A bloom of Lyngbya majuscula in Shoalwater Bay, Queensland, Australia: An important feeding ground for the green turtle (Chelonia mydas)

Lyngbya majuscula, a toxic cyanobacterium, was observed blooming during June-July (winter) 2002 in Shoalwater Bay, Queensland, Australia, an important feeding area for a large population of green turtles (Chelonia mydas). The bloom was mapped and extensive mats of L majuscula were observed overgrowing seagrass beds along at least 18 km of coast, and covering a surface area of more than I I km(2). Higher than average rainfall preceded the bloom and high water temperatures in the preceding summer may have contributed to the bloom. In bloom samples, lyngbyatoxin A (LA) was found to be present in low concentration (26 mu g kg(-1) (dry weight)), but debromoaplysiatoxin (DAT) was not detected. The diet of 46 green turtles was assessed during the bloom and L. majuscula was found in 51% of the samples, however, overall it contributed only 2% of the animals' diets. L. majuscula contribution to turtle diet was found to increase as the availability of the cyanobacterium increased. The bloom appeared to have no immediate impact on turtle body condition, however, the presence of a greater proportion of damaged seagrass leaves in diet in conjunction with decreases in plasma concentrations of sodium and glucose could suggest that the turtles may have been exposed to a Substandard diet as a result of the bloom. This is the first confirmed report of L. majuscula blooming in winter in Shoalwater Bay, Queensland, Australia and demonstrates that turtles consume the toxic cyanobacterium in the wild, and that they are potentially exposed to tumour promoting compounds produced by this organism. (c) 2005 Elsevier B.V. All rights reserved.

Sand and nest temperatures and an estimate of hatchling sex ratio from the Heron Island green turtle (Chelonia mydas) rookery, Southern Great Barrier Reef

Sand and nest temperatures were monitored during the 2002-2003 nesting season of the green turtle, Chelonia mydas, at Heron Island, Great Barrier Reef, Australia. Sand temperatures increased from similar to 24 degrees C early in the season to 27-29 degrees C in the middle, before decreasing again. Beach orientation affected sand temperature at nest depth throughout the season; the north facing beach remained 0.7 degrees C warmer than the east, which was 0.9 degrees C warmer than the south, but monitored nest temperatures were similar across all beaches. Sand temperature at 100 cm depth was cooler than at 40 cm early in the season, but this reversed at the end. Nest temperatures increased 2-4 degrees C above sand temperatures during the later half of incubation due to metabolic heating. Hatchling sex ratio inferred from nest temperature profiles indicated a strong female bias.

Interactions between behaviour and plasma steroids within the scramble mating system of the promiscuous green turtle, Chelonia mydas

We measured plasma androgen (combined testosterone and 5 alpha-dihydrotestosterone) (A) and corticosterone (B) in the promiscuous green turtle (Chelonia mydas) during courtship in the southern Great Barrier Reef. This study examined if reproductive behaviors and intermale aggression induced behavioral androgen and adrenocortical responses in reproductively active male and female green turtles. Associations between reproductive behavior and plasma steroids were investigated in green turtles across the population and within individuals. Levels across a range of both asocial and social behaviors were compared including (a) free swimming behavior; (b) initial courtship interactions; (c) mounted behavior (male and female turtles involved in copulatory activities); (d) intermale aggression (rival males that physically competed with another male turtle or mounted males recipient to these aggressive interactions); and (e) extensive courtship damage (male turtles that had accumulated excessive courtship damage from rival males). Behavioral androgen responses were detected in male turtles, in that plasma A was observed to increase with both attendant and mounted behavior. Male turtles who had been subjected to intermale aggression or who had accumulated severe courtship damage exhibited significantly lower plasma A than their respective controls. No pronounced adrenocortical response was observed after either intermale aggression or accumulation of extensive courtship damage. Female turtles exhibited a significant increase in plasma B during swimming versus mounted behavior, but no change in plasma A. We discuss our results in terms of how scramble polygamy might influence behavioral androgen interactions differently from more typical combative and territorial forms Of male polygamy. (C) 1999 Academic Press.

Los significados de la tortuga verde (chelonia mydas) en El Caribe costarricense

Introducción Este trabajo se enfoca en la identificación cualitativa de los significados culturales atribuidos a la tortuga verde (Chelonia mydas) en la historia del Caribe costarricense. Se distinguen, de maneras hipotéticas, tres etapas en la evolución cultural de esos significados: las tradiciones africanas ancestrales, la tradición jamaiquina y el sincretismo cultural de hoy. Se discute el alcance, el traslape y la oposición conflictiva entre los significados tradicionales y los modernos, y se señala algunas perspectivas sobre la dinámica del cambio cultiral el objetivo principal de la investigación exploratoria realizada es apoyar la enseñanza – aprendizaje de la dimensión humana de la conservación y el manejo de la vida silvestre en la maestría PRMVS-UNA, Estudiantes y profesor colaboraron en el diseño y ejecución del trabajo de campo

Detection of polymorphisms of the mtDNA control region of Caretta caretta (Testudines: Cheloniidae) by PCR-SSCP

Marine turtles are increasingly being threatened worldwide by anthropogenic activities. Better understanding of their life cycle, behavior and population structure is imperative for the design of adequate conservation strategies. The mtDNA control region is a fast-evolving matrilineal marker that has been employed in the study of marine turtle populations. We developed and tested a simple molecular tracing system for Caretta caretta mtDNA haplotypes by polymerase chain reaction-single strand conformation polymorphism (PCR-SSCP). Using this technique, we were able to distinguish the SSCP patterns of 18 individuals of the haplotypes CC-A4, CC-A24 and CCxLO, which are commonly found in turtles sampled on the Brazilian coast. When we analyzed 15 turtles with previously unknown sequences, we detected two other haplotypes, in addition to the other four. Based on DNA sequencing, they were identified as the CC-A17 and CC-A1 haplotypes. Further analyses were made with the sea turtles, Chelonia mydas (N = 8), Lepidochelys olivacea (N = 3) and Eretmochelys imbricata (N = 1), demonstrating that the PCR-SSCP technique is able to distinguish intra-and interspecific variation in the family Cheloniidae. We found that this technique can be useful for identifying sea turtle mtDNA haplotypes, reducing the need for sequencing.

Anthropogenic and Natural Organohalogen Compounds in Blubber of Dolphins and Dugongs (Dugong dugon) from Northeastern Australia

A range of organohalogen compounds (10 polychlorinated biphenyl [PCB] congeners, DDT and metabolites, chlordane-related compounds, the potential natural organochlorine compound Q1, toxaphene, hexachlorobenzene, hexachlorocyclohexanes, dieldrin, and several yet unidentified brominated compounds) were detected in the blubber of four bottlenose dolphins (Tursiops truncatus), one common dolphin (Delphinus delphis), and seven dugongs (Dugong dugon), as well as in adipose tissue of a green turtle (Chelonia mydas) and a python (Morelia spilota) from northeast Queensland (Australia). The green turtle and dugongs accumulated lower organohalogen levels than the dolphins. Lower levels in dugongs were expected because this species is exclusively herbivorous. Highest PCB and DDT levels recorded in dugongs were 209 and 173 mug/kg lipids, respectively. Levels of the nonanthropogenic heptachlorinated compound Q1 (highest level in dugongs was 160 mug/kg lipids) were estimated using the ECD response factor of trans-nonachlor. Highest organohalogen levels were found in blubber of dolphins for sumDDT (575-52,500 mug/kg) and PCBs (600-25,500 mug/kg lipids). Furthermore, Q1 was a major organohalogen detected in all samples analyzed, ranging from 450 -9,100 mug/kg lipids. The highest concentration of Q1 determined in this study represents the highest concentration reported to date in an environmental sample. Levels of chlordane-related compounds were also high (280-7,700 mug/kg, mainly derived from trans-nonachlor), but concentrations of hexachlorobenzene, hexachlorocyclohexanes, dieldrin, and toxaphene were relatively low and contributed little to the overall organohalogen contamination. Furthermore, a series of three major (BC-1, BC-2, and BC-3) and six minor (BC-4 through BC-9) unknown brominated compounds were observable by extracting m/z 79 and m/z 81 from the GC/ECNI-MS full scan run. Structural proposals were made for the two major recalcitrant compounds (referred to as BC-1 and BC-2). BC-2 appears to be a tetrabromo-methoxy-diphenylether (512 u) and BC-1 has 14 u (corresponding with an additional CH2 group) more relative to BC-1. In general the organohalogen pattern observed in blubber of dolphins was different compared to similar samples from other locations in the world, which is apparent from the fact that the four major abundant signals in the GC/ECD chromatogram. of D. delphis originated from the four unknown compounds Q1, BC-1, BC-2, and BC-3.

Modulation of the adrenocortical stress response in marine turtles (Cheloniidae): evidence for a hormonal tactic maximizing maternal reproductive investment

The relationships between reproductive condition, level of reproductive investment and adrenocortical modulation to capture stress in marine turtles form the basis of this study. When subjected to either capture or ecological stressors, nesting marine turtles have demonstrated adrenocortical responses that are both small in magnitude, and slow in responsiveness. These observations were further investigated to determine whether this minimal stress response was a physiological strategy to maximize reproductive investment in adult green Chelonia mydas and hawksbill Eretmochelys imbricata turtles. Female green and hawksbill turtles exhibited a decrease in adrenocortical responsiveness with progressive reproductive condition. Breeding turtles exhibited most suppression of their adrenocortical response to capture compared to both non-breeding and pre-breeding female counterparts. Nesting green turtles maintained a suppressed adrenocortical response to capture throughout the nesting season despite decreased reproductive investment. In contrast, male green and hawksbill turtles were less able to modulate their corticosterone (B) response to acute capture stress. During breeding, male turtles possessed significantly greater adrenocortical responses to capture than females. These results could indicate that the large reproductive investment necessary for female marine turtle reproduction might underlie the marked decrease in adrenocortical responsiveness. This hormonal mechanism could function as one strategy by which female marine turtles maximize their current reproductive event, even though under certain situations this mechanism could entail costs to female survival.

Nocturnal activity in the green sea turtle alters daily profiles of melatonin and corticosterone

In nature, green turtles (Chelonia mydas) can exhibit nocturnal activity in addition to their typically diurnal activity cycle. We examined whether nocturnal activity in captive and free-living green turtles altered daily plasma profiles of melatonin (MEL) and corticosterone (CORT). In captivity, diurnally active green turtles expressed distinct diel cycles in MEL and CORT; a nocturnal rise was observed in MEL and a diurnal rise was observed in CORT. However, when induced to perform both low- and high-intensity nocturnal activity, captive green turtles exhibited a significant decrease in MEL, compared to inactive controls. In contrast, plasma CORT increased significantly with nocturnal activity, and further, the relative increase in CORT was correlated with the intensity of the nocturnal behavior. In free-living green turtles that performed nocturnal activity including: nesting, mate searching, and feeding/swimming behaviors, plasma profiles in MEL and CORT exhibited relatively little, or no, daily fluctuation. Our findings demonstrate that nocturnal activity in green turtles is often associated with MEL and CORT profiles that resemble those measured during the day. We speculate that these conspicuous changes in MEL and CORT during nocturnal activity could either support or promote behaviors that enable acquisition of transient resources important to the survival and reproductive success of green turtles. (C) 2002 Elsevier Science (USA).

Interactions among endocrinology, seasonal reproductive cycles and the nesting biology of the female green sea turtle

We collected data on plasma levels of testosterone+5a-dihydrotestosterone (T+DHT) and corticosterone (CORT) from adult female green sea turtles (Chelonia mydas) from southern Queensland during distinct stages of their reproductive cycle. Those females capable of breeding in a given year had elevated plasma steroid levels (T+DHT 0.91 +/- 0.08; CORT 1.05 +/- 0.29 ng/ml), associated with follicular development, until courtship began in October. At the beginning of the nesting season in November plasma levels of 2 CORT were related to when the female first nested (r(2) = 0.06; F = 10.45; P = 0.01). However, they were not correlated with the number of clutches a female laid in that season (F = 3.65; P = 0.08). We repeatedly sampled 23 turtles over the nesting season and profiled changes in steroids immediately following oviposition of each clutch. Levels of T+DHT (range 0.41-0.58 ng/ml) and CORT (range 2.13-2.81 ng/ml) were similar through the early stages of the nesting season and inter-nesting period, and declined to near basal levels (T+DHT 0.37 +/- 0.03 and CORT 1.85 +/- ng/ml) following the last clutch for the season. Steroid hormone levels were also low (T+DHT 0.38 +/- 0.16; CORT 0.46 +/- 0.21 ng/ml) in four independent post-breeding (atretic) females; samples for these females were taken at a time when body condition was presumably at the lowest for the season. Subtle changes in the nesting environment, such as variation in nesting habitat or the time of night that nesting occurred, were associated with a small and slow CORT increase. We suggest CORT is increased in nesting females to assist in lipid transfer to prepare the ovarian follicles and/or the reproductive organs for ovulation.

Plastic ingestion by sea turtles in Paraíba State, Northeast Brazil

ABSTRACT Currently, plastics are recognized as a major pollutant of the marine environment, representing a serious threat to ocean wildlife. Here, we examined the occurrence and effects of plastic ingestion by sea turtles found stranded along the coast of Paraíba State, Brazil from August 2009 to July 2010. Ninety-eight digestive tracts were examined, with plastic found in 20 (20.4%). Sixty five percent (n = 13) of turtles with plastic in the digestive tract were green turtles (Chelonia mydas), 25% (n = 5) were hawksbills (Eretmochelys imbricata), and 10% (n = 2) were olive ridley (Lepidochelys olivacea). More plastic was found in the intestine (85%) than in other parts of the gastrointestinal tract. We observed complete blockage of the gastrointestinal tract due to the presence of plastic in 13 of the 20 turtles that had ingested plastic. No correlation was found between the curved carapace length (CCL) and the number or mass of the plastic ingested items. Significant differences were found between the intake of hard and soft plastic and the ingestion of white/transparent and colored plastic, with soft and white/transparent plastics being more commonly ingested. This study reveals the serious problem of plastic pollution to sea turtles at the area.

Seasonality and Temperature:Turtles in Hot Water?

Variation in temperature affects the biology of sea turtles at a range of scales. To elucidate the drivers of seasonality of nesting and duration of season, databases across four species of sea turtles (Caretta caretta n=37, Chelonia mydas n=64, Dermochelys coriacea n=44 and Eretmochelys imbricata n=36) at a global scale were created. By using remotely sensed sea surface temperature data, thermal profiles across the nesting season were generated. Duration of nesting season was correlated with latitude in all species but was more tightly coupled with temperature; seasons were significantly longer with increased mean SST. In general, nesting seasonality occurred at warmest time of the year. SST for the month before, month after and the month of peak nesting significantly affected the month of peak nesting.

RAPPORT NATIONAL SUR L'ETAT DE LA BIODIVERSITE

Informations de base sur la République du Cap Vert L'archipel du Cap Vert est constitué par dix îles et huit îlots situés à environ 500 km de la côte occidentale africaine. Sa superficie est de 4033 km2. Les îles sont d'origine volcanique et sont implantées sur la zone sud-ouest de la plate-forme sénégalaise sur la croûte océanique d'âge comprise entre 140 et 120 millions d'années. Le relief est très accidenté dans les îles les plus jeunes (Fogo, Santiago, Santo Antão et S. Nicolau), mais relativement plat dans les îles plus anciennes (Maio, Boavista e Sal). Les sols sont peu évolués, avec des horizons pédologiques peu différenciés. Par sa situation géographique, dans une zone d'aridité météorologique, le climat du Cap Vert est sahélien du type tropical sec, soumis aux vents alizés du nordest, avec des températures modérées (environ 24ºC) et une faible amplitude thermique dû à l'environnement atlantique. Les précipitations sont généralement faibles sur l'ensemble du pays, ne dépassant pas les 300 mm de moyenne annuelle pour les 65% du territoire situé à moins de 400 m d'altitude. Les zones sous l'influence des alizés étant encore plus sèches (150 mm de moyenne annuelle). Sur les versants situés à plus de 500 m d'altitude faisant face aux alizés, on peut atteindre ou dépasser les 700 mm. Les pluies sont irrégulières et généralement mal distribuées dans le temps et dans l'espace. Le peuplement et son influence sur la biodiversité Après leur colonisation par les humains au cours du XVème siècle, les îles du Cap Vert ont été soumises à une forte exploitation des ressources biologiques. Des facteurs anthropiques avec conséquences directe et indirecte sur la végétation, tels que l'agriculture pluviale, dans la plupart des cas pratiquée sur les fortes pentes des versants, l'utilisation du bois de feu, le surpâturage et l'introduction des espèces exotiques ont contribué à la dégradation graduelle de la végétation et des habitats de l'archipel. Le rôle de ces facteurs a été encore accentué par l'action passif des facteurs intrinsèques tels que l'insularité et la fraction importante du territoire occupée par des zones arides et semi-arides. La végétation des zones arides et semi-arides qui occupent, au Cap Vert, plus de 70% du sol arable du territoire, a un faible pouvoir de régénération. Sa flore insulaire est sensible par le fait d'avoir évolué en l'absence de prédateurs et d'être issues de petites populations avec une diversité génétique limitée et par une aire de dissémination très limitée. La diversité des espèces Il existe au Cap Vert, 110 espèces de bryophytes dont 15 sont endémiques. Du total, 36% sont extinctes ou menacées. Parmi les endémiques 40% sont menacées. Les espèces d’angiospermes sont en nombre de 240 dont 45 sont endémiques. A noter que 27% du total sont extinctes ou menacées. Parmi les endémiques, 54% sont en danger de disparition. La biodiversité animale cours des risques majeures de survie. Des 37 espèces de gastéropodes existantes, 15 sont endémiques dont 67% sont menacées. Les arachnides sont au nombre de 111 dont 46 sont endémiques. Parmi les endémiques, 78% sont menacées. Il existe 470 espèces d'insectes (coléoptères) dont 155 sont endémiques. 84% des taxa endémiques sont menacées. On suppose que du total des 470 espèces, 64% sont disparues ou en danger. L'état actuel de la faune et de la flore a été donné par la Première Liste Rouge du Cap Vert, publiée en 1996 et qui indique un certain nombre de statistiques effrayantes : sont menacées plus de 26% des angiospermes, plus de 40% des bryophytes, plus de 65% des ptéridophytes et plus de 29% des lichens ; plus de 47% des oiseaux, 25% des reptiles terrestres, 64% des coléoptères, plus de 57% des arachnides, plus de 59% des mollusques terrestres. L'archipel du Cap Vert est situé dans la zone tropicale où, selon Nunan (1992), si on exclue les espèces migratoires on peu compter environ 273 espèces de poissons, dont 70% sont endémiques. La liste des espèces de poissons des îles du Cap Vert est assez diversifiée et compte environ une centaine d'espèces appartenant à différentes familles. En matière de diversité biologique marine l'exploitation des ressources dans la ZEE (Zone Economique Exclusive) sont encore loin d'atteindre le potentiel estimé. Néanmoins, il existe quelques espèces qui sont en danger, notamment les tortues et les langoustes. Dans les eaux capverdiennes il existe 5 espèces de tortues : Dermocelys coriacea, Chelonia mydas, Eretmochelys imbricata, Caretta caretta et Lepidochelys olivacea. Les tortues sont d'une façon générale soumises à une exploitation irrationnelle depuis des décades. La viande et les oeufs, surtout de la tortue mâle sont très appréciés. La carapace est utilisée dans la bijouterie (boucles, bagues, colliers, etc.). Parmi les quatre familles de langoustes connues, l'archipel du Cap Vert recèle deux : la Palinuridae (langouste rose, verte et marron) et la Scyllaride (langouste de pierre). A signaler également une espèce endémique, le Palinuris charlestoni. Toutes les espèces existantes au Cap Vert sont exploitées, souvent à la limite de la durabilité. La République du Cap Vert et la Convention sur la Biodiversité Le Cap Vert a signé la Convention sur la biodiversité en juin 1992 et l'a ratifié en mars 1995. Pour remplir les obligations découlant de l'adoption de la Convention, le pays a complété sa Stratégie Nationale et Plan d'Action sur la Biodiversité en février 1999. Une institution responsable pour la mise en oeuvre de la politique nationale en matière de l'environnement a été créée, le Secrétariat Exécutif pour l'Environnement (SEPA). Le Plan d'Action National a identifié 21 objectifs divisés en huit groupes thèmatiques et contient des activités jusqu'à l'an 2010. Parallèlement à ces actions, la Loi de Base pour l'Environnement, le Code de l'Environnement, le Code de l'Eau et le Code Forestier ont été adoptés. Ce nouveau Code Forestier a été élaboré afin d'actualiser les normes pour une gestion durable des ressources et le transfert des compétences aux régions et communautés. Au niveau stratégique le Cap Vert a élaboré son Programme d'Action National pour l'Environnement (PANA) et a développé le Programme d'Action National de Lutte Contre la Désertification (PAN-LCD) en utilisant l'approche participative faisant appel à tous les acteurs de la société civile y inclus les associations et ONG. Au niveau international le Cap Vert a adhéré aux conventions telles que la biodiversité, les changements climatiques et le contrôle de la désertification. Le pays a également signé les conventions suivantes : Convention des Nations Unies sur le Droit de la Mer, Convention relative à la Protection du Patrimoine Mondial Culturel et Naturel, Convention de Bâle sur les mouvements trans-frontaliers, Convention internationale pour la Prévention de la pollution par des bateaux, Convention de Vienne sur la protection de la couche de l'ozone, Protocole de Montréal sur les substances qui appauvrissent la couche de l'ozone. La mise en oeuvre de la stratégie nationale sur la Diversité Biologique permettra une meilleure gestion de l'eau, des ressources naturelles et des espaces, l'introduction de nouvelles espèces et de nouvelles technologies alternatives pour l'agriculture et l'élevage ainsi que la création de nouveaux emplois alternatifs, à partir des activités génératrices de revenus, et de diminuer ainsi, la pression sur les ressources naturelles.