J . Fish Biol. (1983) 22, 631-646 The biology of bream, Abramis brama (L), and its natural hybrid with roach, Rutilus rutilus (L), in the River Exe I. G. Cowx Department of Biological Sciences, University of Exeter, England (Received 9 June 1982, Accepted 24 June 1982) Hybrids between bream, Ahrumis brama, and roach, Rutilus rutilus. occur in the lower reaches of the River Exe and were positively identified by their meristic features and shape of the pharyngeal bone. The growth of bream and hybrids was determined by backcalculation from scales. Annual checks were laid down in early June. The mean length for age of female bream was significantly larger than that of males for fish 6 years of age and older. This divergence in growth rate was associated with the sexual maturation of the fish. Data for the sexes were combined and compared with the growth rate of hybrids and roach from the same region. Hybrid growth was similar to that ofbream for the first 6 years of life but was intermediate between that of the two parent species in the older age groups. Some hybrids with developing gonads were found. A change in the diet of bream from planktonic feeding to a benthophagic habit with age was noted. Detritus, substrate and chironomid larvae formed the bulk of the diet of hybrids. I. INTRODUCTION The ecology of bream, Abrumis brumu (L.), in British and Irish waters has received relatively little scientific attention (Hartley, 1947; Leeming, 1967; Kennedy & Fitzmaurice, 1968; Gee, 1978; Smith, 1978; Coles, 1979; Goldspink, 198 1 ) compared with the voluminous works on other cyprinid species. Goldspink (1 98 1) attributed this paucity to the species’ restricted geographical distribution, longevity, schooling habit and sporting value, altogether making it a difficult species to sample and study effectively. Similarly, despite their common occurrence in the wild (Regan, 191 1 ; Wheeler, 1969; Maitland, 1972; Burrough, 1981), little attention had been paid to the ecology of natural hybrids between species of Cyprinidae (Smith, 1978; Cowx, 1980). The majority of work on cyprinid hybrids to date has concentrated almost entirely on their identification (Wheeler, 1976; Child & Solomon, 1977; Wheeler & Easton, 1978; Swinney & Coles, 1982) probably because it is an essential preliminary in such studies and hence a justifiable subject for investigation. However, considering the enormous potential associated with hybridization of animal stocks (Pirchner, 1969) the ecology of cyprinid hybrids has been neglected. This paper describes observations made on the biology of bream and its natural hybrid with roach, Rutilus rutilus (L.), in the lower reaches of the River Exe, Devon. The River Exe in its lower reaches differs from other British waters in which bream has been studied in that it supports good coarse and game fisheries Address for correspondence: Severn-Trent Water Authority, Abelson House, 2297 Coventry Road, Birmingham, England. 63 I 0 1983 The Fisheries Society of the British Isles 0022-1 I12/83/060631+ 16 $03.00/0 632 I . G . COWX and represents the most southerly British water studied. The study forms part of a more detailed investigation into the ecology and management of the coarse fish populations of the River Exe catchment (Smith, 1978; Cowx, 1980). 11. MATERIALS AND METHODS Bream were originally stocked into the Exeter Canal in 1913 by Exeter City Council, with the assistance of a local angling club. The species gradually spread along the canal and was first recorded in the River Exe in 1929, since when it has become common in the lower reaches of the river and has hybridized with the endemic roach population. The River Exe in its lower reaches, in and below Exeter, is slow flowing, wide (60 m) and deep (3-4m) and has been subjected to extensive flood alleviation works, i.e. it is typical of the bream zone of lowland rivers. Flood alleviation works and construction of many weirs has reduced the current speed sufficiently to allow the finer silts to settle and these, with dead leaves, form the substrate. This muddy bottom supports good plant growth, predominantly Elodea canadensis (Michx), Myriophyllum alternijlorum (D.C.) and Potamogeton natans (L.). A total of 164 bream and 45 roach-bream hybrids were taken from the River Exe during a monthly sampling programme extending from September 1976 to November 1977. Gillnetting (mesh sizes 17.5-75 mm) was the principal sampling method employed although a few fish, mainly fry, were taken by electrofishing. Fork length (F.L.-mm) and weight (g) were measured and scales detached for age and growth studies. The anterior third of the gut was removed for analysis by the point’s method (Hynes, 1950) and the sex and maturity state of the fish were noted. To distinguish between fish types, i.e. bream, hybrids and roach, meristic data (fin ray and scale counts) were recorded from all bream and suspected hybrids. Pharyngeal bones were dissected from the fish, cleaned by maceration in hot water, bleached and preserved dry. In addition, similar data were recorded for 50 roach taken from the River Culm, a tributary of the Exe. These roach were considered true bred as the presence of bream has never been recorded in the Culm. 111. RESULTS IDENTIFICATION OF BREAM, ROACH AND THEIR NATURAL HYBRID In fish in which the meristic features of the parents are distinct, identification of the hybrid offspring should present no problems (Wheeler, 1969). Generally, these progeny exhibit meristic characteristics intermediate between those of the parent species. Unfortunately recognition of hybrids is not always so straightforward. Wheeler (1969, 1976) suggested that cyprinids are capable of complex interbreeding between parent and offspring, resulting in a diverse array of characters continuous between those of the parent species. In such cases positive identification of the hybrids may be difficult. Wheeler (1 969) suggested the pharyngeal teeth provide a trenchant character by which the fish can be dis,tinguished. In the then unforeseeable event of complex interbreeding occurring in the River Exe community, examination of the pharyngeal teeth, in addition to the meristic characters, was carried out. Meristic data Data on four of the meristic characters collected for the three fish types are shown in Table I; t-test analysis revealed significant differences (P<O.OO 1) BIOLOGY OF B R E A M A N D H Y B R I D S 633 TABLE I. Comparison of the meristic characteristics of roach, R . rutilus, bream, A . brama, and their natural hybrid Character number Statistic Lateral line scales Range Scales between dorsal fin origin and lateral line Scales between anal fin origin and lateral line Anal fin rays Roach Bream (N=50) (N=164) 4048 5 3-64 Hybrids (N=45) h4eanfS.E. 44.41 +O-25 57.13f0-51 48-55 50-50f0.54 7-9 10-15 8.20 k0-22 I 2.70 f0-1 8 4-5 7-10 Mean+s.E. 4.61 f0-14 8.31 +O-47 Range 8-14 23-30 Mean fS.E. I 1-45f0-19 26.42 k0.26 8-1 1 9.30 f0-21 5-7 6-33k0.19 16-2 1 17.95f0.17 Range Mean fS.E. Range between fish types for each of these characters. No other differences between fish types were detected. Pharyngeal teeth The pharyngeal bone (Fig. 1) provides another positive character by which the three fish types can be distinguished. The characteristic features of the pharyngeal bones of each fish type are as follows. (i) Bream: Teeth are hook-shaped with a smooth masticatory platform and arranged in a single series of five on each bone (i.e. tooth configuration of 5 : 5). The teeth are set high up on the bone which itself has a long ventral extension, pars ventralis. (ii) Roach: Teeth are found in a single row of five or occasionally six ( 5 : 5 or 5 : 6) on a bone which is very much stockier in appearance than the bream pharyngeal bone and by comparison has a small pars ventralis. The roach teeth are conical in shape but with a smooth, concave grinding surface. (iii) Hybrids: The bone shape is intermediate between those of the parent types. The teeth, which are basically roach-like, are laid out in a single series of five or six each side although on occasions a double row was observed with a single tooth in the second row (5 : 5 or 6 : 5 or 6 : 5 + 1). To confirm the different shapes of the pharyngeal bones the relationship between the length of the bone and the length of the edentated segment was determined (Fig. I). Measurements were made to the nearest 0.01 mm using a micrometer screw gauge. A preliminary plot of the data showed the relationship between bone length and edentated length to be curvilinear. Logarithmic transformation of the data (Fig. 2) gave a straight line best described by the following equations: Bream: Log y=0.899 log x-0.336, Hybrid: Log y = 1.063 log x-0.390, Roach: Logy= 1.072 log x-0.242, where y is the length of the edentated segment of the bone, and x is the total length of the pharyngeal bone. 634 1. G . COWX FIG.I . Pharyngeal bones from: (a) bream A . brama; (b) roach-bream hybrids; (c) roach R. rurilus. Magnification x 3. X = length of pharyngeal bone; Y = length of edentated segment of pharyngeal bone. In all cases the correlation coefficient approximated to unity. Analysis of covariance revealed a significant difference ( P <0.0 1) between the relationships for each fish type. Comparison of the meristic features and pharyngeal teeth of bream and roach in the present study (Table I & Fig. 1) with the characteristic features ofthe species established by other workers (Horoszewicz, 1960; Wheeler, 1969; Maitland, 1972) confirms that roach and bream from the lower reaches of the River Exe have been identified correctly. In addition, the existence of a third discrete fish type was established. By virtue of its intermediate form between those of roach and bream it was presumed to be the hybrid progeny of natural interbreeding between the roach and bream populations of the lower reaches of the River Exe. However, in the absence of independent evidence derived from controlled breeding (artificially crossing roach with bream in the laboratory and examining the characteristic features of the progeny) these fish cannot be positively identified as roach-bream hybrids. BIOLOGY OF BREAM A N D HYBRIDS 635 I I I I I I I 5 6 7 8 910 1 15 Length of pharyngeal L I 1 20 25 30 bone (mm) FIG.2. Relationship between pharyngeal bone length and the length of the bone occupied by teeth in roach, R. rutilus, A; bream, A . brama, 0 ;and roach-bream hybrids, x . AGE AND GROWTH Age determination The detailed description of bream scales given by Segerstrfile (1932, 1933), who distinguished between widely spaced edges of sclerites and the formation of an annual check, has led to their general acceptance for age and growth studies, (Hartley, 1947; Steinmetz, 1974; Goldspink 1 9 7 8 ~ .198 1). Similarly, roach scales have been thoroughly described and generally accepted for use in age and growth studies (Segerstrile, 1932; Hartley, 1947; Jones, 1953; Wallin, 1957; Cragg-Hine & Jones, 1969). Unfortunately, no such description of roach-bream hybrid scales, which have a similar appearance to roach scales, has been made and their use for age and growth studies has, therefore, not been validated. This, in addition to the statement of Hellawell (1974), who stressed it was imperative to establish the validity of using scales for age and growth studies in each new population investigated, has resulted in the need to verify the use of scales from River Exe bream and hybrids for age and growth studies. Verification of the annual nature of check deposition on the scales of River Exe hybrids and bream, and hence validation of their use for age and growth studies, was undertaken by observing the seasonal growth pattern on the scales. The mean number of rings outside the last annulus in all 11-V-year-old fish was determined for each month of the year (Fig. 3). From the limited data available check for- 636 1. G . cowx J JASONDJ FMAMJJASON Month FIG. 3. Formation of the annual check in bream and roach-bream hybrids: mean number of rings outside last check for all 11, 111, IV, and V year old fish. x -Mean and 95% confidence limits; 0 values for individual fish. Pecked line fitted by eye to suggest trend. mation in both bream and hybrids was found to be an annual event restricted to a short, well-defined period in June. In view of the annual formation of the scale check the use of scales for the determination of age of bream and hybrids in the present study was considered valid. 1 June was considered the birthday of all fish. Growth The growth of bream and hybrids was determined exclusively by backcalculation from scale measurements made under a microscope fitted with an eyepiece graticule. Measurements were made along the caudal axis of both bream and hybrid scales since measurements along this radius proved to be more closely related to fish length than other scale radii. The relationships, which take the form of simple linear regressions, are: Bream: F.L. =3.99 Sr+ 15-66,r z 0 . 9 4 , Hybrid: F.L. =2.99 Sri-33.34, r ~ 0 . 9 6 , where F.L. = fork length (mm), Sr = scale radius (arbitrary eyepiece units, 12 epu = 1 mm), r = correlation coefficient. Back-calculations were made by substituting measurements of scale radii to respective annuli in the appropriate regression equation. Back-calculated growth was determined for male and female bream separately but all hybrid fish data were BIOLOGY O F BREAM A N D H Y B R I D S 637 combined. Insufficient fish of any particular year class were caught to calculate growth of individual year classes. The back-calculated mean lengths for age of male and female bream and hybrids are given in Table 11. Comparison of the growth rates of male and female bream reveals a difference in the pattern of growth between sexes. Females show a relatively constant rate of growth throughout life with a slight decrease after their sixth birthday. By contrast, males exhibit similar growth to females in the younger age groups but have a pronounced decline in growth rate after their sixth birthday; t-test analysis reveals no significant difference in the growth rate between sexes for the first 6 years of life (P>0.05) but thereafter females grow at a significantly greater rate (P<O*Ol). No previous observation on the variation in growth rate between sexes has been documented. The difference in growth rate between sexes is illustrated in Fig. 4. This figure also compares the growth of River Exe bream with that in other British waters. Growth of River Exe fish in the first 6 years of life is comparable with that documented for other British populations, but the marked decline in growth rate thereafter was not apparent in the other populations examined. In the subjective assessment of growth rate by Backiel & Zawisza (1 968), bream which take 12 years to reach 400 mm in length, as was observed in the River Exe, were considered to have a medium growth rate. In Fig. 5 the back-calculated growth curve for River Exe roach-bream hybrids is illustrated and compared with the composite (i.e. male and female data combined) growth curves for bream and roach (Cowx, 1980) from the lower reaches of the river. The hybrid growth curve is of interest because up until 7 years of age hybrid growth matched that of bream (P>0.05) but thereafter bream grew significantly faster ( P < 0.00 1) than hybrids. Roach, by comparison, exhibited a slower growth rate throughout life than either bream or hybrids (P<O*OOl). It therefore appears that in the older age groups the growth of hybrids is intermediate between the growth curves calculated for the parent species. A similar situation was found by Smith (1978) amongst the mixed roach bream populations of the adjacent Exeter Canal. The annual growth curves for male and female bream and roach-bream hybrids (sexes combined) were tested for agreement with the von Bertalanffy model using Ford-Walford plots (Fig. 6 ) as described by Mann (1973). Estimates of ultimate length (L,) and growth coefficients for anabolism ( E ) and catabolism ( K ) were calculated and are presented in Table 111. The data for bream from the River Exe did not satisfy the von Bertalanffy growth model. The points (L, and &+,) for the younger age groups (both sexes) appear to run ' parallel ' to the line of equality. Accordingly, separate values of L , based on fish older than V years were calculated and are presented in Table 111. New values for the growth coefficients obtained from length data pertaining to mature fish gave conflicting results for the two sexes; the L , value being reduced for males (from 457.2 to 407.6 mm) but increased for females (from 627.5 to 720.4 mm). REPRODUCTIVE BIOLOGY Examination of the gonads of bream from the River Exe showed that mature fish comprise only a relatively small proportion (approximately I 1% ofthe bream Bream (males) Bream (females) Hybrids (sexes combined) Species Length age (mm) VII VIII IX x XI XI1 XI11 XIV 97.2 149.3 194.3 219.3 241.0 167.0 296.3 301.2 317.0 332.8 347.8 VI 57.8 v 1 1 1.3 176-2 228.6 264.3 296-5 313.8 334.2 361.3 394.5 423.5 438.5 464.1 472-8 IV 58.3 111 1076 154.7 193.8 248.8 277.6 283.0 295.0 304.9 314.9 342.8 354.8 382.7 I1 53.8 I TABLE 11. Growth of male and female bream, A . brama, and hybrids in the lower reaches of the River Exe 639 B I O L O G Y OF B R E A M A N D H Y B R I D S 1 I 1 1 1 1 1 1 1 1 1 1 1 1 IIm~vmmmlxxxIxIIm Age (years) FIG.4. Comparison of the growth ofbream in the River Exe with other British waters. (a) Wraysbury 17 (Gee, 1978), (b) Coosan Lough (Kennedy & Fitzmaurice, 1968), (c) River Exe-females, (d) River Exe-males, (e) Norfolk Broads (Hartley, 1947), (0 River Witham (Coles, 1979), (g) Cheshire Meres (Goldspink, I98 I). caught in the River Exe) of the whole population and only superficial observations were possible. Female bream appear to attain maturity in their sixth year of life ( V + ) whereas males mature a year later. These age groups were the youngest breeding fish encountered. The late maturation of River Exe bream compares favourably with other bream populations examined; Neubar (1926), Hartley ( 1947), Kennedy & Fitzmaurice (1 968) and Backiel & Zawisza (1 968) all found bream did not mature until 5 years of age. Generally progeny of a cross between two species are infertile, however, all older roach-bream hybrids of both sexes (> IV years of age) from the Exe were found to have well developed gonads (Tables IV, V). This was particularly evident in the females which had large numbers of apparently ripe eggs in their ovaries. DIET The general components of the diet of bream and hybrids are given in Table VI. Also included is a summary of the diet of roach from the lower reaches of the Exe (Cowx, 1980) for comparison. These data were compiled from fish caught 1. G . COWX 640 I IImmvvrmmlxxxImm Age (years) FIG. 5. Comparison of the growth of bream, roach and roach-bream hybrids in the lower reaches of the River Exe. at regular intervals throughout the year to minimize any variation in diet due to season and thus give a true impression of the diet. Detritus, debris and substrate constitute the major part of the diet of all bream, comprising approximately 50% of the diet. A marked change in the faunistic component of the diet was noted with increase in size. Planktonic crustacea (32%) was the principal component in the diet ofjuvenile fish (< 120 mm) although chironomid larvae (10%) were also important. Chironomid larvae (30%) and benthic crustacea (5%) predominated in the diet of older fish. Hartley (1947), Backiel & Zawisza (1968) and Kennedy & Fitzmaurice (1968) similarly noted a change in the diet of bream from planktonic feeding to a benthophagic habit with age. The composition of the diet of River Exe hybrids was found to be restricted to a few items of which molluscs and diptera larvae were the main faunistic components. The remainder of the diet was principally detritus and substrate (72%) and vegetation (10%) suggesting that hybrids have an omnivorous benthophagic habit. When compared with the diet of roach it appears that the diet of the two are similar except that hybrids have a greater intake of detritus whilst roach graze more intensively on algae and have a higher intake of Ephemeroptera nymphs. One significant omission from the diet of River Exe bream and hybrids was aquatic Oligochaetae. These are quickly digested and little evidence of their consumption remains in the stomachs. Detection of their chaetae amongst the mass of detritus was found to be impractical. However, infestation of the fish by the BIOLOGY OF B R E A M A N D H Y B R I D S 64 1 60C 40C 20c C 1 1 1 1 1 1 1 1 c -- 60C t \r Q) - 40C c 0 -! LL f 200 0 - 0, r 5 LL 0 6 00 400 200 Hybrids all fish L , = 407 rnrn I 0 200 I I 400 I I I 600 Fork length (F L ) a t age f (mm) FIG.6. Ford-Walford plots of male and female bream and roach-bream hybrids from the River Exe. L , derived by calculation. cestode Caryophyllaeus laticeps which has Tubificidae as its intermediate host, provides indirect evidence as to whether fish have been feeding on tubificids (Kennedy, 1969); 7.8% of the bream and 15.5% of the hybrids examined were infected with C. luliceps inferring that they must feed on tubificids. IV. DISCUSSION The existence of hybridization in the River Exe was not unexpected. Since the spread of bream into the lower reaches of the River Exe in the late 1920’s their coexistence with roach within the same habitat and a temporal overlap of spawn- 642 1. G. cowx TABLE 111. Ultimate length (mm), L , , and von Bertalanffy growth coefficients for anabolism, E, and catabolism, K, for bream, A . hrama, and roach-bream hybrids from the River Exe Species Bream (based on all age groups) Males Females Bream (based on fish older than V) Males Females Roach-bream hybrids (sexes combined) L, E K 457-2 625.5 63.6 66.1 0.14 407.6 7204 407.0 80.6 494 0.20 0.06 0.15 61.4 0.11 TABLE IV. Fecundity of female roach-bream hybrids from the River Exe Length (mm) Weight (8) Gonad weight (8) Age (years) 242 243 250 254 305-3 288.5 307.7 342.5 12-03 13.60 17.39 12.79 VI VI VI vl+ Fecundity (eggdfema le) + + + 49 320 53 640 73 040 55 550 TABLEV. Growth in absolute testis weight (g) with age in roach-bream hybrids from the River Exe Age group 11 I11 IV V v1 VII Number of fish examined (N) Mean testis weight (9) 6 4 5 3 1 1 0.79 1.91 2.63 2.68 2.34 15.65 ing season of the two species provide conditions conducive to hybridization. The high degree of hybridization observed in the River Exe, with some 21% of all bream and hybrids examined being of hybrid origin, reflects the extent to which the two parent populations interbreed. Human interference, mainly through channelization of the river and removal of submerged vegetation, probably increased the likelihood of interbreeding between the two species by reducing the number of potential spawning sites. Wheeler (1 969) suggested that in some cases roach-bream and roach-rudd (Scardinius rrythrophthalmus) hybrids can be fertile and if back-crossed to a 643 BIOLOGY OF BREAM AND HYBRIDS TABLE VI. Comparison of the percentage composition of the diet of bream, A . brama, roach, R . rutilus, and their natural hybrid in the River Exe Food items Oligochaetes Mollusca H ydrobidae/Sphaeridae Crustacea Planktonic Asellus aquaticus Gammarus sp. Ephemeroptera nymphs Caenis sp. Ephemera danica Trichoptera larvae Coleoptera larvae Noterus sp. Dytiscus sp. Hemiptera Diptera larvae Chironomidae Others Aerialherrestrial insecta Unidentifiable aquatic insecta Algae Macroph yta Detritus, debris, substrate Number of fish examined (N) Bream 12mm Bream 12mm Roach Hybrids 0.9 1 .o 1.2 5.1 6.8 31-9 0.4 2.2 2.6 5.9 0.8 0.6 2 .o 2-0 0.1 6.8 0-9 0.2 0-4 0.2 0.4 I .2 0.3 0.4 0.4 10.4 1 *o 0.5 2.4 0.1 0.8 49.2 46 29.8 2.1 0.4 3.2 56.7 42 2.4 3.9 4.8 1-1 15.0 9.3 41.8 534 5.4 0.8 0-6 1.6 10.0 71.6 45 parent type could give rise to populations of complex ancestry. The F, backcrossed derivative should show morphological features intermediate between those of the hybrid and the parent; in a freely interbreeding community of two species a continuous range of morphological features between the parent types would be expected. For example, Burrough (198 1) found a range of characters in the pharyngeal teeth of the mixed roach-rudd population of Slapton Ley, Devon, and concluded complex ancestry. No continuous range of characters was evident in the River Exe roach-bream community strongly suggesting the absence of introgressive breeding. Whether this absence of introgression in the River Exe populations was because the hybrids were infertile or because n o F, generation fish were caught is unknown. Both male and female roach-brcam hybrids with highly developed gonads were taken from the Exe (Tables IV, V) but there was no evidence to indicate if they were fertile inter se or with either parent species. As it is unlikely, with such a high degree of hybridization (2I0/o), that the hybrids did not mix with fish of the parent species during the spawning period it is probable that hybrid infertility is the reason for the absence of complex interbreeding in the Exe populations. The growth pattern of bream in the River Exe is of interest. No previous record of between sex variation in growth has been recorded for this species. Faster 644 I . G . COWX growth of female fish has, however, been described frequently in growth studies on other cyprinid species, particularly roach (Cragg-Hine, 1969; Mann, 1973; Goldspink, 1978b). In the River Exe bream population, the variation in growth pattern between sexes was the result of a rapid decline in growth rate of male fish at approximately 6 years of age which was not paralleled in the female growth curve. The most likely factor responsible for the decline in growth rate was sexual maturation of the fish; the inflexion in growth rate occurring about the age at which maturity was attained. The actual mechanism behind these distinct growth patterns is uncertain but, because of the close association with sexual maturity, it is probably a strategy for maximizing the reproductive capacity of the species. Backiel & Zawisza (1 968) stated that bream achieve maturity at a specific length rather than age. Early fast growth of all fish will ensure the population mature at an early age and enhance the proportion of sexually mature fish in the population. Once mature it is advantageous for females to continue growing becaue fecundity (number of eggs per female) is positively correlated with size of fish (Bagenal, 1967; Backiel & Zawisza, 1968). In males, however, continued fast growth is unnecessary since the gonad products of a single mature fish are sufficient to fertilize the eggs of several females, irrespective of size. Backiel & Zawisza (1968) suggested the slowing down of the growth rate of Ural river delta and Sea of Azov bream (both sexes) after the first 3-4 years was, similarly, the result of sexual maturation. It is clear that the poor fit of the bream growth data to the von Bertalanffjl growth model, as expressed in the Ford Walford plots, is a function of the diphasic growth pattern associated with maturation. Under these conditions the values of L , calculated appear to be related to the change in growth rate after maturation rather than to high population density and/or low food availability as suggested by Beverton & Holt (1957). Examination of the data presented by Zawisza (1 961) and Backiel & Zawisza (1968) on growth of beam in Polish waters revealed a similar pattern where the lower points relating to early growth run parallel to the line of equality. This pattern of fit to Ford Walford plots is not restricted to bream growth data. Growth of River Stour chub (Mann, 1976) also exhibit a similar pattern but no values of the von Bertalanfi growth coefficients for the older fish were determined. Hickley & Bailey (1982) also identified similar growth in River Eden chub and derived separate values for older fish. In view of these findings it is suggested that Ford Walford plots are an inadequate method of expressing fish growth, particularly in long-lived species such as bream and chub, unless consideration for the growth pattern of the fish is made. In many animal populations the progeny of interbreeding exhibit superior characteristics when compared to the parental lines, a phenomenon termed heterosis or hybrid vigour. The cause of heterosis is thought to be a complementation of favourable genes from each parent stock. When these favourable genes are dominant the performance of the hybrid will be superior to that of both parent lines. The growth of roach-bream hybrids from the River Exe was intermediate between those of both parent species suggesting absence of any heterotic effect relating to growth in the hybrid form. Heterosis has, however, been known to occur in fish hybrids; Svardson (1949) attributed the rapid growth oftrout, Salrno trutta L., and char, Salvelinus alpinus L., hybrids in Norway to the phenomenon. BIOLOGY OF BREAM A N D H Y B R I D S 645 I wish to thank Dr C. R. Kennedy for his supervision of this work and for critically reviewing the manuscript. I am indebted to South-West Water Authority, particularly Dr E. R. Merry, for their unending co-operation, and to Mr P. Shears and Mr A. Shephard for their continued assistance with the field work. The work was undertaken during the tenure of a NERC Studentship in conjunction with South-West Water Authority. The views expressed are those of the author and not necessarily of the Authority. References Backiel, T. & Zawisza, J. (1968). Synopsis of the biological data on the bream, Abramis brama (L.). F.A.O. Fisheries Synopsis No. 36, FRi/S36. Bagenal, T. B. (1967). A short review of fish fecundity. In The Biological Basis oJFreshwater Fish Production. (S. D. Gerking, ed.), pp. 89-1 11. Oxford: Blackwell Scientific Publications. Beverton, R. J. H. & Holt, S. J. (1957). On the dynamics of exploited fish populations. Fish. Invest., Lond. Ser. 2 19, 1-533. Burrough, R. J. (198 1). Problems of natural hybridization amongst cyprinids. Proc. 2nd Brit. Freshwat. Fish Con$, Univ. of Liverpool pp. 162-17 1. Child, A. R. & Solomon, D. J. (1977). Observations on morphological and biochemical features of some cyprinid hybrids. J . Fish Biol. 11, 125-131. Coles, T. F. (1979). Investigations into fish populations in Lincolnshire rivers. Proc. 1st Brit. Freshwat. Fish Con$, Univ. of Liverpool pp. 345-367. Cowx, I. G. (1980). Population Ecology and Management of Coarse Fish in the River Exe and River Culm. Ph.D. Thesis, Univ. of Exeter, U.K. Cragg-Hine, D. & Jones, J. W. (1969). The growth ofdace, Leuciscus leuciscus (L.), roach, Rutilus rutilus (L.), and chub, Squalis cephalus (L.), in Willow Brook, Northamptonshire. J . Fish Biol. 1, 59-82. Gee, A. S. (1978). The distribution and growth of coarse fish in gravel pit lakes in southeast England. Freshwat. Biol. 8, 385-394. Goldspink, C. R . ( 1 9 7 8 ~ ) The . population density, growth rate and production of bream, Abramis brama, in Tjeukemeer, The Netherlands. J. Fish Biol. 13,499-5 17. Goldspink, C. R. (19786). Comparative observations on the growth rate and year class strengths of roach Rutilus rutilus L. in two Cheshire lakes, England. J . Fish Biol. 12,421433. Goldspink, C. R. (1981). A note on the growth rate and year class strength of bream Abramis brama L., in three eutrophic lakes, England. J . Fish Biol. 19, 665-673. Hartley, P. H. T. (1947). The natural history of some British freshwater fish. Proc. zool. SOC.Lond. 117, 129-206. Hellawell, J. M. (1974). The problems of protracted check formation and the validity of the use of scales in age determinations exemplified in two populations of dace Leuciscus leuciscus (L.). In: The Ageing qfFish (T. B. Bagenal, ed.), pp. 173-1 80. Woking: Unwins. Hickley, P. & Bailey, R. G . (1982). Observations on the growth and production of chub Leuciscus cephalus and dace Leuciscus leuciscus in a small lowland river in southeast England. Freshwat. Biol. 12, 167-178. Horoszewiz, L. (1960). The value of the lower pharyngeal arches as species criteria for defining fish of the family Cyprinidae. Roczn Nauk roln. 75B. 237-258. Hynes, H. B. N. (1950). The food of freshwater sticklebacks (Gasterosteus aculeatus and Pygosteus pungitius), with a review of methods used in studies of the food of fishes. J. anim. Ecol. 19.36-58. Jones, J. W. (1953). Part 1. Scales of roach. Part 11. Age and growth of trout, grayling, perch and roach from Llyn Tegid and the roach from the River Birket. Fish. Invest.. Lond. Ser. 1. 5, 1-18. Kennedy, C. R. (1969). Tubificid oligochaetes as food of the dace Leuciscus Icuciscus (L.). J . Fish Biol. 1 , 1 1715. 646 1. G . cowx Kennedy, M.& Fitzmaurice, P. (1968). The biology of the bream (Abramis brama L.) in Irish waters. Proc. R. Ir. Acad. 5, 95-1 57. Leeming, J. (1967). The biology of some coarse fish in the River Welland. PhD. Thesis, Univ. of Liverpool, U.K. Maitland, P. S. (1972). A key to the freshwater fishes of the British Isles, with notes on their distribution and ecology. Freshwat. Biol. Ass. Sci. Publ. No. 27. Mann, R. H. K. (1973). Observations on the age, growth, reproduction and food of roach, Rutilus rutilus (L.) in two rivers in southern England. J. Fish Biol. 5, 707-736. Mann, R. H. K. (1976). Observations on the age, growth, reproduction and food of the chub Squalius cephalus (L.) in the River Stour, Dorset. J. Fish Biol. 8,265-288. Neubar, C. (1926). Biologisches und Witschaftliches von Blei (Abramis brama L.) im Stettiner Haffund seinen Nebengewassen. Z. Fisch. 24, 163-193. Pirchner, F. (1969). Population Genetics in Anima/ Breeding. San Francisco: W. H. Freeman and Co. Regan, C. T . (191 1). Thefveshwater Fishes ofthe British Isles. London: Methuen 8~Co. Segerstrlle, C . (1932). Uber die jahrlichen Zuwachszonen der Schruppen und Beziehungen zwischen Temperatur und Zuwachs bei Abramis brama. ilcta 2001. .firm. 13, 1-42, Segerstrile, C. ( I 933). Uber scalimetrische Methoden zur Bestimmung des linearen Wachstums bei Fischen insbesondere bei Leuciscus idus L., Abramis hrama L., und Perca fluviatilis L. Acta zool.,fenn. 15, 1-169. Smith, C. R. (1978). Management studies of two contrasting coarse fisheries in Devon. M.Sc. Thesis. Univ. of Exeter, U.K. Steinmetz, B. (1974). Scale reading and back-calculation of bream Ahramis brama (L.) and rudd Scardinius erythrophthalmus (L.). In: The Ageing of Fish (T. B. Bagenal, ed.), pp. 148-157. Woking: Unwins. Svardson, G. (1949). Competition between trout and char (Salmo trutta and Salmo alpinus). Rep. Inst. Freshwat. Rex, Drottningholrn 29, 108-1 1 1. Swinney, G. N. & Coles, T . F. (1982). Description of two hybrids involving bream, Bliccu bjoerkna (L.) from British waters. J. Fish Biol. 20, 121-129. Wallin, 0. (1957). On the growth structure and the development physiology ofthe scales of fishes. Rep. Inst. Freshwat. Res., Drottningholm 35, 385-477. Wheeler, A. (1969). Fishes of the British Isles and North-west Europe. London: Macmillan. Wheeler, A. (1976). On the population of roach (Rutilus rutilus), rudd (Scardinius erythrophthalrnus), and their hybrid in Esthwaite Water, with notes on the distinction between them. J. Fish Biol. 9, 391-400. Wheeler, A. & Easton, K. (1976). Hybrids of chub and roach (Leuciscus cephalus and Rutilus rutilus) in English rivers. J. Fish Biol. 12, 167-1 7 1. Zawisza, J. (1961). The growth of fish in lakes of Wegorzewo District. R o a n . Naukro In. 77-B-2, 681-748.
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