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CSE: MB Copyeditor: SRS JFB 195 DP RO OF Journal of Fish Biology (2003) 63, 1–5 doi:10.1046/j.1095-8649.2003.00195.x, available online at http://www.blackwell-synergy.com BRIEF COMMUNICATION Sex-specific survival and parasitism in three-spined sticklebacks: seasonal patterns revealed by molecular analysis K. E. A R N O L D *†, A. A D A M *, K. J. O R R *, R. G R I F F I T H S * I. B A R B E R ‡ AND *Division of Environmental and Evolutionary Biology, Graham Kerr Building, University of Glasgow, Glasgow G12 8QQ, U.K. and ‡Institute of Biological Sciences, University of Wales Aberystwyth, Aberystwyth, Ceredigion SY23 3DA, U.K. TE (Received 3 October 2002, Accepted 27 June 2003) RR EC A molecular method of identifying sex in three-spined sticklebacks Gasterosteus aculeatus showed that adult males had a higher prevalence of dermal Glugea anomala cysts than adult females, and young-of-the-year had more than adults. At the end of the breeding season, as predicted, the adult sex ratio became female biased and there was a disproportionate increase in # 2003 The Fisheries Society of the British Isles G. anomala parasitism in adult males. Key words: Glugea anomala; molecular sexing; parasites; sex ratio; three-spined stickleback. UN CO A sex difference in vulnerability to parasites, and therefore mortality, is thought to be a viability cost associated with sexual selection (Moore & Wilson, 2002). Thus, the population sex ratio is expected to vary temporally within species that possess sexually selected traits (Andersson, 1994). This bias in sex ratio is only expected to arise among sexually mature adults not in juveniles, so will have important implications for population structure. Procuring information regarding temporal changes in the sex ratio of field populations, however, is often difficult because of problems in non-destructively identifying the sex of individuals. In fishes, such problems are exacerbated in juveniles and in species that lack sexual dimorphism, or are only morphologically distinguishable during the breeding season. In species with chromosomal sex determination, molecular techniques allow the unambiguous assignment of the sex of fishes regardless of their age, reproductive status or condition. In the present study, a recently developed molecular method (Griffiths et al., 2000) was used to determine sex differences in microsporean parasitism, body size and survival throughout the season in a population of three-spined sticklebacks Gasterosteus aculeatus L. †Author to whom correspondence should be addressed. Tel.: þ44 (0) 141 3302898; fax: þ44 (0) 141 3305971; email: [email protected] 1 # 2003 The Fisheries Society of the British Isles 2 K. E. ARNOLD ET AL. UN CO RR EC TE DP RO OF From March to October 2000 inclusive, monthly three-spined stickleback samples were taken from Inverleith Pond. This is a small (c. 1 ha), shallow (c. 1 m deep) artificial lake close to Edinburgh, U.K. (55 550 N; 03 100 W) and is connected to another smaller pond. Three-spined sticklebacks are the only species of fish in the lake, and they are subject to predation by gulls (Laridae). In this population, the bulk of the diet consists of chironomids and nematodes, but this varies with season (Tierney, 1991). On each sampling day, three types of capture technique were employed in order to minimize sex-biased sampling. Eight baited bottle traps were placed at random throughout the pond for 30–60 min c. every 1–2 h over a 6 h period. A 1 m hand-trawl (4 mm mesh) was also used to collect individuals, and hand nets (2 mm mesh) were used to catch both adults and young-of-the-year (YOY) from the periphery of the pond and around submerged obstacles. Standard body length (LS to 01 mm) and wet mass (to 001 g) of all fish were recorded. During the breeding season (May to August), when sexing of adult three-spined sticklebacks can be performed visually using cues from eye and throat colour (Wootton, 1976), the sex was estimated based on these morphological cues at the time of capture in addition to the molecular method. During the sampling period the study population was infected with Glugea anomala Moniez, an obligate intracellular microsporidian parasite, which cause visible white dermal cysts, up to 8 mm in diameter, on the skin surface of infected fishes. Three-spined sticklebacks become infected when spores, released from cysts of dying or dead fish, are ingested either directly, or via contaminated invertebrates. Hatched spores infect individual host cells, which undergo hypertrophy, forming a cyst in which the parasite reproduces vegetatively. Infection with microsporideans such as G. anomala is associated with severe pathology and mortality, particularly in young fishes (Canning, 1977). Because each cyst is founded by a single invading parasite, the number of visible dermal cysts was counted to provide an index of the level of G. anomala parasitism. Although the index is not a precise measure, because the cysts can merge in heavy infections and may also be present internally, the number of visible dermal cysts was regarded as an acceptable approximation of the relative infection level. A total of 913 individuals were collected and a small spine clipping (c. 3 mm) was taken from one of the ventral bony spines of 745 fish for molecular sexing before being returned to the pond. Small fry were collected whole. The results of molecular sexing of adults sampled during the breeding season agreed 100% with estimates of their sex based on morphological cues (Griffiths et al., 2000). A logistic regression model (GLM version 4.09) was performed to examine the sex of individuals in relation to a number of predictors. The following were entered into the model as factors; capture method (both types of net or trap) and ‘age’ (YOY or adult, discriminated by body size). The month of capture (March to October) was entered into the model as a co-variate. Statistics were based on the w2 distribution. Adult males had more G. anomala cysts than females (ANOVA, d.f. ¼ 1 and 592, P ¼ 002), but there was no sex difference in G. anomala cysts among YOY (ANOVA, d.f. ¼ 1 and 149, P > 05). The adult sex difference in G. anomala infection varied throughout the year, with males becoming relatively more infected at the end of the year (Fig. 1; two-way ANOVA, sex month, d.f. ¼ 6 # 2003 The Fisheries Society of the British Isles, Journal of Fish Biology 2003, 63, 1–5 3 SEX-SPECIFIC PARASITISM (a) DP RO OF 2 Log10 number of cysts 1 0 2 (b) 1 0 March April May June July Month August September October TE FIG. 1. Box-and-whisker plots showing the number of dermal Glugea anomala cysts (logþ1 transformed) on (a) adult and (b) young-of-the-year Gasterosteus aculeatus caught at different times of the year. Males (&) and females ( ) are shown separately. Horizontal bars are medians, boxes are interquartile range, whiskers show 95% CI and *, outliers. UN CO RR EC and 594, P ¼ 0001). YOY fish had more dermal G. anomala cysts than adults (ANOVA d.f. ¼ 1 and 743, P < 00001). Among YOY, G. anomala parasitism rate increased with age (two-way ANOVA, d.f. ¼ 3 and 150, P < 00001), but there were no sex differences (Fig. 1). Overall there was a female biased sex ratio in this population (M : F ¼ 343 : 402; w2, P < 005). This bias, however, tended to be among adults (M : F ¼ 277 : 324; w2, P ¼ 0055), not among YOY (M : F ¼ 66 : 78; w2, P > 03). The GLM analyses revealed that the sex ratio varied between months (Fig. 2; GLM Null model – scaled deviance ¼ 10281, d.f. ¼ 744, month of capture d.f. ¼ 1, P < 0025). The sample was significantly male biased in May (M : F ¼ 37 : 15; w2, P ¼ 0002), possibly because males were easier to catch during the spawning season. Males are territorial and nest close to the edges of the Inverleith Pond whereas females form shoals and move around the pond (inshore and in the middle) (unpubl. data). The adult population was female biased towards the end of the season (Fig. 2), as predicted in a species with exclusive male parental care. This female bias amongst adult fish was significant in August (M : F ¼ 62 : 93, w2, P ¼ 0013). Neither age nor capture method influenced the sex of individuals in the model. Adult females were longer (Fig. 2; ANOVA, d.f. ¼ 1 and 592, P < 0001) and heavier than males (ANOVA, d.f. ¼ 1 and 592, P < 0001), but YOY were not significantly size dimorphic (ANOVA, d.f. ¼ 1 and 149, LS: P > 05 and mass: P > 04). Adult mass differences were at least partially due to females being gravid from April to August, but females were also longer than males. Amongst the three-spined sticklebacks sampled from this population, an even sex ratio was found among YOY and adults at the beginning of the breeding # 2003 The Fisheries Society of the British Isles, Journal of Fish Biology 2003, 63, 1–5 4 K. E. ARNOLD ET AL. 20 March DP RO OF 10 0 20 April 10 0 20 May 10 Frequency 0 20 June 10 0 20 July 10 0 20 August 10 0 20 September 20 TE 10 0 October 10 0 CO RR EC 10 12 14 16 18 20 22 24 26 28 30 32 34 36 38 40 42 44 46 48 50 52 54 56 58 60 62 64 66 68 70 Length (mm) FIG. 2. Standard length frequencies ( , young-of-the-year and &, adults) and sex ratios (*, male and *, female) for each month of capture. Mean standard lengths of males (--*--) and females (-- --) amongst adult and YOY samples are also shown. UN season. The sex ratio became female biased during and after breeding, as predicted from the sex differences in nuptial colouration, territorial and parental care behaviour. Although a variety of sampling techniques was used, it is unclear if these differences were due to a season–sex interaction in catchability, or higher male than female mortality rates. Adult males harboured more G. anomala cysts than females, these sex differences in infection level might be due to the heavy demands of sexual selection (Moore & Wilson, 2002) and fatherhood, or sex differences in the rate of encountering parasites because of differences in ecology (Reimchen & Nosil, 2001). Parasitism rates in both adults and YOY increased towards the end of the summer. Among adults, males were disproportionately affected by G. anomala especially in July, just after the main peak in paternal care. References Andersson, M. (1994). Sexual Selection. Princeton, NJ: Princeton University Press. Canning, E. U. (1977). Microsporidia. In Parasitic Protozoa, Vol. IV (Kreier, J. P., ed.). pp. 155–196. London: Academic Press. # 2003 The Fisheries Society of the British Isles, Journal of Fish Biology 2003, 63, 1–5 SEX-SPECIFIC PARASITISM 5 UN CO RR EC TE DP RO OF Griffiths, R., Orr, K. J., Adam, A. & Barber, I. (2000). DNA sex identification in the three-spined stickleback. Journal of Fish Biology 57, 1331–1334. doi: 10.1006/ jfbi.2000.1386. Moore, S. L. & Wilson, K. (2002). Parasites as a viability cost of sexual selection in natural populations of mammals. Science 297, 2015–2018. Reimchen, T. E. & Nosil, P. (2001). Ecological causes of sex-biased parasitism in threespine stickleback. Biological Journal of the Linnean Society 73, 51–63. Tierney, J. F. (1991). Studies on the life history of Schistocephalus solidus: field observations and laboratory experiments. PhD Thesis. University of Glasgow. Wootton, R. J. (1976). The Biology of the Sticklebacks. 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