatching started on day 55, and 50% hatching occurred on day 58 | 55.0 days | Bascinar et al, 2003 |
5 | Incubation time | 109.0 [Mean time to egg hatch within the range of average post-spawning the range post-spawning water temperatures] | 109.0 days | Olden et al, 2006 |
5 | Incubation time | Estimates of the number of days required for 50% of egg to hatch: 74 [5°C], 44 [10°C], and not evaluated at 15°C [In different populations: 52-188 [At 1.4-15.4°C]] | 120.0 days | Humpesch, 1985 |
5 | Incubation time | 142.5 [1.64°C], 122 [3.02°C], 83 [5.65°C], 60 [7.86°C] and 31 [13.45°C] and numerous other examples | 142.5 days | Embody, 1934 |
5 | Incubation time | Eggs hatch in 32-165 days at 54-37°F, usually in February-March | 98.5 days | Goodyear et al, 1982 |
6 | Temperature for incubation | 6 [No hatch occurred at 18°C; The incidence of abnormalities was highest at 15°C] | 6.0 °C | Hokanson et al, 1973 |
6 | Temperature for incubation | 9.4 ± 0.19 | 9.4 °C | Mirza et al, 2001 |
6 | Temperature for incubation | 1.7-5 | 3.35 °C | Fishbase, 2006 |
6 | Temperature for incubation | 5-10 [Upper lethal temperature limit is about 11.7] | 7.5 °C | Scott and Crossman, 1973 |
6 | Temperature for incubation | 1.0-2.5 [Ambient natural temperature], 4.3-4.5 [Interstitial natural temperature] | 1.75 °C | Curry et al, 1991 |
6 | Temperature for incubation | 0.8 ± 0.3 [Natural conditions] | 0.8 °C | Bernier-Bourgault and Magnan, 2002 |
6 | Temperature for incubation | Optimal temperature range from 4.5-11.5 | 8.0 °C | Groot, 1996 |
6 | Temperature for incubation | 2.8-10 [Temperatures above 11°C will kill the eggs] | 6.4 °C | Coad, 2006 |
6 | Temperature for incubation | 4-10 [The upper lethal temperature limit for developping eggs is 11.7°C] | 7.0 °C | Kerr and Grant, 1999 |
6 | Temperature for incubation | 5-12.5°C | 8.75 °C | Jensen, 1997 |
6 | Temperature for incubation | 7.98 ± 1.20, range 4.0-9.5 | 7.98 °C | Bascinar and Okumus, 2004 |
6 | Temperature for incubation | 9.2 ± 1.92 [range 4.5-13°C] | 9.2 °C | Bascinar et al, 2003 |
6 | Temperature for incubation | Optimum temperature was about 5°C [The lower limit for hatching was < 1°C and the upper limit was between ca. 10 and 16°C] | 5.0 °C | Humpesch, 1985 |
6 | Temperature for incubation | Prior to eyed stage, eggs were incubated at a constant temperature of 8°C and then between 8-13°C | 10.5 °C | Dumas et al, 1995 |
6 | Temperature for incubation | The freshwater temperature was 9°C at the beginning of November and rapidly decreased to 1-0°C by the end of December, although heating systems kept the water temperature in the incubation trays above 3°C | 0.5 °C | Roche-Mayzaud et al, 1998 |
7 | Degree-days for incubation | 416 | 416.0 °C * day | Pennel and Barrington. 1996 (79) |
7 | Degree-days for incubation | 350-500 | 425.0 °C * day | Bruslé and Quignard, 2001 |
7 | Degree-days for incubation | 500.0 | 500.0 °C * day | Scott and Crossman, 1973 |
7 | Degree-days for incubation | From 219 to 490 for temperatures of 1.5-6 | 3.75 °C * day | Groot, 1996 |
7 | Degree-days for incubation | 430.8-481.8 [Between 5-12.5°C] | 456.3 °C * day | Jensen, 1997 |
7 | Degree-days for incubation | 415, at a mean of 7.98°C [Also in other studies: 235-444] | 339.5 °C * day | Bascinar and Okumus, 2004 |
7 | Degree-days for incubation | 491 [Hatching started] to 523 [50% hatching] | 491.0 °C * day | Bascinar et al, 2003 |
7 | Degree-days for incubation | 370 [i.e. 74 days at 5°C at ca. optimum temperature] | 370.0 °C * day | Humpesch, 1985 |
7 | Degree-days for incubation | 503.9 ± 0.9 [But also These sampling corresponded approximatively to the end of the hatching period at 462 DD] | 503.9 °C * day | Dumas et al, 1995 |
7 | Degree-days for incubation | 559 [Effective day-degrees] | 559.0 °C * day | Kamler, 2002 |
7 | Degree-days for incubation | After 100% hatching occurred, varying 437 DD, 416 DD and 458 DD, water temperature was gradually increased to 8°C | 100.0 °C * day | Roche-Mayzaud et al, 1998 |
6 | Temperature for incubation | 7.5 | 7.5 °C | Hutchings, 1991 |
2 | Egg size after water-hardening | 4.12-5.22 | 4.67 mm | Hutchings, 1991 |
5 | Incubation time | 75.8 ± 2.1 | 75.8 days | Hutchings, 1991 |
5 | Incubation time | 75.3 ± 3.0 | 75.3 days | Hutchings, 1991 |
5 | Incubation time | 76.0 ± 1.7 | 76.0 days | Hutchings, 1991 |
6 | Temperature for incubation | 11-13 | 12.0 °C | Atchison, 1975 |
5 | Incubation time | 40 | 40.0 days | Atchison, 1975 |
6 | Temperature for incubation | 10 | 10.0 °C | Trojnar, 1977 |
3 | Egg Buoyancy | Demersal | Demersal | Trojnar, 1977 |
6 | Temperature for incubation | 9-10 | 9.5 °C | Hausle and Coble, 1976 |
1 | Oocyte diameter | 3.80-4.80 | 4.3 mm | Vladykov, 1956 |
3 | Egg Buoyancy | Demersal | Demersal | Argent and Flebbe, 1999 |
6 | Temperature for incubation | 6.0-6.6 | 6.3 °C | Argent and Flebbe, 1999 |
7 | Degree-days for incubation | 10.5; 44 | 462.0 °C * day | Witzel and MacCrimmon, 1983 |
7 | Degree-days for incubation | 10.5; 46 | 483.0 °C * day | Witzel and MacCrimmon, 1983 |
7 | Degree-days for incubation | 10.5; 49 | 514.5 °C * day | Witzel and MacCrimmon, 1983 |
7 | Degree-days for incubation | 10.5; 43 | 451.5 °C * day | Witzel and MacCrimmon, 1983 |
7 | Degree-days for incubation | 10.5; 45 | 472.5 °C * day | Witzel and MacCrimmon, 1983 |
3 | Egg Buoyancy | Demersal | Demersal | White, 1930 |
6 | Temperature for incubation | 5.8-6.2 | 6.0 °C | Curry et al, 1995 |
6 | Temperature for incubation | 5.0-7.0 | 6.0 °C | Curry et al, 1995 |
6 | Temperature for incubation | 4.0-5.5 | 4.75 °C | Curry et al, 1995 |
6 | Temperature for incubation | 4.8-5.5 | 5.15 °C | Curry et al, 1995 |
6 | Temperature for incubation | 4.6-6.0 | 5.3 °C | Curry et al, 1995 |
3 | Egg Buoyancy | Demersal | Demersal | Fraser, 1982 |
3 | Egg Buoyancy | Demersal | Demersal | Hazzard, 1932 |
6 | Temperature for incubation | 12.1-12.2 | 12.15 °C | Conklin et al, 1992 |
6 | Temperature for incubation | 10.5-13 | 11.75 °C | Atchinson and Johnson, 1975 |
5 | Incubation time | 40 | 40.0 days | Atchinson and Johnson, 1975 |
7 | Degree-days for incubation | 10.5-13; 32 | 376.0 °C * day | Atchinson and Johnson, 1975 |
6 | Temperature for incubation | 5-8 | 6.5 °C | Rand and Munden, 1993 |
6 | Temperature for incubation | 12 | 12.0 °C | Cleveland et al, 1986 |
6 | Temperature for incubation | 8.2 +/- 4.3 | 8.2 °C | Jordahl and Benson, 1987 |
6 | Temperature for incubation | 9.2 +/- 5.4 | 9.2 °C | Jordahl and Benson, 1987 |
6 | Temperature for incubation | 9.6 +/- 5.3 | 9.6 °C | Jordahl and Benson, 1987 |
7 | Degree-days for incubation | 5.5; 81.8 | 449.9 °C * day | Jordahl and Benson, 1987 |
7 | Degree-days for incubation | 7.5; 47.6 | 357.0 °C * day | Jordahl and Benson, 1987 |
7 | Degree-days for incubation | 7.0; 51.1 | 357.7 °C * day | Jordahl and Benson, 1987 |
7 | Degree-days for incubation | 4.3; 96.5 | 414.95 °C * day | Jordahl and Benson, 1987 |
7 | Degree-days for incubation | 3.7; 94.3 | 348.91 °C * day | Jordahl and Benson, 1987 |
7 | Degree-days for incubation | 4.0; 86.8 | 347.2 °C * day | Jordahl and Benson, 1987 |
6 | Temperature for incubation | 9 +/- 1 | 9.0 °C | Holcombe et al, 1979 |
3 | Egg Buoyancy | Demersal | Demersal | Bernier-Bourgault et al, 2005 |
6 | Temperature for incubation | 7 +/- 1 | 7.0 °C | Bernier-Bourgault et al, 2005 |
6 | Temperature for incubation | 10 | 10.0 °C | Keefe et al, 2000 |
6 | Temperature for incubation | 9 | 9.0 °C | Benoit, 1974 |
2 | Egg size after water-hardening | Quebec: 3.52-4.32 | 3.92 mm | Johnston and McKenna, 1977 |
2 | Egg size after water-hardening | P.E.I: 3.45-4.14 | 3.79 mm | Johnston and McKenna, 1977 |
4 | Egg adhesiveness | No. Only adhesive for a short period after extrusion | Adhesive | Detar, 2007 |
Trait id | Trait | Primary Data | Secondary Data | References |
---|---|---|---|---|
8 | Initial larval size | 20.4 ± 0.3 [Newly-hatched larvae, but not sure to be the size at hatching !] | 20.4 mm | Fraser, 1985 |
8 | Initial larval size | About 20-25 [For emerging fry] | 22.5 mm | Snucins et al, 1992 |
8 | Initial larval size | 20 [Not sure because obtained from a different sTudy] | 20.0 mm | Mittelbach and Persson, 1998 |
8 | Initial larval size | 15.1 | 15.1 mm | Olden et al, 2006 |
8 | Initial larval size | Normal alevin incubated at 9°C measured 13 mm total length | 13.0 mm | Hokanson et al, 1973 |
8 | Initial larval size | Range: 9.00-15.50, mean 12.08 | 12.25 mm | Purtscher and Humpesch, 2006 |
9 | Larvae behaviour | Alevins emerge from the redd after absorbing most of their yolk sac and then rest on the substrate outside the redd reabsorbing of the yolk sac before dispersing in the stream or the lake | Demersal | Mirza et al, 2001 |
9 | Larvae behaviour | When hatched, the larvae or sac fry remain in the gravel within the redd until the yolk is absorbed | Demersal | Scott and Crossman, 1973 |
9 | Larvae behaviour | Remain in the substrate after hatching before emerging | Demersal | Snucins et al, 1992 |
9 | Larvae behaviour | After hatcing, alevins remain in the gravel, deriving nourishment from their yolk sacas until March, when they emerge as new fry | Demersal | Fraser, 1985 |
9 | Larvae behaviour | Alevins remain in the nest until the yolk sac is absorbed | Demersal | Bradbury et al, 1999 |
9 | Larvae behaviour | Newly hatched sac fry remain in the gravel within the redd for between 30 and 80 days until the yolk is absorbed | Demersal | Kerr and Grant, 1999 |
9 | Larvae behaviour | Swim-up from fertilization: 675 degree-days, also from 387-618 [From hatching 675 less 415] | Pelagic | Bascinar and Okumus, 2004 |
9 | Larvae behaviour | Emerge from gravel in January-March | Demersal | Goodyear et al, 1982 |
10 | Reaction to light | Emergence from gravel nests in salmonids is largely nocturnal | Photopositive | Mirza et al, 2001 |
10 | Reaction to light | The trough was covered with black plastic sheeting since salmonid fry are negatively phototactic | Photophobic | Hausle and Coble, 1976 |
11 | Temperature during larval development | The groundwater temperature remained within the range 3.0-7.2°C, and during emergence within the range 4.0-6.0 | 5.1 °C | Snucins et al, 1992 |
11 | Temperature during larval development | 2.5-9.5 [Ambient natural temperature], 4.3-6.0 [Interstitial natural temperature] | 6.0 °C | Curry et al, 1991 |
11 | Temperature during larval development | 12.7 ± 1.8 [Emergence period] | 12.7 °C | Bernier-Bourgault and Magnan, 2002 |
11 | Temperature during larval development | 12.4-15.4°C optimal for fry growth [17.5°C preferred by large fingerlings, 25.3°C upper incipient lethal for yearlings] | 13.9 °C | Kerr and Grant, 1999 |
11 | Temperature during larval development | Reared at 8-13 then 10-15°C for feeding | 10.5 °C | Dumas et al, 1995 |
11 | Temperature during larval development | After 100% hatching occurred, water temperature was gradually increased to 8°C | 100.0 °C | Roche-Mayzaud et al, 1998 |
12 | Sibling intracohort cannibalism | Small, mature males were the most abundant of the egg eaters | Absent | Greeley, 1932 |
13 | Full yolk-sac resorption | 220 | 220.0 °C * day | Bruslé and Quignard, 2001 |
13 | Full yolk-sac resorption | The feeding experiment was initiated 112 days after fertilization (5 weeks after hatching). Sampling started when all fry from a given group hadesorbed started exogenous feeding, with the yolk sac being fully or partially resorbed | 112.0 °C * day | Roche-Mayzaud et al, 1998 |
14 | Onset of exogeneous feeding | The first external feeding activities of the fish larvae start when the larvae swim up. Observations have demonstrated that the larva has a piece of yolk when swimming up, so in trout fisheries the first external feeding starts when over 30% of the larvae swim up. | 30.0 °C * day | Bascinar et al, 2003 |
14 | Onset of exogeneous feeding | 82-188 [Samplings at 544 and 650 DD were conducted to approximatively coincide with the middle and end of yolk absorption period, i.e. 82 and 188 when substrated the DD of incubation (462)] | 135.0 °C * day | Dumas et al, 1995 |
14 | Onset of exogeneous feeding | [6 weeks after hatching at 8-13°C, fish were transfered to 70 l tanks to begin feeding] | 10.5 °C * day | Dumas et al, 1995 |
14 | Onset of exogeneous feeding | The feeding experiment started 16 weeks after fertilization (21 February 1992 for SWF2 and FWF2, and 28 February 1992 for FWF3), when all the free-swimming fry were feeding (mouths and complete digestive tracts functional). This corresponded to 658.2 degree-days from time of fertilization for FWF2 and SWF2, and 622.5 degree-days for FWF3 | 16.0 °C * day | Roche-Mayzaud et al, 1998 |
8 | Initial larval size | 17 | 17.0 mm | Hutchings, 1991 |
8 | Initial larval size | 16.6 | 16.6 mm | Hutchings, 1991 |
13 | Full yolk-sac resorption | 72 days 11-13 C | 12.0 °C * day | Atchison, 1975 |
8 | Initial larval size | 14-15 | 14.5 mm | Kwain and Rose, 1985 |
8 | Initial larval size | 15 | 15.0 mm | Osse and Van den Boogaart, 1995 |
13 | Full yolk-sac resorption | 250-513 | 381.5 °C * day | Granier et al, 2011 |
14 | Onset of exogeneous feeding | 2136 | 2136.0 °C * day | Granier et al, 2011 |
Trait id | Trait | Primary Data | Secondary Data | References |
---|---|---|---|---|
15 | Age at sexual maturity | 2-3 | 2.5 year | Pennel and Barrington. 1996 (77) |
15 | Age at sexual maturity | 2-3 [Sex not specified] | 2.5 year | Bruslé and Quignard, 2001 |
15 | Age at sexual maturity | Mostly 3-4, few at 2 [Both sex] | 3.5 year | Fraser, 1985 |
15 | Age at sexual maturity | Usually reach at 3, but could be 2 [Both sex] | 3.0 year | Kerr and Grant, 1999 |
15 | Age at sexual maturity | 2.0 [Both sex] | 2.0 year | Olden et al, 2006 |
15 | Age at sexual maturity | Sexual maturity of females usually arrives at the age of 3 or 4 years | 3.0 year | Vladykov, 1956 |
15 | Age at sexual maturity | Sexual maturity was attained by the majority of the brrok trout at the end of their 3rd year of life, although many males and females were mature in 2 years | 3.0 year | Wydoski and Cooper, 1966 |
15 | Age at sexual maturity | The youngest maturing fish were 3+ and 1+ for anadromous and fresshwater forms respectively | 3.0 year | Castonguay et al, 1982 |
16 | Length at sexual maturity | Mean 41, range 29.5-53.3 [Both sex] | 41.4 cm | Fraser, 1985 |
16 | Length at sexual maturity | 15.0 [Both sex] | 15.0 cm | Olden et al, 2006 |
16 | Length at sexual maturity | Spawning females were: in 1994, n=47, 37.2 ±6.5; in 1995, n=42, 37.6 ± 6.4 | 37.2 cm | Blanchfield and Ridgway, 1997 |
16 | Length at sexual maturity | The extreme variation in the size of female trout, which would spawned during the year of collection, ranged from 114-559 mm | 336.5 cm | Vladykov, 1956 |
16 | Length at sexual maturity | 87 percent of the anadromous fish which were mature were over 30 cm, whereas 51% of the maturing freshwater fish were under 24 cm | 30.0 cm | Castonguay et al, 1982 |
16 | Length at sexual maturity | Means of female sizes involved in spawing range from 36.5 ±1.2 to 41.1 ± 1.3 | 36.5 cm | Blanchfield and Ridgway, 1999 |
17 | Weight at sexual maturity | Spawning females were: in 1994, n=45, 656 ±395 g; in 1995, n=42, 705 ± 381 g | 656.0 kg | Blanchfield and Ridgway, 1997 |
18 | Female sexual dimorphism | The female are less bright than males and have swollen abdomens full of ripening eggs | Present | Groot, 1996 |
19 | Relative fecundity | About 4 | 4.0 thousand eggs/kg | Bruslé and Quignard, 2001 |
19 | Relative fecundity | 4-7 | 5.5 thousand eggs/kg | Mittelbach and Persson, 1998 |
19 | Relative fecundity | 2.843 ± 0.479, range 2.006-3.572 | 2.84 thousand eggs/kg | Bascinar and Okumus, 2004 |
19 | Relative fecundity | Mean of 3.448 for acid lakes and 2.960 for non-acid lakes | 3.45 thousand eggs/kg | St-Pierre and Moreau, 1986 |
20 | Absolute fecundity | 0.5-3 | 1.75 thousand eggs | Pennel and Barrington. 1996 (77) |
20 | Absolute fecundity | About 1 for a female of 30 cm | 1.0 thousand eggs | Rivier, 2001 |
20 | Absolute fecundity | 0.1-5 | 2.55 thousand eggs | Scott and Crossman, 1973 |
20 | Absolute fecundity | Mean 2.3, range 0.8-3.8 | 2.3 thousand eggs | Fraser, 1985 |
20 | Absolute fecundity | Varies from 0.1 to 5 | 0.1 thousand eggs | Groot, 1996 |
20 | Absolute fecundity | 0.919 ±0.324, range 0.521-1.569 | 0.92 thousand eggs | Bascinar and Okumus, 2004 |
20 | Absolute fecundity | The average number of egg spanwed varied from 90 to 4,800, according to the size of the female | 90.0 thousand eggs | Vladykov, 1956 |
21 | Oocyte development | Group-synchronous | Group-synchronous | Frantzen et al, 1997 |
21 | Oocyte development | Group-synchronous | Group-synchronous | Rinchard, 1996 |
22 | Onset of oogenesis | May-June | ['May', 'June'] | Tam et al, 1986 |
22 | Onset of oogenesis | Development begins in June for both sexes and reaches a peak in September | ['June', 'September'] | Wydoski and Cooper, 1966 |
23 | Intensifying oogenesis activity | August-Sepember | ['August'] | Tam et al, 1986 |
23 | Intensifying oogenesis activity | The secondary growth phase normally begins in early July, and is completed by mid-October | ['July', 'October'] | Henderson, 1963 |
23 | Intensifying oogenesis activity | July-August | ['July', 'August'] | Wydoski and Cooper, 1966 |
24 | Maximum GSI value | 16-18% [Mid-October] | 17.0 percent | Tam et al, 1986 |
24 | Maximum GSI value | Mean of 9.74, range 9.04 to 12.92 [Not specified] | 9.74 percent | Vladykov, 1956 |
24 | Maximum GSI value | Mean of 10-11% [September/October] | 10.5 percent | Wydoski and Cooper, 1966 |
24 | Maximum GSI value | Maturity indices were higher at 19 and 21 C since these fish did not spawn. The decoded-mean-maturity index (8.6) for female brook tout at 19C was derived from only three fish (0.5, 15.6, and 17.7) on November 7 the female maturity indices were 19.7 at 19°C and 16.2 at 21°C | 19.0 percent | Hokanson et al, 1973 |
24 | Maximum GSI value | Mean of 13.9 for anadromous populations, and 13.2 (range 10-16.8%) for resident populations | 13.4 percent | Fleming, 1998 |
24 | Maximum GSI value | Mean of 8.37 for acid lakes and 5.73 for non-acid lakes in September | 8.37 percent | St-Pierre and Moreau, 1986 |
26 | Resting period | Oocyte development and yolk formation is relatively low from November until May | 7.0 months | Tam et al, 1986 |
26 | Resting period | November to June, < 1% | 1.0 months | Wydoski and Cooper, 1966 |
Trait id | Trait | Primary Data | Secondary Data | References |
---|---|---|---|---|
27 | Age at sexual maturity | Mostly 3-4, few at 2 [Both sex] | 3.5 years | Fraser, 1985 |
27 | Age at sexual maturity | Usually reach at 3, but could be 2 [Both sex] | 3.0 years | Kerr and Grant, 1999 |
27 | Age at sexual maturity | 2.0 [Both sex] | 2.0 years | Olden et al, 2006 |
27 | Age at sexual maturity | Sexual maturity was attained by the majority of the brrok trout at the end of their 3rd year of life, although many males and females were mature in 2 years | 3.0 years | Wydoski and Cooper, 1966 |
28 | Length at sexual maturity | Mean 41, range 29.5-53.3 [Both sex] | 41.4 cm | Fraser, 1985 |
28 | Length at sexual maturity | 15.0 [Both sex] | 15.0 cm | Olden et al, 2006 |
28 | Length at sexual maturity | Spawning females were: in 1994, n=50, 33.4 ±7.7; in 1995, n=65, 33.7 ± 6.5 | 33.4 cm | Blanchfield and Ridgway, 1997 |
28 | Length at sexual maturity | Means of male sizes involved in spawing range from 37.5 ±2.0 to 42.4 ± 1.2 | 37.5 cm | Blanchfield and Ridgway, 1999 |
29 | Weight at sexual maturity | Spawning females were: in 1994, n=48, 480 ±407 g; in 1995, n=63, 507 ± 351 g | 480.0 kg | Blanchfield and Ridgway, 1997 |
30 | Male sexual dimorphism | Male developp a small kype on the lower jaw | Present | Groot, 1996 |
30 | Male sexual dimorphism | Spawning males develop a hooked lower jaw or kype | Present | Coad, 2006 |
30 | Male sexual dimorphism | Pectoral and pelvic fins are longer in male than female brook char. [In Salmo, most Salvelinus, and most Oncorhynchus, a major sexual difference is found in the development , in normal breeding individuals, of elongated, hooked jaws with enlarged teeth.An upturned lower jaw is technically called a kype; an enlarged and often distorted upper jaw is termed a snout.Kype and sount development differs not only among individuals but also among species and conspecific populations: it is generally greater in stream-dwelling and anadromous forms than in lake-spawning or strickly freshwater forms.Kypes andsnouts are best developed in males, although females of some species also develop smaller ones. Another secondary trait is a hump anterior to dorsal fin, found especially in males.] | Present | Willson, 1997 |
30 | Male sexual dimorphism | There is some evidence that male matures earlier in the season than the females do | Absent | Wydoski and Cooper, 1966 |
30 | Male sexual dimorphism | Males bigger than females | Absent | Fleming, 1998 |
31 | Onset of spermatogenesis | Development begins in June for both sexes and reaches a peak in September | ['June', 'September'] | Wydoski and Cooper, 1966 |
32 | Main spermatogenesis activity | June-July | ['June', 'July'] | Wydoski and Cooper, 1966 |
33 | Maximum GSI value | Mean of 2.9 and 3.4 at 19 and 21°C respectively [November] | 2.9 percent | Hokanson et al, 1973 |
33 | Maximum GSI value | Between 1.5 and 2% [August/September] | 1.5 percent | Wydoski and Cooper, 1966 |
33 | Maximum GSI value | Mean of 1.5 for resident populations | 1.5 percent | Fleming, 1998 |
33 | Maximum GSI value | Mean of 2.78 for acid lakes and 2.50 for non-acid lakes in September | 2.78 percent | St-Pierre and Moreau, 1986 |
35 | Resting period | From November to June | 8.0 months | Wydoski and Cooper, 1966 |
Trait id | Trait | Primary Data | Secondary Data | References |
---|---|---|---|---|
36 | Spawning migration distance | Mature fish may travel many miles upstream to reach the spawning grounds | No data | Scott and Crossman, 1973 |
36 | Spawning migration distance | Only make a few habitat changes during their life history [Do not migrate far from spawning grounds] | No data | Groot, 1996 |
37 | Spawning migration period | Upstream migrations have been observed as early as July in some Newfoundland rivers | ['July'] | Bradbury et al, 1999 |
37 | Spawning migration period | Enter their natal stream in spring and summer even though spawning occur in fall | ['April', 'May', 'June', 'July', 'August', 'September', 'October', 'November', 'December'] | Coad, 2006 |
37 | Spawning migration period | Lake-run fish ("coasters") enter and ascend streams beginning in mid-August | ['August'] | Goodyear et al, 1982 |
38 | Homing | Tag recaptures from fish tagged several years suggest that brrok trout spawn each year at the same spawning bed | Present | Fraser, 1985 |
38 | Homing | Enter their natal stream in spring and summer even though spawning occur in fall | Present | Coad, 2006 |
39 | Spawning season | October-November | ['October', 'November'] | Billard, 1997 |
39 | Spawning season | Begin on September, 28, reached its peal during October and early November | ['September', 'October', 'November'] | Hokanson et al, 1973 |
39 | Spawning season | October to January | ['January', 'October', 'November'] | Bruslé and Quignard, 2001 |
39 | Spawning season | Normally spawns in late August or in September in the nothermost part of its range (60°N), and during November in the southermost areas | ['August', 'September', 'November'] | Henderson, 1963 |
39 | Spawning season | Autumn | ['October', 'November', 'December'] | Rivier, 2001 |
39 | Spawning season | September to November, sometimes August to December | ['August', 'September', 'October', 'November', 'December'] | Fishbase, 2006 |
39 | Spawning season | Usually during late September, October or November, but may take place as early as August or as late as December | ['August', 'September', 'October', 'November', 'December'] | Scott and Crossman, 1973 |
39 | Spawning season | From October 20 to November 26 | ['October', 'November'] | Snucins et al, 1992 |
39 | Spawning season | October | ['October'] | Curry et al, 1991 |
39 | Spawning season | October-November | ['October', 'November'] | Fraser, 1985 |
39 | Spawning season | Over most of the range, October is the usual time of spawing [Occurs in late summer (late August or September) in the nothern part of their rnage to early december in the southern part] | ['July', 'August', 'September', 'October'] | Groot, 1996 |
39 | Spawning season | Normally occurs between late September and early November in Newfoundland | ['September', 'November'] | Bradbury et al, 1999 |
39 | Spawning season | Spawning in Nort America takes place from August to December | ['August', 'September', 'October', 'November', 'December'] | Coad, 2006 |
39 | Spawning season | Spawn in the fall (when day length decreases) mainly in October and early December, or Late August to early September | ['August', 'September', 'October', 'November', 'December'] | Kerr and Grant, 1999 |
39 | Spawning season | Mid-November to December | ['November', 'December'] | Terver, 1984 |
39 | Spawning season | Salmo and most char are fall breeders, although a few populations of Arctic char breed in spring | ['April', 'May', 'June', 'October', 'November', 'December'] | Willson, 1997 |
39 | Spawning season | Brook trout were observed on or near the spanwing grounds over a 64-d period in 1994 (30 September to 2 December) and a 61-d period in 1995 (25 September to 24 November) | ['September', 'November', 'December'] | Blanchfield and Ridgway, 1997 |
39 | Spawning season | Winter spawner [Other authors described between October and March] | ['January', 'February', 'March', 'October', 'November'] | Humpesch, 1985 |
39 | Spawning season | Normally spawn during October, November and december in new Hampshire | ['October', 'November'] | Hoover and Hubbard, 1937 |
39 | Spawning season | The spawning season on cold lakes (Grand lac Jacques Cartier and des Neiges), starts as early as August 20, while in othr lakes it typically limited to the moth of September, with the greatest activity taking place during the first two weeks. The latest date for spawning in the Laurentide Park is about October 20 | ['August', 'September', 'October'] | Vladykov, 1956 |
39 | Spawning season | Spawn in late August or in September in the northernmost pats of their range (60°N), and during November in the southernmost areas (35°N) | ['August', 'September', 'November'] | Hokanson et al, 1973 |
39 | Spawning season | August-March but usually October-December | ['January', 'February', 'March', 'August', 'September', 'October', 'November', 'December'] | Goodyear et al, 1982 |
40 | Spawning period duration | 5 [First redd at October 20 and the last at November 26, i.e. 38] | 5.0 weeks | Snucins et al, 1992 |
40 | Spawning period duration | The spawning periods lasted as long as 4 weeks, but the greatest number of spawning charr were present for less than 2 weeks | 4.0 weeks | Curry et al, 1991 |
40 | Spawning period duration | 4-5 [From Mid-October to end of November, Males apparently spent a longer period of time on the spawning area, probably 15-20 days, while females seldom seen on the bed more than 10 days after their first appeareance] | 4.5 weeks | Fraser, 1985 |
40 | Spawning period duration | Males usually arrive first on the spawning ground | No data | Groot, 1996 |
40 | Spawning period duration | Males arrive on the spawning ground first and defend a territory | No data | Coad, 2006 |
40 | Spawning period duration | A 15 day peak within a spawning period of about 50 days [With a decline in water temperature below 11°C and increased rainfall] | 15.0 weeks | Kerr and Grant, 1999 |
40 | Spawning period duration | 5-6 | 5.5 weeks | Terver, 1984 |
40 | Spawning period duration | 3-4: The seasonal peak in spawning activity: 1994, days 296-310; 1995, days 296-312 coincided with peak counts of males and females [Brook trout were observed on or near the spanwing grounds over a 64-d period in 1994 (30 September to 2 December) and a 61-d period in 1995 (25 September to 24 November). Peak number of males and females occurred approximatively the same time, between 22 Ocotber to 8 November. The duration of time spent on the spawning grounds was longer for males in 1994 than in 1995 (31 ± 12 and 22 ± 9 d, respectively), although no difference was observed for females between years (11 ± 6 and 15 ± 7, respectively).] | 31.0 weeks | Blanchfield and Ridgway, 1997 |
40 | Spawning period duration | From October 24 to december 6, 1931 [An individual may remain on the spawning grounds for a smuch as 25 days] | 24.0 weeks | Greeley, 1932 |
40 | Spawning period duration | Spawning begins late in September and extends into November | No data | Wydoski and Cooper, 1966 |
41 | Spawning temperature | 2 (A voir ?) | 2.0 °C | Pennel and Barrington. 1996 (79); |
41 | Spawning temperature | 10-16 | 13.0 °C | Hokanson et al, 1973 |
41 | Spawning temperature | Starts at 11.6 and finished at 2.9 | 11.6 °C | Snucins et al, 1992 |
41 | Spawning temperature | Declined to less than 12°C | 12.0 °C | Curry et al, 1991 |
41 | Spawning temperature | 2.9 ± 1.2 | 2.9 °C | Bernier-Bourgault and Magnan, 2002 |
41 | Spawning temperature | Preferred temperature is from 4.5 to 10, and spawning does not occur above 16°C | 4.5 °C | Groot, 1996 |
41 | Spawning temperature | Spawning activity and success occurs at below 9°C [4.5-10°C] | 7.25 °C | Kerr and Grant, 1999 |
41 | Spawning temperature | 4 [Temperature at which spawning is typically initiated] | 4.0 °C | Olden et al, 2006 |
41 | Spawning temperature | During peak spawning periods, water temperature in the spawning area decreased from 11.3 to 8.8°C in 1994 and from 10.3 to 5.9°C in 1995 | 11.3 °C | Blanchfield and Ridgway, 1997 |
41 | Spawning temperature | When the temperature is falling from 55 to 36°F | 55.0 °C | Goodyear et al, 1982 |
42 | Spawning water type | Near the shoreline (about 3 to 13 m) | Stagnant water | Bruslé and Quignard, 2001 |
42 | Spawning water type | Shallows of headwaters of streams but may successfully accomplished in gravelly shallows of lakes if there is a spring upwelling and a moderate current | Stagnant water | Scott and Crossman, 1973 |
42 | Spawning water type | Lakes ans streams | Stagnant water | Snucins et al, 1992 |
42 | Spawning water type | Stream | No category | Curry et al, 1991 |
42 | Spawning water type | Current: 24.2 ± 19.3 cm/s | Flowing or turbulent water | Bernier-Bourgault and Magnan, 2002 |
42 | Spawning water type | Typically spawn in streams or in gravel surronding sprin-up-welling areas of lakes and ponds | Stagnant water | Groot, 1996 |
42 | Spawning water type | Streams and occasionally in lakes | Stagnant water | Bradbury et al, 1999 |
42 | Spawning water type | Streams | No category | Coad, 2006 |
42 | Spawning water type | Both lakes and streams, and are closely associated with upwellings or seepages of ground water | Stagnant water | Kerr and Grant, 1999 |
42 | Spawning water type | Streams, shoreline reefs | Stagnant water | Willson, 1997 |
42 | Spawning water type | Spring streams, near sources of spring water | No category | Greeley, 1932 |
42 | Spawning water type | Spawn directly over areas of upwelling groundwater or near spring-fed tributaries | No category | Carline, 1980 |
42 | Spawning water type | Groundwater upwelling at redd sites | No category | Ridgway and Blanchfiled, 1998 |
42 | Spawning water type | Riffles or pools near headwaters of clear, well-shaded streams, in spring-fed areas with gradient not more than 2%; also along lake shores with moderately swift current, usually near sites of upwellings | Stagnant water | Goodyear et al, 1982 |
43 | Spawning depth | Shallow waters, mostly below 1 m but range between 0.60-2.60 m | 1.6 m | Bruslé and Quignard, 2001 |
43 | Spawning depth | Shallow | No data | Scott and Crossman, 1973 |
43 | Spawning depth | 20-55 cm deep | 37.5 m | Snucins et al, 1992 |
43 | Spawning depth | The depth of the water is mostly 50-75 cm, but can fluctuate up to 15 cm during the spawning season, and as much as 30 cm at other times of the season | 62.5 m | Fraser, 1985 |
43 | Spawning depth | In lakes, spawning has been observed at depths ranging from 0.1-8.0, but occurs most commonly at depth < 2 m | 4.05 m | Bradbury et al, 1999 |
43 | Spawning depth | Spawning sites are generally located near shore in water anywhere between 1.0 m or less and 2.4 m deep | 1.0 m | Kerr and Grant, 1999 |
43 | Spawning depth | Redds were located in the shallow littoral zone (1994, 1± 0.4 m; 1995, 1.6 ± 0.5 m) and near shore | 1.0 m | Blanchfield and Ridgway, 1997 |
43 | Spawning depth | Most redds were found in water approximatively 1 m deep | 1.0 m | Ridgway and Blanchfiled, 1998 |
43 | Spawning depth | 10 inches to 5 feet in streams, to more than 8 feets in lakes | 10.0 m | Goodyear et al, 1982 |
44 | Spawning substrate | Gravels | Lithophils | Mirza et al, 2001 |
44 | Spawning substrate | Gravels | Lithophils | Billard, 1997 |
44 | Spawning substrate | Gravels or clear sand | Lithophils | Rivier, 2001 |
44 | Spawning substrate | Small pebbles | Lithophils | Fishbase, 2006 |
44 | Spawning substrate | Most often over gravels beds | Lithophils | Scott and Crossman, 1973 |
44 | Spawning substrate | Gravels | Lithophils | Snucins et al, 1992 |
44 | Spawning substrate | Gravel-sand shoal that extends about 25 m from shore | Lithophils | Fraser, 1985 |
44 | Spawning substrate | Particle diameter mostly 8 -15.99 mm | No category | Bernier-Bourgault and Magnan, 2002 |
44 | Spawning substrate | Suitable spawning gravel range from 3 to 8 cm | Lithophils | Groot, 1996 |
44 | Spawning substrate | Gravel-bottomed [Preferred lake spawning substrate isgravel or a sand/gravel/small cobble mixture] | Lithophils | Bradbury et al, 1999 |
44 | Spawning substrate | Usually gravelly streams | Lithophils | Coad, 2006 |
44 | Spawning substrate | While "pea" gravel (0.4-2.0 cm) is the preferred substrate for spawning, brrok trout are know to used other loose bottom material [Areas of silt where upwellings are present are also commonly used, even in the absence of gravel | Lithophils | Kerr and Grant, 1999 |
44 | Spawning substrate | Lithophils | Lithophils | Balon, 1975 |
44 | Spawning substrate | Gravels [Fines (small and smaller particles) in spawning gravel can be deleterious to eggs | Lithophils | Hausle and Coble, 1976 |
44 | Spawning substrate | Gravels | Lithophils | Greeley, 1932 |
44 | Spawning substrate | The stream bottoms were composed of large stones, broken pieces of shale, gravel and sand | Lithophils | Wydoski and Cooper, 1966 |
44 | Spawning substrate | Eggs are deposited in redd dug in clean rubble, marl, or gravel | Lithophils | Goodyear et al, 1982 |
45 | Spawning site preparation | Lay their eggs in gravel nests called redds | Susbtrate chooser | Mirza et al, 2001 |
45 | Spawning site preparation | Lay eggs in nests and recovered by gravels | No category | Billard, 1997 |
45 | Spawning site preparation | Lay their eggs in gravel nests | Susbtrate chooser | Rivier, 2001 |
45 | Spawning site preparation | A receptive female chooses a spot and digs a redd | Susbtrate chooser | Fishbase, 2006 |
45 | Spawning site preparation | The female clears away debris and silt from the nesting area by a series of repid fanning movements of the caudal fin made while on her side | No category | Scott and Crossman, 1973 |
45 | Spawning site preparation | Redd, egg pocket | Susbtrate chooser | Snucins et al, 1992 |
45 | Spawning site preparation | Redd | Susbtrate chooser | Curry et al, 1991 |
45 | Spawning site preparation | During spawning, the female digs and cleans a shallow nest or redd in which the eggs are deposited | Susbtrate chooser | Bradbury et al, 1999 |
45 | Spawning site preparation | The female begins building a redd by fanning the finer particles of the substrate with her tail | Susbtrate chooser | Kerr and Grant, 1999 |
45 | Spawning site preparation | Brood hiders | Susbtrate chooser | Balon, 1975 |
45 | Spawning site preparation | Redds | Susbtrate chooser | Hausle and Coble, 1976 |
45 | Spawning site preparation | The digging of spawning pit is exclusively a phase of female behavior [Both male and female trout defend the redd against other fish in the period just preceding spawning] | Susbtrate chooser | Greeley, 1932 |
45 | Spawning site preparation | Nest by female | Best build by female | Fleming, 1998 |
46 | Nycthemeral period of oviposition | Spawning occurs during the daytime | Day | Scott and Crossman, 1973 |
46 | Nycthemeral period of oviposition | Primarily during daytime | Day | Groot, 1996 |
46 | Nycthemeral period of oviposition | Spawning generally occurs during the day with peaks in spawning activity occuring between 1300 and 1400 | Day | Kerr and Grant, 1999 |
46 | Nycthemeral period of oviposition | We observed spawning at all times of the day throughout both seasons, with a distinct peak in activity between 13:00 and 14:00. Eighthy-nine percent of all spawning toook place during the hours of daily observation (09:00-18:00), the remaining spawnings occurred either just prior to our arrival (3%) or sometime after our departure (8%) | Day | Blanchfield and Ridgway, 1997 |
46 | Nycthemeral period of oviposition | Species were more active during the mid-day period when the light was bright than in early morning and late evening | Day | Greeley, 1932 |
47 | Mating system | When the redd is completed, the pair entered the nest and deposit eggs and milt, once the eggs are completely covered, she moves to the upstream end of the redd and begins digging a new redd | No category | Fishbase, 2006 |
47 | Mating system | The actual spawning act is performed by one male and one female, but each may spawn with different mates during the reproductive period | Monogamy | Scott and Crossman, 1973 |
47 | Mating system | By pair, but both sex may spawn again with other fish | Monogamy | Coad, 2006 |
47 | Mating system | The male, a larger fish then the female at all observed instances of spanwing, darts to a position agasint one side of the female and curves his body toward hers in such a manner as to hold her against the bottom [Both males and females participate in several mating acts before becoming entirelyfinished with the reprodcutive activities of a single season] | No category | Greeley, 1932 |
47 | Mating system | For males and females, tha mating costs of peripheral males were substantial because more than half (56%) of all observed brrok trout spawnings involved peripheral males. Males that paired with large females experienced a greater incidence of kleptogamy due to increase numbers of peripheral males present | No category | Blanchfield and Ridgway, 1999 |
48 | Spawning release | Females spawned an average of 2.7-3.4 times to deposit a total of 552-571 eggs each | Total | Hokanson et al, 1973 |
48 | Spawning release | There are usually several extrutions followed by a resting period | Multiple | Scott and Crossman, 1973 |
48 | Spawning release | During spawning, there are usually several extrusions of eggs and milt followed by resting periods before the nest is closed | Multiple | Groot, 1996 |
48 | Spawning release | Female brook trout continue to excavate new redds an deposits eggs until they are spent | No category | Kerr and Grant, 1999 |
48 | Spawning release | Repeat spawning has been reported for brrok trout, but the accounts of successive spawning indicate that such behavior may lead to the deposition of ova in seperate pockets within a redd | No category | Hausle and Coble, 1976 |
49 | Parity | Tag recaptures from fish tagged several years suggest that brrok trout spawn each year at the same spawning bed | No category | Fraser, 1985 |
49 | Parity | Adults leave spawnig areas shortly after spawning | No category | Bradbury et al, 1999 |
49 | Parity | Brook trout mature early in life but have a considerably shorter life span than other salmonids | No category | Kerr and Grant, 1999 |
49 | Parity | Male brrok char often reproduce annually, but females in some populations only breed at 2 to 3 year intervals. This species tends to be short lived, with a maximum lifespan of less than 12 years; females tend to live longer than males | No category | Willson, 1997 |
49 | Parity | Iteroparous | Iteroparous | Berejikian et al, 2000 |
49 | Parity | Iteroparous | Iteroparous | Blanchfield and Ridgway, 1997 |
49 | Parity | As soon as S; fontinalis of either sex attains sexual maturity, it can spawn several years in succession | No category | Vladykov, 1956 |
49 | Parity | Most of the brook trout in these infertile streams mature, spawn, and die before reaching 6 inches in total length | Semelparous | Wydoski and Cooper, 1966 |
49 | Parity | Mean of 21% of repeat spawners for anadromous populations, and 24 (range 12-32%) for resident populations | No category | Fleming, 1998 |
49 | Parity | May return to lake after spawning | Iteroparous | Goodyear et al, 1982 |
50 | Parental care | The nests are not defended for extended periods | No care | Mirza et al, 2001 |
50 | Parental care | Nonguarders, the female covers the eggs and then leaves | No care | Fishbase, 2006 |
50 | Parental care | On completion of spawning, the female covers the eggs with gravel in a manner resembling the excavation of the redd | Female parental care | Scott and Crossman, 1973 |
50 | Parental care | Females become very aggressive during the post-spawinng period and defend the redd against possible intruders | No category | Groot, 1996 |
50 | Parental care | Adults leave spawnig areas shortly after spawning | No care | Bradbury et al, 1999 |
50 | Parental care | No parental care is provided after the nest is covered | No care | Kerr and Grant, 1999 |
50 | Parental care | Arctic char females may defend the nest briefly, unlike brook char | No category | Willson, 1997 |
50 | Parental care | The female, throughout the long period of egg covering (a process continued for one to several hours) resents the presence of any fish at or just above the spot where the eggs lie [Male defence lasts only trough early stages of egg covering] | No category | Greeley, 1932 |
50 | Parental care | No defence | No care | Fleming, 1998 |