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1. Adaptation of sea turtles to climate warming: Will phenological responses be sufficient to counteract changes in reproductive output?

Author

Fuentes, M. M. P. B., Santos, A. J. B., Abreu‐grobois, A., Briseño‐dueñas, R., Al‐khayat, J., Hamza, Samir, Saliba, S., Anderson, D., Rusenko, K. W., Mitchell, N. J., Gammon, M., Bentley, B. P., Beton, D., Booth, D. T. B., Broderick, A. C., Colman, L. P., Snape, R. T. E., Calderon‐campuzano, M. F., Cuevas, E., Lopez‐castro, M. C., Flores‐aguirre, C. D., Mendez de la cruz, F., Segura‐garcia, Y., Ruiz‐garcia, A., Fossette, S., Gatto, C. R., Reina, R. D., Girondot, M., Godfrey, M., Guzman‐hernandez, V., Hart, C. E., Kaska, Y., Lara, P. H., Marcovaldi, M. A. G. D., Leblanc, A. M., Rostal, D., Liles, M. J., Wyneken, J., Lolavar, A., Williamson, S. A., Manoharakrishnan, M., Pusapati, C., Chatting, M., Mohd salleh, S., Patricio, A. R., Regalla, A., Restrepo, J., Garcia, R., Santidrián tomillo, P., Sezgin, C., Shanker, K., Tapilatu, F., Turkozan, O., Valverde, R. A., Williams, K., Yilmaz, C., Tolen, N., Nel, R., Tucek, J., Legouvello, D., Rivas, M. L., Gaspar, C., Touron, M., Genet, Q., Salmon, M., Araujo, M. R., Freire, J. B., Castheloge, V. D., Jesus, P. R., Ferreira, P. D., Paladino, F. V., Montero‐flores, D., Sozbilen, D., Monsinjon, Jonathan, Fuentes, M. M. P. B., Santos, A. J. B., Abreu‐grobois, A., Briseño‐dueñas, R., Al‐khayat, J., Hamza, Samir, Saliba, S., Anderson, D., Rusenko, K. W., Mitchell, N. J., Gammon, M., Bentley, B. P., Beton, D., Booth, D. T. B., Broderick, A. C., Colman, L. P., Snape, R. T. E., Calderon‐campuzano, M. F., Cuevas, E., Lopez‐castro, M. C., Flores‐aguirre, C. D., Mendez de la cruz, F., Segura‐garcia, Y., Ruiz‐garcia, A., Fossette, S., Gatto, C. R., Reina, R. D., Girondot, M., Godfrey, M., Guzman‐hernandez, V., Hart, C. E., Kaska, Y., Lara, P. H., Marcovaldi, M. A. G. D., Leblanc, A. M., Rostal, D., Liles, M. J., Wyneken, J., Lolavar, A., Williamson, S. A., Manoharakrishnan, M., Pusapati, C., Chatting, M., Mohd salleh, S., Patricio, A. R., Regalla, A., Restrepo, J., Garcia, R., Santidrián tomillo, P., Sezgin, C., Shanker, K., Tapilatu, F., Turkozan, O., Valverde, R. A., Williams, K., Yilmaz, C., Tolen, N., Nel, R., Tucek, J., Legouvello, D., Rivas, M. L., Gaspar, C., Touron, M., Genet, Q., Salmon, M., Araujo, M. R., Freire, J. B., Castheloge, V. D., Jesus, P. R., Ferreira, P. D., Paladino, F. V., Montero‐flores, D., Sozbilen, D., and Monsinjon, Jonathan

Abstract

Sea turtles are vulnerable to climate change since their reproductive output is influenced by incubating temperatures, with warmer temperatures causing lower hatching success and increased feminization of embryos. Their ability to cope with projected increases in ambient temperatures will depend on their capacity to adapt to shifts in climatic regimes. Here, we assessed the extent to which phenological shifts could mitigate impacts from increases in ambient temperatures (from 1.5 to 3°C in air temperatures and from 1.4 to 2.3°C in sea surface temperatures by 2100 at our sites) on four species of sea turtles, under a “middle of the road” scenario (SSP2‐4.5). Sand temperatures at sea turtle nesting sites are projected to increase from 0.58 to 4.17°C by 2100 and expected shifts in nesting of 26–43 days earlier will not be sufficient to maintain current incubation temperatures at 7 (29%) of our sites, hatching success rates at 10 (42%) of our sites, with current trends in hatchling sex ratio being able to be maintained at half of the sites. We also calculated the phenological shifts that would be required (both backward for an earlier shift in nesting and forward for a later shift) to keep up with present‐day incubation temperatures, hatching success rates, and sex ratios. The required shifts backward in nesting for incubation temperatures ranged from −20 to −191 days, whereas the required shifts forward ranged from +54 to +180 days. However, for half of the sites, no matter the shift the median incubation temperature will always be warmer than the 75th percentile of current ranges. Given that phenological shifts will not be able to ameliorate predicted changes in temperature, hatching success and sex ratio at most sites, turtles may need to use other adaptive responses and/or there is the need to enhance sea turtle resilience to climate warming.

Published
2023
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2. Monitoring micro-litter ingestion in marine fish : A harmonized protocol for MSFD and RSCS areas: version 01

Author

Matiddi, M., Pham, Christopher K., Anastasopoulou, A., Andresmaa, E., Avio, C.G., Bianchi, J., Chaieb, O., Palazzolo, L., Darmon, G., de Lucia, G.A., Deudero, S., Sozbilen, D., Eriksson, J., Fischer, E., Gomez, M., Herrera, A., Hattia, E., Kaberi, H., Kaska, Y., Kuhn, S., Lips, I., Miaud, C., Gambaiani, D., Nelms, S., Piermarini, R., Regoli, F., Sbrana, A., Setala, O., Settiti, S., Soederberg, L., Tomas, J., Tsangaris, C., Vale, M., Valente, T., Silvestri, C., Matiddi, M., Pham, Christopher K., Anastasopoulou, A., Andresmaa, E., Avio, C.G., Bianchi, J., Chaieb, O., Palazzolo, L., Darmon, G., de Lucia, G.A., Deudero, S., Sozbilen, D., Eriksson, J., Fischer, E., Gomez, M., Herrera, A., Hattia, E., Kaberi, H., Kaska, Y., Kuhn, S., Lips, I., Miaud, C., Gambaiani, D., Nelms, S., Piermarini, R., Regoli, F., Sbrana, A., Setala, O., Settiti, S., Soederberg, L., Tomas, J., Tsangaris, C., Vale, M., Valente, T., and Silvestri, C.

Published
2021

3. Prevalence and pathology of Lernaea cyprinacea (Crustacea: Lernaeidae)

Author

Innal, D, Sozbilen, D, and Ozmen, O

Subjects
Anchor worms, disease, parasitic copepods, parasitism
Abstract

This is a report of the first record of the occurrence of Lernaea cyprinacea on tadpoles of Pelophylax bedriagae, a frog species native from Karpuzcay Creek, Antalya, Turkey. A total of 20 tadpoles of P. bedriagae were examined and 14 (70%) specimens were infected. A maximum of two parasites per host was found, primarily around the cloaca. In general, slight to moderate hyperemia was noticed around the parasite. Typically, granuloma form in the tissues around the parasite. Histopathological examination revealed that hemorrhages and pathological lesions such as dermal erosions, and a chronic inflammatory reaction in skin and muscle were present at the site of parasite attachment. C1 [Innal, D.] Burdur Mehmet Akif Ersoy Univ, Dept Biol, TR-15030 Burdur, Turkey. [Sozbilen, D.] Pamukkale Univ, Acipayam Vocat Sch, Dept Vet, Denizli, Turkey. [Ozmen, O.] Burdur Mehmet Akif Ersoy Univ, Dept Pathol, Fac Vet Med, TR-15030 Burdur, Turkey.

Published
2019

4. for Good Environmental Status

Author

Matiddi, M, deLucia, GA, Silvestri, C, Darmon, G, Tomas, J, Pham, CK, Camedda, A, Vandeperre, F, Claro, F, Kaska, Y, Kaberi, H, Revuelta, O, Piermarini, R, Daffina, R, Pisapia, M, Genta, D, Sozbilen, D, Bradai, MN, Rodriguez, Y, Gambaiani, D, Tsangaris, C, Chaieb, O, Moussier, J, Loza, AL, and Miaud, C

Subjects
Environmental Sciences, Issue 147, Sea turtle, plastic ingestion, necropsy, marine litter, MSFD, EcAp process, good environmental status, thresholds
Abstract

The following protocol is intended to respond to the requirements set by the European Union's Marine Strategy Framework Directives (MSFD) for the D10C3 Criteria reported in the Commission Decision (EU), related to the amount of litter ingested by marine animals. Standardized methodologies for extracting litter items ingested from dead sea turtles along with guidelines on data analysis are provided. The protocol starts with the collection of dead sea turtles and classification of samples according to the decomposition status. Turtle necropsy must be performed in authorized centers and the protocol described here explains the best procedure for gastrointestinal (GI) tract isolation. The three parts of the GI (esophagus, stomach, intestine) should be separated, opened lengthways and contents filtered using a 1 mm mesh sieve. The article describes the classification and quantification of ingested litter, classifying GI contents into seven different categories of marine litter and two categories of natural remains. The quantity of ingested litter should be reported as total dry mass (weight in grams, with two decimal places) and abundance (number of items). The protocol proposes two possible scenarios to achieve the Good Environmental Status (GES). First: "There should be less than X% of sea turtles having Y g or more plastic in the GI in samples of 50-100 dead turtles from each sub-region", where Y is the average weight of plastic ingested and X% is the percentage of sea turtles with more weight (in grams) of plastic than Y. The second one, which considers the food remain versus plastic as a proxy of individual health, is: "There should be less than X% of sea turtles having more weight of plastic (in grams) than food remains in the GI in samples of 50-100 dead turtles from each sub-region". C1 [Matiddi, Marco; Silvestri, Cecilia; Piermarini, Raffaella; Daffina, Roberto; Pisapia, Marco; Genta, Daniela] Italian Natl Inst Environm Protect & Res ISPRA, Rome, Italy. [deLucia, Giuseppe A.; Camedda, Andrea] Inst Coastal Marine Environm Natl Res Council IAM, Rome, Italy. [Darmon, Gaelle; Gambaiani, Delphine; Miaud, Claude] Univ P Valery, PSL Res Univ, UMR 5175 CE3FE,EPHE, CNRS,UM,IRD,INRA,SupAgro,Biogeog & Ecol Vertebras, Montpellier, France. [Tomas, Jesus; Revuelta, Ohiana] Univ Valencia, Cavanilles Inst Biodivers & Evolutionary Biol, Valencia, Spain. [Pham, Christopher K.; Vandeperre, Frederic; Rodriguez, Yasmina] Univ Acores, Dept Oceanog & Pescas, Inst Mar Okeanos, Ponta Delgada, Portugal. [Vandeperre, Frederic] Univ Acores, MARE Marine & Environm Sci Ctr, Ponta Delgada, Portugal. [Claro, Francoise; Moussier, Judicaelle] Museum Natl Hist Nat, Paris, France. [Kaska, Yakup; Sozbilen, Dogan] Pamukkale Univ, Sea Turtle Res & Applicat Ctr DEKAMER, Pamukkale, Turkey. [Kaberi, Helen; Tsangaris, Catherine] Hellenic Ctr Marine Res, Inst Oceanografy, Anavyssos, Greece. [Bradai, Mohamed N.; Chaieb, Olfa] INSTM, Salammbo, Tunisia. [Loza, Ana L.] Univ Las Palmas Gran Canaria, Las Palmas Gran Canaria, Spain.

Published
2019

6. Protected Area: An important foraging ground with an increasing

Author

Baskale, E, Sozbilen, D, Katilmis, Y, Azmaz, M, and Kaska, Y

Subjects
Caretta caretta, Chelonia mydas, Bycatch, Stranding, Fethiye-Gocek specially protected area, Foraging ground
Abstract

The Fethiye-Gocek Specially Protected Area (SPA) is an important protected area in Turkey that includes important loggerhead turtle nesting beaches and marine habitats for sea turtles. Here, we analysed the number of stranded loggerhead and green sea turtles in the Fethiye-Gocek SPA, Turkey. A total of 139 dead sea turtles (102 loggerhead and 37 green turtles) were found between the years 2000 and 2016. The majority of stranded loggerheads were considered to be adults (77.45%), while the majority of stranded green turtles were immature individuals (86.49%). Mean annual strandings were 6.0 individuals for loggerhead turtles and 2.2 individuals for green turtles. The main cause of strandings was determined as incidental catch in fishing gear (51% for loggerhead turtle, 41% for green turtle) and marine vehicle collisions (23% for loggerhead turtle and 27% for green turtles). Strandings were encountered all year round. These results suggest that the Fethiye-Gocek SPA should not be only considered as a seasonal nesting ground for loggerhead turtles, but also a year-round feeding ground for both species. An increase in the number of stranded turtles in the study area suggests that negative anthropogenic effects on sea turtle populations are relatively high and that conservation and monitoring efforts on the nesting beaches are not sufficient to protect sea turtle populations. Research is required to identify the fisheries' segments and metiers responsible for sea turtle mortality in order to develop bycatch mitigation, prioritising the marine habitats of the Fethiye-Gocek SPA.

Published
2018

7. and injured loggerhead sea turtles (Caretta caretta) in Turkey

Author

Sozbilen, D and Kaska, Y

Subjects
Loggerhead sea turtle, Caretta caretta, plasma biochemistry, steroid, hormone, health, rehabilitation, KAMER, Sea Turtle Rescue Center, Mugla, Turkey
Abstract

The biochemical blood parameters of 22 (7 foraging, 7 nesting, and 8 injured) loggerhead sea turtles (Caretta caretta) from the southwest coast of Turkey were investigated. A total of 27 blood variables were analyzed in three groups (plasma enzymes, plasma metabolites, and plasma ions), and 4 steroid hormones: testosterone (T) estradiol (E-2), progesterone (Pro), and corticosterone (B). Triglyceride, cholesterol, low-density lipoprotein, very low-density lipoprotein, magnesium, and phosphorus were higher in nesting females; urea was high in foraging individuals; and sodium, potassium, and chloride were lower while estradiol levels were higher in injured individuals. In addition, plasma steroid hormone levels T, Pro, and B were assessed in healthy and stranded individuals. The results of the present study provide valuable blood parameters for the medical care of the species in rescue centers and help us to understand the physiological response of loggerhead sea turtles to different conditions.

Published
2018

8. Natural and anthropogenic factors affecting the nest-site selection of

Author

Kaska, Y, Baskale, E, Urhan, R, Katilmis, Y, Gidis, M, Sari, F, Sozbilen, D, Canbolat, AF, Yilmaz, F, Barlas, M, Ozdemir, N, and Ozkul, M

Subjects
Loggerhead Turtle, Caretta caretta, nest site selection, anthropogenic, factors, beach protection, beach rocks, water sports
Abstract

The nesting activities of Loggerhead Turtles (Caretta caretta Stejneger, 1902) and anthropogenic factors affecting them were monitored over 7 years (2002-2008) on Dalaman-Sarigerme beach, one of the main nesting grounds in Turkey. Out of the 2620 nesting emergences recorded during the entire study period, only 645 (24.6%) resulted in successful nesting, giving an annual mean number of nests of 92. The collective number of eggs in these nests numbered 50239, with 40079 (79.8%) of them producing hatchlings. Out of the total number of eggs laid, 8128 (16.2%) resulted in dead embryos and 2032 (4.0%) in unfertilized eggs. The mean incubation period averaged 49 days (range 40-67 days) and the mean clutch size was 79.0 (range 18-150 eggs). Turtle nests were more concentrated on the undeveloped parts of the beach than on developed parts. In the other sections, few emergences occurred and either no or few nests were recorded. In Section 1, which contained hotels and water sports facilities, only a few non-nesting emergences were observed. Of the number of nests that were observed, 32% were laid in Section II, which contained recently built hotels, 60% were in Section III and 8% were in Section IV, the undeveloped portion containing beach rocks. There is very clear evidence that the Loggerhead Turtles are shifting their nesting sites to the undisturbed sites along the beach. The negative factors that seem to be affecting them include water sports, hotel lights and beach rocks. In order to protect sea turtles, there needs to be a better understanding of how effective beach protection can be established.

Published
2010

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