ABSTRACT
Some species of fish have been used as bioindicators of aquatic environmental pollution all over the world. Pejerrey (Odontesthes bonariensis) was selected for the current study due to its sensitivity to pollutants and because is one of the emblematic fish species that inhabits shallow lakes of the Pampa region (Argentina). Recently, in Chascomús lake were recorded concentrations of Cd, Cr, Cu and Zn with values above the Argentine National Guidelines for the Protection of the Aquatic life. Regarding this, the aim of the present study was to investigate the effects of environmental concentrations of these metals on the sperm quality, fertilization and hatching rates, and embryo and larval survival of pejerrey. Also, the same endpoints were analyzed with concentrations ten times higher to simulate a polluted worst-case scenario. The results showed that the presence of some metals in aquatic environments reduced pejerrey sperm motility (in ~50%) and velocity (in ~30%). These results were obtained using a computer assisted sperm analyzer enforcing the application of this analysis as a tool or bioindicator of aquatic pollution. In addition, fertilization rate was diminished (in ~40%) for all treatments. Besides, the hatching rate, and embryo and larval survival were drastically affected being zero for the highest metal concentrations assessed. All together these results, showed that even lower metal concentrations can negatively affect different reproductive parameters of one of the most emblematic fish species of the Argentinean water bodies.
Subject(s)
Embryo, Nonmammalian/drug effects , Fertilization/drug effects , Metals, Heavy/adverse effects , Smegmamorpha/physiology , Spermatozoa/drug effects , Water Pollutants, Chemical/adverse effects , Animals , Embryonic Development/drug effects , Longevity/drug effects , Male , Semen Analysis/veterinaryABSTRACT
Some heavy metals related to human activities were measured in the water of Chascomús lake. The maximum concentrations were: 0.23⯵g/L for Cd, 4.28⯵g/L for Cr, 22.09⯵g/L for Cu, 2.49⯵g/L for Ni, 3.24⯵g/L for Pb and 210.76⯵g/L for Zn. The values of Cd, Cr, Cr, Pb and Zn were above the Argentine National Guidelines for the Protection of the Aquatic life. The analysis of gonadal condition of pejerrey fish (Odontesthes bonariensis) from this lake did not revealed any reproductive damages. However, exposures with environmental concentrations of Cd, Cr, Cu and Zn under laboratory conditions of pejerrey males (14â¯days), caused a significant increase of the expression of the three variants of gnrh in the brain (within Cd exposure) and a decrease in cyp19a1b mRNA (within Cu exposure). Furthermore, at pituitary level, a decrease in fshb transcript levels was observed in the fish exposed to Cd and Cr and a decrease in the expression of both gonadotropin receptors at gonadal level in Zn exposure. Moreover, the gonads of the fish exposed to all the tested metals suffered structural damages showing shortness of the spermatic lobules, fibrosis, testis ova and the presence of piknotic cells. All these findings alert that heavy metals pollution affects the expression of key reproductive genes and gonadal structure of fish species that represent the predominant group of organisms and are considered sentinel species in the aquatic ecosystems.
Subject(s)
Endocrine System/metabolism , Environmental Monitoring , Fishes/metabolism , Lakes/chemistry , Metals, Heavy/toxicity , Reproduction , Water Pollutants, Chemical/toxicity , Animals , Apoptosis/drug effects , Endocrine System/drug effects , Fish Proteins/genetics , Fish Proteins/metabolism , Fishes/blood , Male , Metals, Heavy/analysis , Proliferating Cell Nuclear Antigen/metabolism , RNA, Messenger/genetics , RNA, Messenger/metabolism , Testis/drug effects , Testis/metabolism , Testis/pathology , Testosterone/blood , Water Pollutants, Chemical/analysisABSTRACT
The present study focuses on the effects of E2 and EE2 environmental concentrations on different components of the reproductive axis of pejerrey (Odontesthes bonariensis), a native fish species from Pampas lakes of Argentina. The results obtained demonstrated that E2 and EE2 separate or mixed, could disrupt key pathways of the pejerrey Brain-Pituitary-Gonadal axis. First, it was observed that at the brain level, gnrh-III and cyp19a1b mRNA expression increased significantly in the exposed fish. Secondly, in the pituitary fshb and lhb mRNA expression levels, the study did not show any differences between treated and control groups. Thirdly, fshr and lhcgr transcript levels showed a significant decrease at testicular level. Nevertheless, testosterone plasmatic levels remained unchanged in exposed fish. In addition, in a histological analysis, it was possible to find pyknotic nuclei in estrogen only on treated fish testis linked to a reduction in the GSI index and a decrease in the length of spermatogenic lobules. All these findings highlighted the fact that environmental concentrations of E2, EE2 and their mixture disrupted the endocrine-reproductive axis of pejerrey, being the testis the main direct target.
Subject(s)
Endocrine Disruptors/toxicity , Estradiol/toxicity , Ethinyl Estradiol/toxicity , Pituitary Gland/drug effects , Smegmamorpha/metabolism , Testis/drug effects , Animals , Argentina , Brain/drug effects , Brain/metabolism , Gene Expression/drug effects , Gonadal Steroid Hormones/genetics , Male , Pituitary Gland/metabolism , Smegmamorpha/genetics , Spermatogenesis/drug effects , Testis/metabolismABSTRACT
17ß-Estradiol (E2) and synthetic 17α-Ethinylestradiol (EE2) are estrogenic compounds present in surface waters as a consequence of municipal sewage discharges. The aim of this study was to evaluate the effects of E2, EE2 and its mixtures on different reproductive parameters and embryo-larval survival in pejerrey fish (Odontesthes bonariensis). In order to analyze the effect of these compounds on sperm quality, fertilization%, embryo-larval survival (%), and the point of no return (PNR), different assays were performed using concentrations 175, 350, 700 and 1400 ng/L of E2; 22.5, 45, 90 and 180 ng/L of EE2 and mixtures M1 (175 E2+22.5 EE2, ng/L), M2 (350 E2+45 EE2, ng/L), M3 (700 E2+90 EE2, ng/L) and M4 (1400 E2+180 EE2 ng/L). No significant differences in motility parameters were observed between E2 and EE2 treatments and the control group. However, a significant decrease in motility% was recorded for all mixtures tested compared with the control samples. For fertilization%, only sperm activated with M4 showed a significant decrease compared with the control group. In the case of embryo survival, there was only a significant decrease in the highest concentration of EE2 compared with the control group. For the mixtures, M3 is the one that had the most adverse effect on embryo survival. In larval survival, there was a significant decrease in concentration 175 and 700 ng/L of E2 compared with the control group. In EE2 treatments, the ones with a significant reduction in larval survival were concentration 45 and 90 ng/L. And for the mixture treatments, M1, M3 and M4 had a significantly lower larval survival than the control group. In comparison to other treatments, M1 demonstrated a significant difference in PNR when compared with the control group. The results obtained demonstrated that the exposure to mixtures of E2 and EE2 affected fish sperm motility, fertilization% and, embryo and larval survival even at relevant environmental concentrations highlighting the necessity of considering the effects of pollutants mixtures in ecotoxicological studies.
Subject(s)
Embryo, Nonmammalian/drug effects , Estradiol/toxicity , Ethinyl Estradiol/toxicity , Fertilization/drug effects , Smegmamorpha/physiology , Spermatozoa/drug effects , Water Pollutants, Chemical/toxicity , Animals , Male , Reproduction/drug effects , Sewage/chemistry , Sperm Motility/drug effectsABSTRACT
Juveniles of pejerrey, Odontesthes bonariensis, were exposed to 0.1% Alizarin Red S (ARS) alone or with a previous immersion in 2.2% saline solution (Osmotic Induction, OI) to enhance the ARS marking method. Fish were marked in the field and immediately released in 1 m3 cages in "La Salada de Monasterio" lagoon, Chascomús, Buenos Aires , Argentina. After 73 days, clear marks were observed in the otoliths, caudal fin rays and scales with both treatments, being the intensity of the signal in the scales of OI+ARS treated fish higher. On the other hand, no marks were observed in the control group on the same structures. Approximately one year post-treatment (385 days), only marks in caudal fin rays were found clearly in OI+ARS treated fish. After this period, no significant differences in total length or weight between marked or control fish were observed and the mortality ranged between 30-40 % in all cages. These results provide strong evidence for the potential applicability of this cost-effective marking technique in differentiation of wild and hatchery-produced pejerrey. The success in the caudal fin rays marking is also important because it is easy to do and does not require the sacrifice of fish.(AU)
Juvenis de pejerrey, Odontesthes bonariensis, foram expostos a Vermelho de Alizarina S (ARS) 0,1% de duas formas, sozinho ou com uma imersão anterior em 2,2% de solução salina (Indução osmótica, IO) para melhorar o método de marcação ARS. Os procedimentos foram realizados no campo e os peixes foram liberados em gaiolas (tanques-rede) de 1 m3 na lagoa "La Salada de Monasterio", Chascomús, Buenos Aires, Argentina. Após 73 dias, marcas claras foram observadas nos otólitos, raios da nadadeira caudal e escamas em ambos os tratamentos, sendo que a intensidade do sinal nas escalas de IO + ARS de peixe tratado foi superior. Por outro lado, não foram observados marcas no grupo controle sobre as mesmas estruturas. Aproximadamente um ano pós-tratamento (385 dias), apenas marcas nos raios da nadadeira caudal foram encontrados claramente nos peixes tratados com IO+ARS. Entre os peixes observados, após este período, não houve diferenças significativas no comprimento total ou peso entre o grupo controle e marcados, ademais, a mortalidade variou entre 30-40% em todas as gaiolas. Estes resultados fornecem fortes evidências e um grande potencial para aplicação desta técnica rentável de marcação que diferencia o pejerrey selvagem e o produzido em cativeiro. O sucesso na marcação dos raios da nadadeira caudal também é de grande importância, pois sua verificação é fácil e não requer o sacrifício de peixes.(AU)
Subject(s)
Animals , Fishes/growth & development , Coloring Agents/administration & dosage , Animal Identification Systems , Animal Fins , FisheriesABSTRACT
Juveniles of pejerrey, Odontesthes bonariensis, were exposed to 0.1% Alizarin Red S (ARS) alone or with a previous immersion in 2.2% saline solution (Osmotic Induction, OI) to enhance the ARS marking method. Fish were marked in the field and immediately released in 1 m3 cages in "La Salada de Monasterio" lagoon, Chascomús, Buenos Aires , Argentina. After 73 days, clear marks were observed in the otoliths, caudal fin rays and scales with both treatments, being the intensity of the signal in the scales of OI+ARS treated fish higher. On the other hand, no marks were observed in the control group on the same structures. Approximately one year post-treatment (385 days), only marks in caudal fin rays were found clearly in OI+ARS treated fish. After this period, no significant differences in total length or weight between marked or control fish were observed and the mortality ranged between 30-40 % in all cages. These results provide strong evidence for the potential applicability of this cost-effective marking technique in differentiation of wild and hatchery-produced pejerrey. The success in the caudal fin rays marking is also important because it is easy to do and does not require the sacrifice of fish.
Juvenis de pejerrey, Odontesthes bonariensis, foram expostos a Vermelho de Alizarina S (ARS) 0,1% de duas formas, sozinho ou com uma imersão anterior em 2,2% de solução salina (Indução osmótica, IO) para melhorar o método de marcação ARS. Os procedimentos foram realizados no campo e os peixes foram liberados em gaiolas (tanques-rede) de 1 m3 na lagoa "La Salada de Monasterio", Chascomús, Buenos Aires, Argentina. Após 73 dias, marcas claras foram observadas nos otólitos, raios da nadadeira caudal e escamas em ambos os tratamentos, sendo que a intensidade do sinal nas escalas de IO + ARS de peixe tratado foi superior. Por outro lado, não foram observados marcas no grupo controle sobre as mesmas estruturas. Aproximadamente um ano pós-tratamento (385 dias), apenas marcas nos raios da nadadeira caudal foram encontrados claramente nos peixes tratados com IO+ARS. Entre os peixes observados, após este período, não houve diferenças significativas no comprimento total ou peso entre o grupo controle e marcados, ademais, a mortalidade variou entre 30-40% em todas as gaiolas. Estes resultados fornecem fortes evidências e um grande potencial para aplicação desta técnica rentável de marcação que diferencia o pejerrey selvagem e o produzido em cativeiro. O sucesso na marcação dos raios da nadadeira caudal também é de grande importância, pois sua verificação é fácil e não requer o sacrifício de peixes.
Subject(s)
Animals , Coloring Agents/administration & dosage , Fishes/growth & development , Animal Identification Systems , Animal Fins , FisheriesABSTRACT
In the present study it was showed for the first time the ultrastructural morphology of O. bonariensis sperm using electron microscopy techniques. Different kinds of abnormalities were described in fresh and post thawed sperm caused by crogenic protocols. Pejerrey spermatozoon is uniflagellated and is differentiated into three parts: a small roundish head (~1.80µm in length and 1.67µm in width), a midpiece or transitional region (~1.11µm in length and 1.56µm in width), and a long tail or flagellum (~29.08µm). Samples of fresh and post thawed sperm showed evidence of morphological anomalies affecting various intracellular compartments. Spermatozoa with swollen, ruptured, or absent membranes in the head showing excess of cytoplasm, and with alteration of the spatial orientation of the mitochondria were observed. A swollen flagellum was observed containing cytoplasmic vesicles, distributed along the whole length or concentrated in a restricted part of the tail. It was also found a high level of abnormalities (60%) in frozen sperm when compared with normal sperm (18%) reflecting the damage provoked by cryopreservation procedures.(AU)
No presente estudo mostrou-se pela primeira vez a morfologia estrutural dos espermatozoides de O. bonariensis utilizando técnicas de microscopia eletrônica. Diferentes tipos de anormalidades foram descritas para sêmen fresco e descongelado. O espermatozoide de Pejerrey é uniflagelado e dividido em três partes: uma cabeça pequena e arredondada (~1.80µm de comprimento e 1.67µm de largura), uma parte intermediária ou região de transição (~1.11µm de comprimento e 1.56µm de largura) e uma cauda longa ou flagelo (~29.08µm). Amostras de sêmen fresco e descongelado mostraram evidências de anormalidades morfológicas afetando vários compartimentos intracelulares. Na cabeça haviam espermatozoides com membranas dilatadas, rompidas ou ausentes, mostrando excesso de citoplasma e alteração na orientação espacial das mitocôndrias. Um flagelo dilatado foi observado contendo vesículas citoplasmáticas, as quais estavam distribuídas ao longo de todo o seu comprimento ou concentradas em uma parte restrita da cauda. Também foi encontrado um alto nível de anormalidades (60%) em sêmen congelado em comparação com o sêmen normal (18%), refletindo os danos provocados pelos procedimentos de criopreservação.(AU)
Subject(s)
Animals , Cryopreservation , Spermatozoa , Congenital Abnormalities , Fishes/classificationABSTRACT
In the present study it was showed for the first time the ultrastructural morphology of O. bonariensis sperm using electron microscopy techniques. Different kinds of abnormalities were described in fresh and post thawed sperm caused by crogenic protocols. Pejerrey spermatozoon is uniflagellated and is differentiated into three parts: a small roundish head (~1.80µm in length and 1.67µm in width), a midpiece or transitional region (~1.11µm in length and 1.56µm in width), and a long tail or flagellum (~29.08µm). Samples of fresh and post thawed sperm showed evidence of morphological anomalies affecting various intracellular compartments. Spermatozoa with swollen, ruptured, or absent membranes in the head showing excess of cytoplasm, and with alteration of the spatial orientation of the mitochondria were observed. A swollen flagellum was observed containing cytoplasmic vesicles, distributed along the whole length or concentrated in a restricted part of the tail. It was also found a high level of abnormalities (60%) in frozen sperm when compared with normal sperm (18%) reflecting the damage provoked by cryopreservation procedures.
No presente estudo mostrou-se pela primeira vez a morfologia estrutural dos espermatozoides de O. bonariensis utilizando técnicas de microscopia eletrônica. Diferentes tipos de anormalidades foram descritas para sêmen fresco e descongelado. O espermatozoide de Pejerrey é uniflagelado e dividido em três partes: uma cabeça pequena e arredondada (~1.80µm de comprimento e 1.67µm de largura), uma parte intermediária ou região de transição (~1.11µm de comprimento e 1.56µm de largura) e uma cauda longa ou flagelo (~29.08µm). Amostras de sêmen fresco e descongelado mostraram evidências de anormalidades morfológicas afetando vários compartimentos intracelulares. Na cabeça haviam espermatozoides com membranas dilatadas, rompidas ou ausentes, mostrando excesso de citoplasma e alteração na orientação espacial das mitocôndrias. Um flagelo dilatado foi observado contendo vesículas citoplasmáticas, as quais estavam distribuídas ao longo de todo o seu comprimento ou concentradas em uma parte restrita da cauda. Também foi encontrado um alto nível de anormalidades (60%) em sêmen congelado em comparação com o sêmen normal (18%), refletindo os danos provocados pelos procedimentos de criopreservação.