Žiga FIŠER et al: The utility of non-genetic data collected during genetic monitoring... / »SOS Proteus« – FIELD NOTE Biotehniška fakulteta Univerze v Ljubljani in Nacionalni inštitut za biologijo, Ljubljana, 2017 35 The utility of non-genetic data collected during genetic monitoring of proteus populations Uporabnost ne-genetskih podatkov, pridobljenih med genetskim monitoringom močerila Žiga FIŠER1, Valerija ZAKŠEK1, Magdalena NĂPĂRUȘ-ALJANČIČ2, Gregor ALJANČIČ2, Teo DELIĆ1, Peter TRONTELJ1 1Department of Biology, Biotechnical Faculty, University of Ljubljana, Jamnikarjeva 101, SI-1000 Ljubljana, Slovenia; E-mails: ziga.fiser@bf.uni-lj.si, valerija.zaksek@bf.uni-lj.si, teo.delic@bf.uni-lj.si, peter.trontelj@bf.uni-lj.si 2Tular Cave Laboratory, Society for Cave Biology, Oldhamska cesta 8a, SI-4000 Kranj, Slovenia; E-mails: magda.aljancic@gmail.com, gregor.aljancic@guest.arnes.si Proteus anguinus is the only obligate cave vertebrate of the European continent (Aljančič et al. 1993, Parzefall et al. 1999) and a Dinaric Karst endemic (Sket 1997). In the past decades, population declines of this charismatic species have been reported from a number of localities (Sket 1997, Hudoklin 2011). However, only recently initiatives have been undertaken to develop and establish schemes for monitoring population numbers and distribution. As a part of these initiatives, various new methodological approaches have been tested: a) in situ underwater animal tagging (Balázs et al. 2015), b) detection via environmental DNA (Aljančič et al. 2014, Gorički et al. 2017, Vörös et al. 2017), and c) genetic monitoring (Trontelj & Zakšek 2016). Genetic monitoring as described in Trontelj & Zakšek (2016) requires catching substantial numbers of live proteus. In order to maximize the amount of scientific information obtained once an individual is caught, besides DNA, a number of other biological data are collected. These include body length and mass as well as observations on anomalies such as injuries, pigmentation, gravidity, parasites, etc. Body size can be used to assess population demography and, conjointly with data on injuries and parasites, even health of populations. Taking into account possible fixed differences in body size between proteus phyletic lineages, ecological conditions of cave systems can be inferred. Long term monitoring of animals’ body size reveals life-history traits, which have been so far investigated mostly in captive individuals bred in cave laboratories (e.g. Briegleb 1962, Durand & Delay 1981, Juberthie et al. 1996, Aljančič & Aljančič 1998). In this contribution, we present first results based on non-genetic data obtained during the fieldwork for the genetic monitoring of proteus. In 2015 and 2016, we extensively sampled proteus in several Slovenian caves. These were selected to represent populations from all major mitochondrial DNA lineages of proteus (Trontelj et al. 2009). Each year, we caught about 900 individuals, most of them in the Postojna-Planina Cave System. This is probably the largest dataset ever assembled for natural populations of proteus. Animals were caught using diving equipment and hand nets. First, a DNA sample was non-invasively taken from each individual using a skin swab. Then, body length and mass were measured, the animal was thoroughly examined for anomalies, photographed, and released back to the cave river. The demographic structure of populations was tentatively assessed by estimating the proportion of reproductively capable individuals in a population. Relying on data from proteus bred in captivity (Durand & Delay 1981, Juberthie et al. 1996, Voituron et al. 2011), we assumed that 20 cm long animals are at least 18 years old and almost certainly already sexually mature. According to preliminary results, the proportion of reproductively capable individuals differed between our samples from different proteus populations. For example, in the Črna jama population we caught almost exclusively sexually mature animals, while in the cave Vetrovna jama pri Laški kukavi these represented only about one quarter of all individuals found. The relationship between body length and mass was statistically modelled using a power function (see legend to Fig. 1 for more details). Preliminary results on the length-to-mass relationship in four proteus populations for which we had roughly similar sample sizes are shown in Fig. 1. Substantial differences were found between some of these populations. The populations from the subterranean Pivka and Reka Rivers differed most. At the maximal length of about 30 cm, animals Žiga FIŠER et al: The utility of non-genetic data collected during genetic monitoring... / »SOS Proteus« – FIELD NOTE NATURA SLOVENIAE 19(1): 35-37 36 from the subterranean Reka River were almost twice as heavy as animals from the subterranean Pivka River. Whether this difference is genetically determined or the consequence of differences in food abundance and quality between cave systems, remains to be investigated. Some individuals, whose mass was much lower than expected for animals of their length, were found to be infested with parasites. If a connection between infestation and low body mass is confirmed by additional cases, such outliers could be used to estimate population health. In Planina Cave, about 6% of individuals had some minor body injuries, mostly cuts in the tail fin and missing toes. This percentage was similar in both years of sampling, as was the percentage of individuals with at least some darkly pigmented patches of skin (about 7%). Genetic identification of captured individuals provides an opportunity to assess changes in body size. Within a year, none of the 73 so far identified recaptured individuals from Planina Cave has grown more than one centimeter in length. Their change in mass was much more variable, showing increase and decrease of up to 8 g. As body mass can markedly change already after feeding or defecation, this variability needs to be taken into account before making conclusions about changes in body mass. Taken together, the fieldwork undertaken in our genetic monitoring scheme produces, as a side product, a number of additional data that are relevant for the biology and conservation of this unique and enigmatic amphibian. Acknowledgements We are grateful to Aja Zamolo, Ana Miglioranca, Andrej Hudoklin, Anja Kos, Borut Lozej, Ciril Mlinar Cic, Claudio Bratoš, Daniela Eilers, Dare Hribar, Darja Kolar, Edvard Gregorčič, Ester Premate, Franc Kljun, Frank Körner, Gabriela Enache, Gregor Bračko, Jan Gojznikar, Jerneja Rovtar, Kaja Vukotić, Katarina Novak, Katarina Tušar, Katja Leban, Lilijana Bizjak Mali, Lisa Fisler, Ljerka Lah, Lucija Slemenšek, Luka Mrzelj, Maja Jelenčič, Maja Sever, Manca Velkavrh, Marjeta Konec, Matej Simčič, Mike Patton, Mitja Prelovšek, Nataša Sivec, Nika Šumer, Primož Gnezda, Rok Kostanjšek, Rožle Kaučič, Ryan Riegg, Sandi Vidrih, Sašo Weldt, Sebastjan Kovač, Selena Trontelj, Špela Borko, Špela Gorički, Tadeja Balanč, Tajda Gredar, Tatjana Kordiš, Tobias Trontelj, Urška Ratajc, Vinko Kukman, Žan Kuralt, and Živa Hanc for their help with the fieldwork. This study was funded by the Slovenian Research Agency (Project number L1-6731), and co-funded by the Slovenian Ministry of the Environment and Spatial Planning and the Centre for Cartography of Fauna and Flora (CKFF). The research was performed in accordance with permits No. 35601-132/2014-4 and No. 35601- 26/2016-4 issued by the Slovenian Environment Agency. References Aljančič G., Aljančič M. (1998): Človeška ribica (Proteus anguinus). Proteus 61(2): 83-87. Aljančič G., Gorički Š., Năpăruş M., Stanković D., Kuntner M. (2014): Endangered Proteus: combining DNA and GIS analyses for its conservation. In: Sackl P., Durst R., Kotrošan D., Stumberger B. (Eds.), Dinaric Karst Poljes – Floods for Life. EuroNatur, Radolfzell, pp. 71-75. Aljančič M., Bulog B., Kranjc A., Josipovič, D., Sket B., Skoberne P. (1993): Proteus: the mysterious ruler of Karst darkness. Vitrum, Ljubljana, 75 pp. Balázs G., Lewarne B., Herczeg G. (2015): In situ underwater tagging of aquatic organisms: a test using the cave-dwelling olm, Proteus anguinus. Ann. Zool. Fennici 52(3): 160-166. Briegleb W. (1962): Zur Biologie und Ökologie des Grottenolms (Proteus anguinus Laur. 1768). Zeitschrift für Morphol. und Ökologie der Tiere 51(3): 271-334. Durand J.P., Delay B. (1981): Influence of temperature on the development of Proteus anguinus (Caudata: Proteidae) and relation with its habitat in the subterranean world. J. Therm. Biol. 6(1): 53-57. Gorički Š., Stanković D., Snoj A., Kuntner M., Jeffery W., Trontelj P., Pavićević M., Grizelj Z., Năpăruș-Aljančič M., Aljančič G. (2017): Environmental DNA in subterranean biology: range extension and taxonomic implications for Proteus. Sci. Rep.-UK 7: 45054. Žiga FIŠER et al: The utility of non-genetic data collected during genetic monitoring... / »SOS Proteus« – FIELD NOTE NATURA SLOVENIAE 19(1): 35-37 37 Hudoklin A. (2011): Are we guaranteeing the favourable status of Proteus anguinus in the Natura 2000 network in Slovenia? In: Prelovšek M., Zupan Hajna N. (Eds.), Pressures and Protection of the Underground Karst – Cases from Slovenia and Croatia. Inštitut za raziskovanje krasa ZRC SAZU, Postojna, pp. 169-181. Juberthie C., Durand J., Dupuy M. (1996): La reproduction des protées (Proteus anguinus): bilan de 35 ans d'élevage dans les grottes- laboratoires de Moulis et d'Aulignac. Mém. Biospéol. 23: 53-56. Parzefall J., Durand J.P., Sket B. (1999): Proteus anguinus Laurenti, 1768 – Grottenolm. In: Grossenbacher K., Thiesmeier B. (Eds.), Handbuch der Reptilien und Amphibien Europas. Band 4/I: Schwanzlurche I. Aula-Verlag, Wiesbaden, pp. 57-76. Sket B. (1997): Distribution of Proteus (Amphibia: Urodela: Proteidae) and its possible explanation. J. Biogeogr. 24(3): 263-280. Trontelj P., Douady C.J., Fišer C., Gibert J., Gorički Š., Lefébure T., Sket B., Zakšek V. (2009): A molecular test for cryptic diversity in ground water: how large are the ranges of macrostygobionts? Freshwater Biol. 54: 727-744. Trontelj P., Zakšek V. (2016): Genetic monitoring of Proteus populations. Nat. Slov. 18(1): 53-54. Voituron Y., de Fraipont M., Issartel J., Guillaume O., Clobert J. (2011): Extreme lifespan of the human fish (Proteus anguinus): a challenge for ageing mechanisms. Biol. Lett. 7(1): 105-107. Vörös J., Márton O., Schmidt B.R., Gál J.T., Jelić D. (2017): Surveying Europe’s only cave-dwelling chordate species (Proteus anguinus) using environmental DNA. PLoS One 12(1): e0170945. Figure 1. Relationship between body length and mass in four populations of Proteus anguinus. The power function M = a Lb (M – mass, L – length, a – intercept, b – slope) was linearized and fitted to the log-transformed data. When length increases by 1%, mass increases by b%. Slika 1. Odnos med telesno dolžino in maso pri štirih populacijah močerila (Proteus anguinus). Odnos opisuje potenčna funkcija M = a Lb (M – masa, L – dolžina, a – presečišče, b – naklon), ki smo jo najprej linearizirali, nato pa ocenili vrednosti parametrov a in b za logaritemsko transformirane podatke. Pri povečanju telesne dolžine za 1 % se masa poveča za b %.