JNIVERSITY ©. ILLINOIS LIBRARY AT URBANA-CHAMPAIGN NATURAL HIST SURVE’ Life Histories of the Bandfin Darter, Etheostoma zonistium, and the Firebelly Darter, Etheostoma pyrrhogaster, in Western Kentucky Douglas A. Carney Brooks M. Burr Illinois Natural History Survey Biological Notes 134 December 1989 Illinois Natural History Survey, Lorin I. Nevling, Chief A Division of the Illinois Department of Energy and Natural Resources Printed by authority of the State of Illinois X02837-—2M-12-89 US ISSN 0073-490X Cover photograph of a male Etheostoma zonistium was taken by W.N. Roston, Forsyth, Missouri. Graphic Assistance: Molly Hardin Scott Editors: Audrey S. Hodgins and Eva L. Steger A catalog of the publications of the Illinois Natural History Survey is available without charge from the address below. A price list and an order blank are included with the catalog. Illinois Natural History Survey Distribution Center Natural Resources Building 607 East Peabody Drive Champaign, Illinois 61820 Citation: Carney, D.A., and B.M. Burr. 1989. Life histories of the bandfin darter, Etheostoma zonistium, and the firebelly darter, Etheostoma pyrrhogaster, in western Kentucky. Illinois Natural History Survey Biological Notes 134. 16 p. Life Histories of the Bandfin Darter, Etheostoma zonistium, and the Firebelly Darter, Etheostoma pyrrhogaster, in Western Kentucky Bailey and Etnier (1988) described the bandfin darter, Etheostoma zonistium, from Leath Creek, Chambers Creek drainage, Hardin County, Tennessee, and the firebelly darter, E. pyrrhogaster, from Clear Creek, North Fork Obion River drainage, Henry County, Tennessee. Both species are members of the subgenus Nanostoma, which encompasses E. zonale and all species previously referred to in the subgenus Ulocentra (Page 1981). Nanostoma includes thirteen taxonomically described species, eight of which were described as new species (Bouchard 1977; Page & Burr 1982; Bailey & Etnier 1988; Etnier & Bailey 1989) or elevated from synonomy (Etnier & Starnes 1986) in recent years. At least five species of Nanostoma remain taxonomically undescribed. Substantial life history information is available for four species of Nanostoma: Etheostoma zonale (Lachner etal. 1950), E. coosae (O’Neil 1981), E. stmoterum (Page & Mayden 1981), and E. baileyi (Clayton 1984). In addition, the reproductive behavior of E. duryi (Page et al. 1982) and E. rafinesquei and E. barrenense (Winn 1958a, b; Stiles 1974) has been described. Other publications discuss fecundity and spawning substrate (Weddle 1989), distributions (Bouchard 1972, 1973, 1974; Kuehne 1972; Fallo & Warren 1982; Burr & Warren 1986), interspecific interactions (Greenburg 1984, 1985), food habits (Adamson & Wissing 1977; Cordes & Page 1980), respiration and habitat selection (Ultsch et al. 1978), and evolutionary trends in repro- duction, morphology, and ecology (Page & Swofford 1984; Page 1985) of species of Nanostoma. Finally, Kuehne and Barbour (1983) and Page (1983) provide summaries of the natural history of members of Nanostoma. This paper was submitted in its original form by Douglas A. Carney in partial fulfillment of the requirements for the degree of Master of Arts in the Graduate School of Southern Illinois University at Carbondale. Mr. Carney was formerly a Technical Research Biologist with the Illinois Natural History Survey and is now a Resource Planner with the Illinois Department of Conservation. Dr. Brooks M. Burr is a Professor in the Department of Zoology at Southern Illinois University at Carbondale and an Affiliate of the Survey. Douglas A. Carney and Brooks M. Burr Etheostoma zonistium occurs in lower western tribu- taries of the Tennessee River in western Kentucky and Tennessee, barely extending into northern Mississippi and Alabama, and in the Hatchie River drainage in Tennessee and the Black Warrior River drainage in Alabama (Fig. 1). Etheostoma pyrrhogaster occurs in tributaries of the Mississippi River in extreme south- western Kentucky and in western Tennessee (Fig. 1). In Tennessee (Starnes & Etnier 1980) and in Kentucky (Warren et al. 1986), E. pyrrhogaster is regarded as a species of special concern because of its restricted distribution and the loss of habitat resulting from the channelization of streams. Methods Observations and minnow-seine (1.2 m x 3.1 m, 3.8- mm mesh) collections were made at approximately monthly intervals from 5 January to 13 November 1983. Additional observations and collections were made during spawning periods in 1983 and 1984. Data collected at West Fork Clarks River and at Terrapin Creek on each sampling date included stream condi- tions, darter habitat, and darter behavior. Water velocity in darter habitat was measured during spawn- ing periods with a Teledyne-Gurley Pygmy current meter. Fishes captured with the two darter species and the habitats in which these captures occurred were quanti- fied in a series of three monthly samples (May-July 1983). Unit-effort sampling consisted of five seining efforts in each of four subjectively identified habitat types: Riffles, defined as shallow areas with swift current and surface turbulence over gravel and sand substrate. Raceways, defined as moderately shallow areas with swift current and little to no surface turbulence over gravel and sand substrate. Stream margin zones, defined as areas of moderate depth and current next to a bank (often undercut) and primarily over sand (sometimes sand with large stones or gravel). Pools, defined as deep areas with sluggish current over sand and detritus. 2 Illinois Natural History Survey Biological Notes Kick-sets were used to capture fish in all habitat types except pools, where seine hauls were made. All captured fishes in each habitat type were identified and enumerated. Unit-effort sampling comprised 60 seining efforts per study site (all habitat types combined). To facili- tate discussion, an arbitrary rating of darter abundance at each study site was established for quantified sampling efforts: Abundant, at least 60 individuals of a given species captured. Common, 12 to 59 individuals. Uncommon, 6 to 11 individuals. Rare, fewer than 6 individuals. Specimens were preserved in 10 percent formalin and stored in 70 percent ethanol. Totals of 336 E. zonistium from West Fork Clarks River and 164 E. pyrrhogaster from Terrapin Creek were preserved and examined. Additional specimens from the ichthyologi- cal collection at Southern Illinois University at Carbon- dale were examined, and all darters collected during the study were deposited at that facility. All specimens were sexed, measured, and aged. Sexing was by examination of the genital papillae or, when necessary, by examination of the gonads. Meas- urements were to the nearest 0.1 mm standard length (SL). Age-to-year class was determined by counting annuli on scales removed from the dorsum near the junction of the first and second dorsal fins. Year-classes were corroborated by analysis of length-frequency distribution and number of annual rings on otoliths (sagittae). Otoliths were removed by making an incision from the breast to the sacculus and bending the head back until the sagittae were exposed. Whole sagittae were immersed in glycerine, and annuli were counted with the aid of a fiber-optic light and dissect- ing microscope. Age to month was determined by using April, the month of greatest spawning activity, as month zero. Seasonal variation in the reproductive conditions of males and females was determined by the gonadoso- matic index (GSI). Gonad weight and adjusted body weight (weight of the specimen minus gonads, stom- ach, intestine, and liver) of alcohol-stored specimens (blotted dry) were measured to the nearest 0.001 gm on an analytical balance. Ovaries of preserved specimens were dissected, and oocytes were selected at random to create a subset of total ova for diameter measurements. All fertilized eggs recovered from aquaria were measured. Fertilized eggs were incubated in an aerated malachite green solution. The larval terminology used was that of Snyder (1976). Diameters of ova and lengths of larvae and genital papillae were measured to the nearest No. 134 0.01 mm with an ocular micrometer. Ovum diameter was calculated as the mean of three measurements. Spawning behavior was observed in the laboratory in 71-liter (30 cm high x 25 cm wide x 91 cm long) aquaria. Adults in spawning condition were given a choice of all known egg deposition sites used by other species of darters (Page 1983:165): vertical rock, vertical plant, raised horizontal rock, and a substrate of mixed gravel and sand. Regression coefficients were calculated by the method of least squares using the Systems Regression procedure of the Statistical Analysis System (SAS). Correlations were Pearson product-moments. In statistical tests, differences of P<0.05 were considered significant. Study Areas The site selected for study of Etheostoma zonistium was West Fork Clarks River (Tennessee River drainage) at the Kentucky Highway 121 bridge, 0.6 km east of Coldwater, Calloway County, Kentucky (Fig. 2). At this site, the stream is of moderate gradient and consists of shallow riffles with gravel and sand substrate alternat- ing with deep, sand-bottomed pools. Widths of 2 to 6 m and depths to 1.0 m are characteristic of the study area during normal flow. Water is generally clear but becomes turbid during flooding. Agricultural lands are immediately adjacent to parts of the stream; however, a narrow margin of deciduous trees lines most of the study site. During 1983 monthly water temperature ranged from 8.5°C in January to 25°C in July. Nineteen fish species were collected from West Fork Clarks River. Species taken, in addition to those captured in the stream margins during unit-effort sampling (Table 1), were Notropis lutrensis, N. umbra- tilis, N. whipplei, Phenacobius mirabilis, Moxostoma se 28 eae S g: y 89° 87° 85° 83° Figure 1. Ranges of Etheostoma zonistium (circles) and E. pyrrhogaster (triangles). Life history study sites are enclosed by open circles. Map modified from Bailey and Etnier (1988). December 1989 erythrurum, Ameiurus natalis, Noturus nocturnus, Lepomis cyanellus, and Percina maculata. Etheostoma pyrrhogaster was studied in Terrapin Creek (Obion River drainage) just north (upstream) of the Tennessee Highway 69 bridge at the Kentucky—Tennessee border, Graves County, Kentucky (Fig. 3). Terrapin Creek has a low-to-moderate gradi- ent and consists of sand- and gravel-bottomed riffles alternating with sand-bottomed pools. Widths of 2 to 5 m and depths to 1.5 m are characteristic of Terrapin Creek at normal flow. The water, as in West Fork Clarks River, is turbid only during flooding. The study area is immediately bordered by deciduous forest; however, agricultural land is nearby. During 1983, monthly water temperatures ranged from 8°C in January to 20°C in June. On 27 March and 18 April 1983, E. pyrrhogaster was taken for aquarium spawning observation from a backwater slough of Terrapin Creek, 0.8 km south of Bell City, Graves County, Kentucky. The slough was Figure 2. Study area for Etheostoma zonistium, West Fork Clarks River, Calloway County, Kentucky, 18 April 1983. Figure 3. Study area for Etheostoma pyrrhogaster, Terrapin Creek, Graves County, Kentucky, 22 July 1983. Carney and Burr: Bandfin and Firebelly Darters in Western Kentucky 3 1 m wide with depths to 30 cm and had water tempera- tures of 14°C and 17°C on the above sampling dates, respectively. A silt substrate and abundant aquatic vegetation were present in the slough, which was surrounded by deciduous forest. Fishes collected in Terrapin Creek and the back- water slough during this study, in addition to those taken during unit-effort sampling of stream margins and pools (Table 2), include Umbra limi, Notropis fumeus, Pimephales promelas, Moxostoma poecilurum, Noturus hildebrandi, Fundulus olivaceus, Elassoma zo- natum, Aphredoderus sayanus, Etheostoma chlorosomum, E. gracile, and E. parvipinne. Other fishes reported from the study area by Walsh and Burr (1981) but not taken during this study were Esox americanus, Notemigonus Table 1. Relative abundance of fishes captured with Etheo- stoma zonistium in West Fork Clarks River, expressed as percent of individuals (N= 167) captured by unit-effort seining of stream margin habitat in May, June, and July 1983. Species Percentage Etheostoma zonistium 44.3 Campostoma oligolepis 22.2 Pimephales notatus 17.4 Semotilus atromaculatus 7.8 Hypentelium nigricans 2.4 Fundulus olivaceus 1.8 Erimyzon oblongus L.2 Etheostoma flabellare U2, Etheostoma neopterum 1.2 Micropterus punctulatus 0.6 Table 2. Relative abundance of fishes captured with Etheo- stoma pyrrhogaster in Terrapin Creek, expressed as percent of individuals (N= 221) captured by unit-effort seining of stream margin and pool habitat in May, June, and July 1983. Species Percentage Etheostoma nigrum S157 Semotilus atromaculatus Ded Etheostoma lynceum 16.3 Notropis camurus 6.3 Etheostoma pyrrhogaster 6.3 La mpetra aepyplera 5.4 Phenacohius mirabilis 3.6 Percina sciera 3.2 Noturus phaeus 1.0 Gambusia affinis 1.0 Lepomis marginatus 1.0 Etheostoma swaini 1.0 Erimyzon oblongus 0.5 Minytrema melanops 0.5 Lepomis cyanellus 0.5 Lepomis macrochirus 0.5 4 Illinois Natural History Survey Biological Notes crysoleucas, Notropis umbratilis, Ameiurus natalis, A. melas, Lepomis gulosus, and L. megalotis. A total of 34 fish species are known to occur in the Terrapin Creek study area. Habitat and Associated Species In West Fork Clarks River, Etheostoma zonistium was frequently collected over a substrate of sand or gravel and sand near the stream margin at depths of 15 to 75 cm and was often found in emergent soft rush (Juncus effusus). Unit-effort seining by habitat type confirmed the observation that E. zonistiwm typically inhabited the stream margin (Fig. 4). The species was abundant in West Fork Clarks River as was E. flabellare; however, the two were weakly associated due to the propensity of E. flabellare for riffles (Fig. 4). Analysis of a 2 x 4 contin- gency table of these species versus habitats by the log likelihood ratio test (Sokal & Rohlf 1981) indicated a significant association (G= 148.65, P<0.001) between species and habitat. Etheostoma neopterum was rare at the study site but was found with E. zonzstium in the stream margin (Fig. 4), a habitat commonly noted for E. neopterum (Howell & Dingerkus 1978; Braasch & Mayden 1985). Fishes captured in greatest numbers with E. zonistium were Campostoma oligolepis, Pimephales notatus, and Semotilus atromaculatus (Table 1). In Terrapin Creek, E. pyrrhogaster typically inhab- ited the stream margin at depths of 30 cm to 1 m but also occurred in deeper pools, often among exposed tree roots in undercut banks over sand. Unit-effort sampling indicated an affinity of individuals (N= 8) for stream margin habitats; however, a number of indi- viduals (N= 6) were also recovered from pools (Fig. 5). Etheostoma pyrrhogaster was classified as uncommon in Terrapin Creek with 18 individuals captured during the unit-effort seining (Fig. 5). Although too few individuals were captured to warrant statistical analysis of the association between species and habitat, the data represent a reliable estimate of the habitat affinity of E. pyrrhogaster in Terrapin Creek as judged from nonquantitative observations during the course of the study. Fishes collected in greatest numbers with E. pyrrhogaster were E. nigrum, Semotilus atromaculatus, and E. lynceum (Table 2, Fig. 5). Page and Mayden (1981) described characteristic Nanostoma habitat as clean pools with moderate current over bedrock, cobble, or gravel. The relatively fine substrates over which E. zonisttum and E. pyrrhogas- ter were taken, in comparison with other members of Nanostoma, were indicative of their lowland stream habitats. Reproductive Cycle of the Male Male Etheostoma zonistium and E. pyrrhogaster developed brilliant nuptial coloration as described by Bailey and Etnier (1988). Color intensification began as early as TOTAL NUMBER OF DARTERS TOTAL NUMBER OF DARTERS > 3° No. 134 October in individuals over 1 year of age. Two-year-old males of both species collected in October were dark red above the lateral line and orange-red ventrolater- ally. At this time ventrolateral coloration extended from the origin of the pelvic fin to the origin of the caudal fin in EF. zonistium and from the origin of the pelvic fin to midway through the caudal fin in E. pyrrhogaster. By late March ventrolateral body colora- tion was bright red midway through the caudal fin in E. zonistium and throughout all but the margins of the caudal fin in EF. pyrrhogaster. Commencement of spawning activity in aquaria was accompanied by a change in color of the chin and breast from blue-gray to lavender in E. zonistiwm and from gray-green to green in E. pyrrhogaster. By mid-July nuptial coloration in field-collected individuals had faded considerably; however, males of both species retained some red on the body and dorsal fins throughout the year. (J Etheostoma zonistium Etheostoma flabellare BB Etheostoma neopterum STREAM MARGIN RIFFLE POOL Figure 4. Number of darters captured in unit-effort seining by habitat type, West Fork Clarks River, Calloway County, Kentucky, May-July 1983. (Etheostoma pyrrhogaster Etheostoma lynceum HBEtheostoma nigrum EEJEtheostoma swaini 40 30 20 XM W000 q| NWA 'Y Y Z RACEWAY STREAM MARGIN Figure 5. Number of darters captured in unit-effort seining by habitat type, Terrapin Creek, Graves County, Kentucky, May-July 1983. POOL RIFFLE December 1989 The genital papilla of male E. zonistiwm was a white to cream, somewhat flattened, broad-based structure that terminated in a short tube (Fig. 6A, B). Mean papilla length was 0.8 mm (range 0.5-1.1, sp = 0.15) in 32 males that ranged in SL from 32 to 50 (x = 40.8) mm. Genital papillae of male E. pyrrhogaster were identical in structure and color to those of E. zonistium. Mean papilla length was 0.7 mm (range 0.5-1.0, sp = 0.11) in 29 males that ranged in SL from 32.8 to 49.7 (x= 41.2) mm. For both species, size and weight of testes gradually increased as the spawning season approached. For male E. zonistium, the relationship between weight of the testes x 1000/adjusted body weight (Y) and the month (X), with October = 1 and May = 8, was log Y= 0.152 + 0.323, with r= 0.932 (Fig. 7). In male E. pyrrhogaster, the relationship, with October = 1 and June = 9, was log Y= 0.391 + 0.275, with r= 0.852 (Fig. 8). All 1-year-old males collected in April (N= 11 E. zonistium, N= 9 E. pyrrhogaster) had enlarged testes and were potential spawners. The proportionally largest testes in E. zonistium equaled 1.6 percent of the ad- justed body weight and were found in a 3l-mm SL male collected on 18 April 1983. The proportionally Carney and Burr: Bandfin and Firebelly Darters in Western Kentucky or largest testes in E. pyrrhogaster equaled 1.4 percent of the adjusted body weight and were taken from a 37- mm SL male also collected on 18 April 1983. Reproductive Cycle of the Female Coloration of females showed no seasonal variation. Bright colors in female Etheostoma zonistium included a red ocellus in the first interradial membrane and a red band in the distal one-half of the spinous dorsal fin. Female E. pyrrhogaster also had a red ocellus; in some individuals, a submedian red band was apparent in the second dorsal fin. The genital papillae of female E. zonistium (Fig. 6C, D) and E. pyrrhogaster were thick, tubular structures white to cream in color. In E. zonistium, mean papilla length was 1.2 mm (range 0.8-1.7, sp = 0.20) in 47 females ranging in SL from 29.4 to 45.0 (x= 41.2) mm. Mean papilla length of female E. pyrrhogaster was 1.3 mm (range 1.0—1.6, sp = 0.18) in 31 individuals ranging in SL from 30.8 to 44.5 (x= 39.4) mm. As females became distended with maturing ova, the genital papillae shifted in position from lying against the abdomen to an angle varying from acute to nearly perpendicular to the abdominal wall. This change in position was accompanied by a change in the distal Figure 6. Genital papillae of Etheostoma zonistium from West Fork Clarks River, 18 April 1983: A) breeding male 43 mm SL, lateral view; B) ventral view of A; C) breeding female 33 mm SL, lateral view; D) ventral view of C. 6 Illinois Natural History Survey Biological Notes end of the papilla from somewhat rounded to flat- tened, as the diameter of the gonopore increased. Increased abdominal girth and change in position of the genital papillae were first evident in late February for females of both species. Small white ova appeared in females of both species in November. Intermediate-sized yellow ova were present in each species in February, and by late March mature ova were apparent. Mature ova were translucent with a pitlike indentation. This indenta- tion, also present in other darters (Page 1983:162), has recently been shown to serve as a micropyle (J. M. Grady, pers. comm.). Mean diameter of white ova in November-collected E. zonistium was 0.24 mm (range 0.17—0.34, sp = 0.062, N= 20). January-collected E. pyrrhogaster had white ova with a mean diameter of 0.26 mm (range 0.15—0.41, sp = 0.068, N= 20). Mean diameters of yellow ova in March-collected females were 0.78 mm (range 0.50—0.99, sp = 0.180, N= 20) in E. zonistium and 0.68 mm (range 0.54—0.86, sp = 0.098, N= 20) in E. pyrrhogaster. Mean diameters of mature ova in March- collected females were 1.08 mm (range 1.01-1.17, sp = 0.038, N= 20) in E. zonistium and 1.09 mm (range 1.02-1.18, sp = 0.048, N= 20) in E. pyrrhogaster. 5005 LOG Y=1.728+0.431X FEMALES r =0.974 ¢ mes r=0.932 — = © uu = > (a) Q 100 Q = w 50 = sy 8 S ° o °o . e = ® 10 2 Sate z fe} e) 5 ° 8 © 20) rs) 6 pers 6 — 4 5 8“ Log y=0.152+0.323x MALES 8 rr = MONTH Figure 7. Monthly variation in gonad weight relative to adjusted body weight in Etheostoma zonistium. Dots represent individual females; circles represent individual males. Data points for June and July were not included in the analysis but are presented to illustrate the decline in relative gonad weights. 1 OCT NOV DEC JAN FEB MAR APR MAY JUN JUL No. 134 Counts of yellow and mature ova in 1-year-old E. zonistium ranged from 41 to 137 (x= 77.0, sp = 25.17, N=9) (Table 3). In contrast, females of 1-year-old E. pyrrhogaster contained from 0 to 84 (x= 28.4, sp = 23.85, N= 9) yellow and mature ova (Table 4). Similar counts of 2- to 3-year-old females ranged from 98 to 155 (x= 127.5, sp = 20.25, N= 4) in E. zonistium and from 115 to 197 (x= 144.3, sp = 37.32, N= 3) in E. pyrrhogaster. Etheostoma simoterum females 12 months old con- tained 110 to 240 mature (orange or translucent) ova (Page & Mayden 1981). Total egg complements ranged from 288 to 496 (x= 382.8) in E. coosae (O'Neil 1981) and 228 to 864 (x= 481.2) in E. bailey: (Clayton 1984). Winn (1958b) estimated that 1- and 2-year-old female E. barrenense lay an average of 364 and 798 eggs per spawning season, respectively. His estimates are based on the premise that all ova present in the ovaries were spawned in a season. Some darters spawn more than one egg clutch per year (Hubbs 1985), as demonstrated for E. (Boleosoma) olmstedi (Gale & Deutsch 1985) and E. rafinesquez (Weddle 1989). Both species were shown to spawn over a period of several weeks at intervals ranging from 3 to 16 days (Gale & Deutsch 1985; Weddle 1989). 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