RESUMO

Floating natives (Eichhornia crassipes and Pistia stratiotes) and emergent exotic invasives (Hedychium coronarium and Urochloa arrecta) macrophytes grow as aquatic weeds in both natural and artificial floodplain areas in Brazil, where the chemical control should be researched. The herbicides glyphosate and saflufenacil, alone or mixed, were tested for weed control under simulated floodplain condition in mesocosms. Glyphosate (1,440 g ha-1), saflufenacil (120 g ha-1), or glyphosate (1,440 g ha-1) + saflufenacil (42, 84, and 168 g ha-1) were applied firstly; and 75 days after treatment (DAT), glyphosate (1,680 g ha-1) was applied as a follow-up treatment to control plant regrowth. An herbicide-free check was also used. Echhinornia crassipes was the species most susceptible to the different herbicides. Saflufenacil alone presented the lowest control on the macrophytes (≤45%) from 7 to 75 DAT, and in most cases they presented high regrowth rates, i.e., this herbicide was the least effective treatment in reducing the dry mass production of the macrophyte community. Glyphosate alone presented low efficacy to control H. coronarium (30-65%), but for the other macrophytes, it presented control peaks ≥90%, maintaining control levels ≥50% until 75 DAT. Glyphosate + saflufenacil, regardless rate of saflufenacil, caused similar damage to glyphosate in E. crassipes and P. stratiotes; however, in U. arrecta it caused 20-30% less injury. In contrast, these treatments provided the best control of H. coronarium. The complementary application of glyphosate was essential to improve the level of control of the first application, after plant regrowth.

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RESUMO

The aim of this study was to assess the efficacy of imazamox for control of S. molesta and to assess the effects of plant decomposition on environmental indicators after application of this herbicide in microcosm conditions. The following rates were used: 600, 700, 800 and 900 g ai ha-1 and spray volume 50 L ha-1. Control efficacy was determined as the percentage (from 0 to 100%) of visible injury symptoms in the plants, biochemical and chemical oxygen demand (BOD5 and COD), water quality variables, chlorophyll a and pheophytin a at 0, 7, 15, 30, 45 and 60 days after application (DAA) and fresh and dry biomass at 60 DAA. Imazamox was effective in controlling 94% of S. molesta with 900 g ai ha-1; it reduced 95% of fresh weight and 92% of dry weight of plant at 60 DAA, and reduced chlorophyll a of the plants for all rates. For BOD5, there was an increase for all rates at 15, 30 and 45 DAA with restoration of the parameters at 60 DAA, and for COD, there was an increase at 60 DAA with 700 and 900 g ai ha-1. For temperature, pH, dissolved oxygen and electrical conductivity, there was no significant effect after spraying. Imazamox was effective in controlling S. molesta with 900 g ai ha-1 without causing significant effects on the physical-chemical parameters of water quality.

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RESUMO

The use of chemotherapy agents has been growing worldwide, due to the increase number of cancer cases. In several countries, mainly in Europe countries, these drugs have been detected in hospitals and municipal wastewaters. In Brazil this issue is poorly explored. The main goal of this study was to assess the presence of three anti-cancer drugs, 5-fluorouracil (5-FU), gemcitabine (GEM) and cyclophosphamide (CP), and two metabolites, alpha-fluoro-beta-alanine (3-NH2-F) and 2'-deoxy-2',2'-difluorouridine (2-DOH-DiF), in effluents from a large cancer hospital, in the municipal wastewater treatment plant (WWTP) influent and effluent, and also to evaluate toxicity of the mixtures of these compounds by ecotoxicological testing in zebrafish. The sample collections were performed in Barretos Cancer Hospital of the large cancer center in Brazil. After each collection, the samples were filtered for subsequent Liquid Chromatography Mass Spectrometry analysis. The presence of CP, GEM, and both metabolites (3-NH2-F and 2-DOH-DiF) were detected in the hospital wastewater and the WWTP influent. Three drugs, GEM, 2-DOH-DiF and CP, were detected in the WWTP effluent. Two drugs were detected below the limit of quantification, 2-DOH-DiF:

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RESUMO

This study aimed to assess, in a microcosm condition, the efficacy of electrostatic spraying of herbicide imazamox in the control of Salvinia molesta and the effects of decomposition of plant material on water quality. The herbicide rates used were 600, 700, 800, and 900 g ai ha-1 and spray volume of 50 L ha-1 in electrostatic application. Control effectiveness was assessed at 7, 15, 30, 45, and 60 days after application (DAA), expressed in percentage (0-100%) of visible injury symptoms in the plants, biochemical oxygen demand (BOD5), chemical oxygen demand (COD), chlorophyll a and pheophytin a contents at 0, 7, 15, 30, 45, and 60 DAA, and fresh and dry biomass at 60 DAA. Imazamox was effective in controlling 63% of S. molesta with 900 g ai ha-1 in 45 DAA and 30% with 800 g ai ha-1 in 30 DAA, and reduced 82.3% and 17.5% of fresh weight and 62.6% and 9.3% of dry weight of plant at 60 DAA, respectively. The imazamox spray reduced chlorophyll a with all doses applied and increased BOD5 in 45 DAA with 900 g ai ha-1 and COD in all assessment periods, but for temperature, dissolved oxygen, electrical conductivity, and pH, there was no significant effect after spraying. The herbicide imazamox reduced S. molesta plants with 900 g ai ha-1, without causing significant effects on environmental indicators of water quality. Electrostatic spraying of herbicide can be used in management strategies of aquatic plants to reduce plant density in water bodies and maintain the colonization of plants at a level not harmful to the aquatic biota.

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RESUMO

Successful disease treatment depends on molecular studies under indoor conditions with experimental infection protocols that facilitate understanding the disease and the drug`s efficacy. The internal transcribed spacer (ITS) region was sequenced from three isolates, which were identified as Saprolegnia aenigmatica. Subsequently, healthy fish were immunosuppressed with dexamethasone (1.2 mg kg-1) and descaled to the skin using a sharp scalpel. These individuals were isolated in individual aquariums maintained at 22°C. Individuals in one group were subcutaneously inoculated with 9,000 zoospores (DDZ treatment), a second group was exposed to oomycetes in water with three colonized baits (DDB), a third group was maintained in water without zoospores (DD), and a control group (C) consisted of healthy animals. After 48 and 96 hours, two animals from each group were euthanized for fungal reisolation. The fish from groups DD and C did not show clinical signs, and no oomycetes were isolated. The animals from the DDZ and DDB groups showed cotton-wool-like masses on the skin, and S. aenigmatica was re-isolated. Thus, for infection using zoospores or baits parasitized by S. aenigmatica, an immunosuppressor (dexamethasone) and a sharp scalpel can be used effectively to establish an experimental infection in P. mesopotamicus.

O sucesso do tratamento de uma enfermidade depende do estudo de moléculas em condições de laboratório por meio de protocolos de infecção experimental que viabilizam a compreensão da doença e da eficácia dos fármacos. Pela sequência ITS foram identificadas três cepas de Saprolegnia aenigmatica. Dessa forma, pacus sadios foram submetidos à imunossupressão com dexametasona (1,2 mg kg-1), esfoliados com auxílio de bisturi e distribuídos em aquários a 22ºC. Após este procedimento, um grupo de animais foi inoculado com 9.000 zoósporos/peixe subcutâneo (DEZ), a outro foram adicionadas três iscas colonizadas com o oomiceto na água (DEI), um terceiro grupo foi mantido sem contato com o oomiceto (DE) e um quarto grupo, de animais sadios, representaram o controle (C). Após 48 e 96h deste procedimento, foram eutanaziados animais de cada grupo para reisolamento. Os animais do grupo DE e C não apresentaram sinais clínicos e não foi reisolado o oomiceto. Porém, tanto os animais do grupo DEZ quanto como os animais do grupo DEI apresentaram micélio branco na pele e foi reisolado Saprolegnia aenigmatica. Assim, a infecção com zoósporos ou com iscas colonizadas por S. aenigmatica, com o uso de dexametasona e abrasivo epitelial são formas eficazes de infecção experimental em P. mesopotamicus.

Assuntos

RESUMO

Successful disease treatment depends on molecular studies under indoor conditions with experimental infection protocols that facilitate understanding the disease and the drug`s efficacy. The internal transcribed spacer (ITS) region was sequenced from three isolates, which were identified as Saprolegnia aenigmatica. Subsequently, healthy fish were immunosuppressed with dexamethasone (1.2 mg kg-1) and descaled to the skin using a sharp scalpel. These individuals were isolated in individual aquariums maintained at 22°C. Individuals in one group were subcutaneously inoculated with 9,000 zoospores (DDZ treatment), a second group was exposed to oomycetes in water with three colonized baits (DDB), a third group was maintained in water without zoospores (DD), and a control group (C) consisted of healthy animals. After 48 and 96 hours, two animals from each group were euthanized for fungal reisolation. The fish from groups DD and C did not show clinical signs, and no oomycetes were isolated. The animals from the DDZ and DDB groups showed cotton-wool-like masses on the skin, and S. aenigmatica was re-isolated. Thus, for infection using zoospores or baits parasitized by S. aenigmatica, an immunosuppressor (dexamethasone) and a sharp scalpel can be used effectively to establish an experimental infection in P. mesopotamicus.(AU)

O sucesso do tratamento de uma enfermidade depende do estudo de moléculas em condições de laboratório por meio de protocolos de infecção experimental que viabilizam a compreensão da doença e da eficácia dos fármacos. Pela sequência ITS foram identificadas três cepas de Saprolegnia aenigmatica. Dessa forma, pacus sadios foram submetidos à imunossupressão com dexametasona (1,2 mg kg-1), esfoliados com auxílio de bisturi e distribuídos em aquários a 22ºC. Após este procedimento, um grupo de animais foi inoculado com 9.000 zoósporos/peixe subcutâneo (DEZ), a outro foram adicionadas três iscas colonizadas com o oomiceto na água (DEI), um terceiro grupo foi mantido sem contato com o oomiceto (DE) e um quarto grupo, de animais sadios, representaram o controle (C). Após 48 e 96h deste procedimento, foram eutanaziados animais de cada grupo para reisolamento. Os animais do grupo DE e C não apresentaram sinais clínicos e não foi reisolado o oomiceto. Porém, tanto os animais do grupo DEZ quanto como os animais do grupo DEI apresentaram micélio branco na pele e foi reisolado Saprolegnia aenigmatica. Assim, a infecção com zoósporos ou com iscas colonizadas por S. aenigmatica, com o uso de dexametasona e abrasivo epitelial são formas eficazes de infecção experimental em P. mesopotamicus.(AU)

Assuntos

RESUMO

The aim of this research was to evaluate the feasibility for the use of the organisms Lemna minor, Azolla caroliniana, Hyphessobrycon eques, Pomacea canaliculata and Daphnia magna as exposure bioindicators for ethanol (lethal and effective concentration 50% - LC50(I)/EC50(I)). Thus, the following concentrations were used 5.0; 10.0; 20.0; 30.0; 40.0 and 50.0 mg L-1 ethanol on L. minor; 25.0; 50.0; 75.0; 100.0; 150.0 and 200.0 mg L-1 on A. caroliniana; 0.3; 0.5; 1.0; 2.0 and 3.0 mg L-1 on H. eques; 0.05; 0.10; 0.20; 0.40 and 0.80 mg L-1 on P. canaliculata; and 40.0; 60.0; 80.0; 100.0; 120.0 and 140.0 mg L-1 on D. magna. An untreated control was also kept for all organisms, with three repetitions. The increase in the ethanol concentration elevated the electrical conductivity and decreased the water dissolved oxygen and pH. The ethanol LC50 for L. minor and A. caroliniana were 12.78 and 73.11 mg L-1, respectively, and was classified as slightly toxic; 1.22 mg L-1 for H. eques (moderately toxic); 0.39 mg L-1 for P. canaliculata (highly toxic) and 98.85 mg L-1 for D. magna (slightly toxic). Thus, H. eques and P. canaliculata have showed good potential for the use as ethanol exposure bioindicators on water bodies.

O objetivo deste estudo foi avaliar a viabilidade do uso dos organismos teste Lemna minor, Azolla caroliniana, Hyphessobrycon eques, Pomacea canaliculata e Daphnia magna como bioindicadores de exposição ao etanol (concentração letal e efetiva 50% - CL50(I)/CE50(I)). Assim, foram utilizadas as seguintes concentrações: 5,0; 10,0; 20,0; 30,0; 40,0 e 50,0 mg L-1 de etanol para L. minor; 25,0; 50,0; 75,0; 100,0; 150,0 e 200,0 mg L- 1 (A. caroliniana); 0,3; 0,5; 1,0; 2,0 e 3,0 mg L-1 (H. eques); 0,05; 0,10; 0,20; 0,40 e 0,80 mg L-1 (P. canaliculata ) e 40,0; 60,0; 80,0; 100,0; 120,0 e 140,0 mg L-1 para D. magna, todos com controle em triplicata. O aumento da concentração do etanol elevou a condutividade elétrica e diminuiu o oxigênio dissolvido e o pH da água. A CL50 do etanol para as macrófitas L. minor e A. caroliniana foi 12,78 e 73,11 mg L-1, respectivamente, sendo classificado como ligeiramente tóxico; para o H. eques, foi de 1,22 mg L-1 (moderadamente tóxico); 0,39 mg L-1 para o P. canaliculata (altamente tóxico) e 98,85 mg L-1 para D. magna (ligeiramente tóxico). Assim, o H. eques e o P. canaliculata apresentaram potencial para uso como organismos bioindicadores de exposição do etanol em corpos hídricos.

Assuntos

RESUMO

A paca (Cuniculus paca) é um roedor típico de regiões tropicais. Com a finalidade de estudar esta espécie selvagem para manejo adequado e sua preservação, objetivou-se neste trabalho caracterizar a histoquímica das glândulas anexas do trato reprodutor do macho da paca. Para este fim, cortes histológicos dessas glândulas foram submetidas às reações histoquímicas com Ácido Periódico de Schiff (PAS), Alcian blue (AB), PAS. + AB. e PAS + Amilase. Na glândula bulbouretral foi constatado que o epitélio produz secreção rica em glicoproteínas neutras e ácidas, glicosaminoglicanas, e em algumas regiões produz mais de um tipo de secreção. Não foi observada a presença de glicogênio no epitélio. Na glândula vesicular, seu epitélio em borda em escova corou-se por glicoproteínas neutras e também por substância de composição desconhecida, não contendo glicoproteínas ácidas, glicogênio ou glicosaminoglicanas. Verificou-se presença de pequena quantidade de glicoproteínas ácidas e neutras na próstata, em especial na mucosa, além de glicoproteínas ácidas carboxiladas e sulfatadas em pequena quantidade no tecido conjuntivo da lâmina própria dessa glândula. Por fim, a glândula coaguladora apresentou pequena quantidade de glicoproteínas neutras na borda em escova de seu epitélio e substância de composição desconhecida, sendo ausente o glicogênio. Conclui-se que as glândulas anexas do trato reprodutor da paca apresentam características histoquímicas que compartilham certa similaridade com outras espécies da ordem Rodentia, com a presença de glicoproteínas neutras e ácidas em algumas glândulas, principalmente no epitélio da glândula bulbouretal e na borda em escova do epitélio das demais glândulas.(AU)

Paca is a wild rodent typical of the tropical region. In order to study this species with focus on the proper management and preservation, this study aims to characterize the histochemistry of the accessory glands of the reproductive tract of the male paca. For this purpose, histological sections were stained with Periodic Acid-Schiff (PAS), Alcian Blue (AB), PAS + AB e PAS + Amilase. In the histochemical reaction of the bulbouretral gland was found that the epithelium produces secretion rich in neutral and acid glycoproteins, glycosaminoglycans, and in some regions produces more than one type of secretion. The epithelium did not contain any glycogen. In the vesicular gland the epithelium had bush border stained by neutral glycoproteins, but no acid glycoproteins, glycogen or glycosaminoglycan. The coagulating gland showed small amount of neutral glycoproteins in the brush border of the epithelium, without glycogen. It is concludes that the accessory glands of paca have histochemical characteristics that share some similarity with other species of the Order Rodentia, with some glands with neutral and acid glycoproteins, mainly in the epithelium of the bulbouretral gland and in the brush border of the other glands.(AU)

Assuntos

RESUMO

Paca is a wild rodent typical of the tropical region. In order to study this species with focus on the proper management and preservation, this study aims to characterize the histochemistry of the accessory glands of the reproductive tract of the male paca. For this purpose, histological sections were stained with Periodic Acid-Schiff (PAS), Alcian Blue (AB), PAS + AB e PAS + Amilase. In the histochemical reaction of the bulbouretral gland was found that the epithelium produces secretion rich in neutral and acid glycoproteins, glycosaminoglycans, and in some regions produces more than one type of secretion. The epithelium did not contain any glycogen. In the vesicular gland the epithelium had bush border stained by neutral glycoproteins, but no acid glycoproteins, glycogen or glycosaminoglycan. The coagulating gland showed small amount of neutral glycoproteins in the brush border of the epithelium, without glycogen. It is concludes that the accessory glands of paca have histochemical characteristics that share some similarity with other species of the Order Rodentia, with some glands with neutral and acid glycoproteins, mainly in the epithelium of the bulbouretral gland and in the brush border of the other glands.

A paca (Cuniculus paca) é um roedor típico de regiões tropicais. Com a finalidade de estudar esta espécie selvagem para manejo adequado e sua preservação, objetivou-se neste trabalho caracterizar a histoquímica das glândulas anexas do trato reprodutor do macho da paca. Para este fim, cortes histológicos dessas glândulas foram submetidas às reações histoquímicas com Ácido Periódico de Schiff (PAS), Alcian blue (AB), PAS. + AB. e PAS + Amilase. Na glândula bulbouretral foi constatado que o epitélio produz secreção rica em glicoproteínas neutras e ácidas, glicosaminoglicanas, e em algumas regiões produz mais de um tipo de secreção. Não foi observada a presença de glicogênio no epitélio. Na glândula vesicular, seu epitélio em borda em escova corou-se por glicoproteínas neutras e também por substância de composição desconhecida, não contendo glicoproteínas ácidas, glicogênio ou glicosaminoglicanas. Verificou-se presença de pequena quantidade de glicoproteínas ácidas e neutras na próstata, em especial na mucosa, além de glicoproteínas ácidas carboxiladas e sulfatadas em pequena quantidade no tecido conjuntivo da lâmina própria dessa glândula. Por fim, a glândula coaguladora apresentou pequena quantidade de glicoproteínas neutras na borda em escova de seu epitélio e substância de composição desconhecida, sendo ausente o glicogênio. Conclui-se que as glândulas anexas do trato reprodutor da paca apresentam características histoquímicas que compartilham certa similaridade com outras espécies da ordem Rodentia, com a presença de glicoproteínas neutras e ácidas em algumas glândulas, principalmente no epitélio da glândula bulbouretal e na borda em escova do epitélio das demais glândulas.

Assuntos

RESUMO

The aims of this research were to evaluate the efficacy of copper oxychloride (CuCl2.3Cu(OH)2), copper hydroxide (Cu(OH)2) and diquat (1.1'-ethylene-2.2'-bipyridyldiylium dibromide), isolated and in association with 0.1% of both copper sources, in the control of the unicellular algae Ankistrodesmus gracilis and the filamentous algae Pithophora kewesis, and to determine the acute toxicity of the tested chemicals in Hyphressobrycon eques, Pomacea canaliculata, Lemna minor and Azolla caroliniana. The efficacy was estimated by the methods of chlorophyll a and pheophytin a readings, changed into growth inhibition percentage. Both algae were exposed to the following concentrations: 0.2; 0.4; 0.8; 1.2 mg L(-1) of diquat and its association with the copper sources; and 0.1; 0.3; 0.5; 0.7; 1.0 and 1.5 mg L(-1) in the isolated applications of copper hydroxide and copper oxychloride. An untreated control was kept. The acute toxicity was estimatedby 50% lethal concentration (LC50). The copper sources were effective for A. gracilis control, at rates as high as 0.1 mg L(-1) (>95% efficacy). Isolated diquat and its association with copper hydroxide were both effective at rates as high as 0.4 mg L(-1), with 95 and 88% control efficacy, respectively. The copper oxychloride was effective at 0.2 mg L(-1), with 93% efficacy. None of the tested chemicals and associations was effective on P. kewesis control. The most sensitive non target organism to the tested chemicals was L. minor; the less sensitive was H. eques.

Assuntos

RESUMO

The aim of this research was to evaluate the feasibility for the use of the organisms Lemna minor, Azolla caroliniana, Hyphessobrycon eques, Pomacea canaliculata and Daphnia magna as exposure bioindicators for ethanol (lethal and effective concentration 50% - LC50(I)/EC50(I)). Thus, the following concentrations were used 5.0; 10.0; 20.0; 30.0; 40.0 and 50.0 mg L-1 ethanol on L. minor; 25.0; 50.0; 75.0; 100.0; 150.0 and 200.0 mg L-1 on A. caroliniana; 0.3; 0.5; 1.0; 2.0 and 3.0 mg L-1 on H. eques; 0.05; 0.10; 0.20; 0.40 and 0.80 mg L-1 on P. canaliculata; and 40.0; 60.0; 80.0; 100.0; 120.0 and 140.0 mg L-1 on D. magna. An untreated control was also kept for all organisms, with three repetitions. The increase in the ethanol concentration elevated the electrical conductivity and decreased the water dissolved oxygen and pH. The ethanol LC50 for L. minor and A. caroliniana were 12.78 and 73.11 mg L-1, respectively, and was classified as slightly toxic; 1.22 mg L-1 for H. eques (moderately toxic); 0.39 mg L-1 for P. canaliculata (highly toxic) and 98.85 mg L-1 for D. magna (slightly toxic). Thus, H. eques and P. canaliculata have showed good potential for the use as ethanol exposure bioindicators on water bodies.(AU)

O objetivo deste estudo foi avaliar a viabilidade do uso dos organismos teste Lemna minor, Azolla caroliniana, Hyphessobrycon eques, Pomacea canaliculata e Daphnia magna como bioindicadores de exposição ao etanol (concentração letal e efetiva 50% - CL50(I)/CE50(I)). Assim, foram utilizadas as seguintes concentrações: 5,0; 10,0; 20,0; 30,0; 40,0 e 50,0 mg L-1 de etanol para L. minor; 25,0; 50,0; 75,0; 100,0; 150,0 e 200,0 mg L-1 (A. caroliniana); 0,3; 0,5; 1,0; 2,0 e 3,0 mg L-1 (H. eques); 0,05; 0,10; 0,20; 0,40 e 0,80 mg L-1 (P. canaliculata) e 40,0; 60,0; 80,0; 100,0; 120,0 e 140,0 mg L-1 para D. magna, todos com controle em triplicata. O aumento da concentração do etanol elevou a condutividade elétrica e diminuiu o oxigênio dissolvido e o pH da água. A CL50 do etanol para as macrófitas L. minor e A. caroliniana foi 12,78 e 73,11 mg L-1, respectivamente, sendo classificado como ligeiramente tóxico; para o H. eques, foi de 1,22 mg L-1 (moderadamente tóxico); 0,39 mg L-1 para o P. canaliculata (altamente tóxico) e 98,85 mg L-1 para D. magna (ligeiramente tóxico). Assim, o H. eques e o P. canaliculata apresentaram potencial para uso como organismos bioindicadores de exposição do etanol em corpos hídricos.(AU)

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RESUMO

The aims of this study were to evaluate the possibility of using the tetra-serpae fish (Hyphessobrycon eques) and macrophyte duckweed (Lemna minor) as biomarkers of toxicity of vinasse, estimating the LC50 and mortality percentages of the test organisms in the period crop of sugarcane. The concentrations tested were: 0.5; 1.0; 1.5; 2.0; 2.5; 3.0; 3.5; 4.0; 4.5; 5.0; 7.5 and 10% vinasse, with three fish per repetition and three repetitions, and the macrophytes were exposed to: 1.0; 3.0; 5.0 and 7.0% of vinasse, with 12 fronds per repetition and three repetitions, both completely randomized design in tests (CRD). The LC50 values for fish ranged from 0.75 to 7.72% and macrophyte, 1.30 to 4.27%. The biomarkers H. eques (fish tetra serpae) and L. minor (macrophyte duckweed) can be used in ecotoxicological effluent vinasse ratings, which is very toxic to fish during the months of August and September and toxic for fish and for macrophyte duckweed in the remaining months of trial.(AU)

Os objetivos deste estudo foram avaliar a possibilidade de utilização do peixe mato grosso (Hyphessobrycon eques) e da macrófita lentilha dágua (Lemna minor) como bioindicadores da toxicidade da vinhaça, estimando a CL50 e as porcentagens de mortalidade dos organismos-teste no período de safra da cana-de-açúcar. As concentrações testadas foram: 0,5; 1,0; 1,5; 2,0; 2,5; 3,0; 3,5; 4,0; 4,5; 5,0; 7,5 e 10% de vinhaça, com três peixes por repetição e três repetições, e as macrófitas foram expostas a: 1,0; 3,0; 5,0 e 7,0% de vinhaça, com 12 frondes por repetição e três repetições, ambos os testes em delineamento inteiramente casualizado (DIC). Os valores de CL50 para o peixe variaram de 0,75 a 7,72% e para macrófita, de 1,30 a 4,27%. Os bioindicadores H. eques (peixe mato grosso) e L. minor (macrófita lentilha dágua) podem ser utilizados em avaliações ecotoxicológicas do efluente vinhaça, sendo esta muito tóxica para o peixe nos meses de agosto e setembro e tóxica para o peixe e para a macrófita lentilha dágua nos demais meses de ensaio.(AU)

Assuntos

RESUMO

The aims of this study were to evaluate the possibility of using the tetra-serpae fish (Hyphessobrycon eques) and macrophyte duckweed (Lemna minor) as biomarkers of toxicity of vinasse, estimating the LC50 and mortality percentages of the test organisms in the period crop of sugarcane. The concentrations tested were: 0.5; 1.0; 1.5; 2.0; 2.5; 3.0; 3.5; 4.0; 4.5; 5.0; 7.5 and 10% vinasse, with three fish per repetition and three repetitions, and the macrophytes were exposed to: 1.0; 3.0; 5.0 and 7.0% of vinasse, with 12 fronds per repetition and three repetitions, both completely randomized design in tests (CRD). The LC50 values for fish ranged from 0.75 to 7.72% and macrophyte, 1.30 to 4.27%. The biomarkers H. eques (fish tetra serpae) and L. minor (macrophyte duckweed) can be used in ecotoxicological effluent vinasse ratings, which is very toxic to fish during the months of August and September and toxic for fish and for macrophyte duckweed in the remaining months of trial.

Os objetivos deste estudo foram avaliar a possibilidade de utilização do peixe mato grosso (Hyphessobrycon eques) e da macrófita lentilha dágua (Lemna minor) como bioindicadores da toxicidade da vinhaça, estimando a CL50 e as porcentagens de mortalidade dos organismos-teste no período de safra da cana-de-açúcar. As concentrações testadas foram: 0,5; 1,0; 1,5; 2,0; 2,5; 3,0; 3,5; 4,0; 4,5; 5,0; 7,5 e 10% de vinhaça, com três peixes por repetição e três repetições, e as macrófitas foram expostas a: 1,0; 3,0; 5,0 e 7,0% de vinhaça, com 12 frondes por repetição e três repetições, ambos os testes em delineamento inteiramente casualizado (DIC). Os valores de CL50 para o peixe variaram de 0,75 a 7,72% e para macrófita, de 1,30 a 4,27%. Os bioindicadores H. eques (peixe mato grosso) e L. minor (macrófita lentilha dágua) podem ser utilizados em avaliações ecotoxicológicas do efluente vinhaça, sendo esta muito tóxica para o peixe nos meses de agosto e setembro e tóxica para o peixe e para a macrófita lentilha dágua nos demais meses de ensaio.

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The aim of this study was to determine the environmental concentration of atrazine (ATZ) in five streams located in the north of São Paulo state (Brazil) and evaluate its toxicological impact on young specimens of the pacu fish Piaractus mesopotamicus. Samples of water were collected on three occasions between 2010 and 2011, corresponding to periods signifying the beginning, middle, and end of rain season. ATZ levels were estimated by a high-performance liquid chromatography coupled with a mass spectrometry (HPLC-MS/MS) triple quadrupole. Later, the quotient of environmental risk (QR) was determined based on the medium lethal concentration (LC50 48 h), non-observable effect concentration (NOEC), and the estimated environmental concentration (EEC) of ATZ detected in the environment. Histological changes in gills and liver were also studied, along with the brain activity of the enzyme acetylcholinesterase (AChE). The highest concentration of ATZ measured was 10.4 µg L(-1). The ATZ LC50 (48 h) for young P. mesopotamicus was 24.46 mg L(-1) and the QR was classified as "safe". Although the QR indicated that ATZ could be safe for the tested species, it caused many histological alterations in the liver and gills of the exposed specimens, and an increase in the AChE levels.

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Fish parasites are among the crucial limiting factors in aquaculture. The organophosphorous pesticide trichlorfon is widely used as an insecticide and against fish parasites worldwide. In this study, the effects of environmental trichlorfon on biochemical and physiological parameters were investigated in Piaractus mesopotamicus (pacu), a widely farmed fish in South America, through sublethal exposure (8 µg L(-1), 10 % of the LC50; 96 h) and recovery. The activity of brain acetylcholinesterase (AChE) was reduced after exposure (15.5 %) and remained decreased during the recovery (21.5 %). In white muscle, AChE activity decreased 31 % only after recovery. Alkaline phosphatase (ALP) and acid phosphatase (ACP) activities of the liver, muscle and plasma were steady during exposure. However, after the recovery period, ALP activity was increased in the liver and muscle and decreased in plasma, while ACP was increased in the liver and decreased in muscle. Intermediary metabolism was also affected by trichlorfon, depicting increase of energetic demand (hypoglycemia, neoglucogenesis and lipid catabolism), which remained even after recovery. These results indicate that P. mesopotamicus is adversely affected by sublethal concentrations of trichlorfon and are useful for assessing the impact as well as the pros and cons of its use in controlling fish parasites in aquaculture.

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Este estudo teve como objetivo avaliar as possíveis alterações histopatológicas hepática de tilápias do Nilo alimentadas com dietas contendo silagem biológica de pescado com diferentes concentrações protéicas. Foram utilizados 180 juvenis alimentados com dietas contendo três níveis de proteína (20, 24 and 28% PB), e duas proporções de silagem biológica (» e ½) durante 75 dias. Os fragementos de fígado foram fixados em Bouin e inclusos em Histosec®. Posteriorente foram cortados em microtomo com espessura de 2 a 5µm. O método utilizado para coloração foi hematoxilina/eosina e PAS. Os cortes histológicos foram analisados em microscopio de luz. O desarranjo na morfologia do fígado dos peixes alimentados com silagem biológica foi influenciado pelos altos níveis protéicos, e pelo aumento ½ de proporções de proteínas de origem animal das dietas. Foi observado que a variação dos hepatócitos está diretamente ligada com o tipo da dieta fornecida para os peixes. Nos peixes alimentados com as dietas contendo 28% PB, o fígado apresentou desarranjo da estrutura cordonal dos hepatócitos, pontos de necrose e deslocamento do núcleo para periferia. Níveis elevados de silagem biológica de pescado provoca alterações deletérias no fígado. O nível de proteína adequado para manter o desenvolvimento associado à saúde do peixe é de 24%PB.(AU)

This study aimed to evaluate possible histopathological liver of tilapia fed diets containing fish silage and level protein. Sample of 180 fed with tilapia fingerlings fed with diets containing three protein levels (20, 24 and 28% CP), and Proportions residue fermented silage of tilapia (» and ½) of were analyzed during 75 days. The tissue fragments were fixed in Bouin and included in Histosec®. After that, between 2 to 5µm slices were done in a rotation microtome. The methods used for tissue analysis were hematoxilin/eosin and PAS. The histological slices were examined under light microscope (Olympus BX-50). The disarray in the morphology of the liver of fish fed biological silage was influenced by high protein levels, and increased proportions of ½ of animal protein diets. It was observed that the variation of hepatocytes is directly related to the type of diet for fish. In fish fed diets containing 28% CP, the liver showed disruption of the structure cordon of hepatocytes, necrosis and shifting points of the core to the periphery. Elevated levels of biological fish silage cause deleterious changes in the liver. The level of protein required to maintain the health of the associated development fish is 24% crude protein.(AU)

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The aim of this study was to estimate copper sulfate acute toxicity and to determine death percentage and environmental risk on guppy fish (Phallocerus caudimaculatus), zebrafish (Brachydanio rerio), mato grosso (Hyphessobrycon eques), and pacu (Piaractus mesopotamicus). Fish were exposed to 0.01, 0.03, 0.05, 0.07, 0.10, and 0.30 mg L-1 (guppy), 0.05, 0.07, 0.10, and 0.30 mg L-1 (zebrafish), 0.07, 0.10, 0.20, and 0.30 mg L-1 (mato grosso) and 9.5, 10.0, 10.5, 11.0, 11.5, and 12.0 mg L-1 (pacu) of copper sulfate, with triplicate control. The estimated 50% average lethal concentrations (LC50; 96 hours) were 0.05 (guppy), 0.13 (zebrafish); 0.16 (mato grosso) and 10.36 mg L-1 (pacu). Copper sulfate was extremely toxic for guppy, highly toxic for zebrafish and mato grosso and lightly toxic for pacu and presents environmental risk of high adverse effects on the guppy, zebrafish and mato grosso and moderate adverse effect to the pacu. Therefore, the guppy fish, zebrafish, and mato grosso are important alternatives for copper sulfate toxicity evaluation in waterbodies.

O objetivo deste estudo foi estimar a toxicidade aguda, determinar a porcentagem de mortalidade e o risco ambiental do sulfato de cobre para o peixe guaru (Phallocerus caudimaculatus), zebrafish (Brachydanio rerio), mato grosso (Hyphessobryconeques) e pacu (Piaractus mesopotamicus). Para realização dos ensaios com sulfato de cobre foram utilizados: 0,01; 0,03; 0,05; 0,07; 0,10 e 0,30 mg L-1 (guaru), 0,05; 0,07; 0,10 e 0,30 mg L-1 (paulistinha), 0,07; 0,10; 0,20 e 0,30 mg L-1 (mato grosso) e 9,5; 10,0; 10,5; 11,0; 11,5 e 12,0 mg L-1 (pacu) como controle em triplicata. A concentração letal média 50% (CL50; 96h) estimada para o guaru foi de 0,05, para o paulistinha foi de 0,13 para o mato grosso foi de 0,16 e para o pacu foi de 10,36 mg L-1. O sulfato de cobre foi classificado como extremamente tóxico para o guaru, altamente tóxico para o paulistinha e mato grosso e ligeiramente tóxico para o pacu e apresenta risco ambiental de elevado efeito adverso para o guaru, paulistinha e mato grosso e moderado efeito adverso para o pacu. Assim, conclui-se que o guaru, paulistinha e mato grosso são importantes alternativas para avaliação da toxicidade do sulfato de cobre em corpos hídricos.

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The aims of this research were to evaluate the acute toxicity (LC/EC50) and the environmental risk of toltrazuril (TOL) and florfenicol (FFC) for plant Lemna minor, snail Pomacea canalicuta, fish Piaractus mesopotamicus and Hyphessobrycon eques and the microcrustace an Daphnia magna. The organisms were acclimated in room bioassay with controlled temperature according to standard to each one. They were exposed at nominal concentrations in static system. For environmental risk (RQ) was used the estimated environmental concentration (EEC) that is the dosage indicate to treatment and the lethal or effective concentration (LC/CE50) from each drug in acute exposure. FFC showed LC50; 7d of 97.03 mg L-1 for L. minor; >100.0 mg L-1 for P. mesopotamicus and H. eques and EC50; 48h > 100.0 mg L-1 for P. canaliculata and D. magna, and it was classified low risk (RQ =0.01) for all bioindicators. TOL howed LC50; 7d >100.0 mg L-1 for L. minor, 3.72 mg L-1 for P. mesopotamicus; 6.22 mg L-1 for H. eques and CE50;48h of 7.59 mg L-1 for P. canaliculata and 18.57mg L-1 for D. magna, and it was classified low risk (RQ = 0.01) for L. minor and high risk for P. mesopotamicus (RQ= 2.68), H. eques (RQ= 6.22), P. canaliculata (RQ= 1.31)and D. magna (RQ=0.53). Lemnaminor was the bioindicator indicating of FFC toxicity and H. eques, bioindicator of the TOL. FFC is safety however and the use of TOL necessaries cautions to treat the wastewaterbefore discard on the environment.(AU)

Os objetivos deste estudo foram avaliar a toxicidade aguda(CL/CE50)e o risco ambientaldo toltrazuril (TOL) e doflorfenicol(FFC)paraa planta aquática Lemna minor,o caramujo Pomacea canalicuta,os peixes Piaractus mesopotamicuseHyphessobrycon equeseo microcrustáceo Daphnia magna.Os organismos foram aclimatados em salas de bioensaiode acordo com as normas vigentes para cada organismo. Estesforam expostos àsconcentrações nominaisem sistema estático. Para a avaliação do risco ambiental (RQ) foiutilizadaa concentração ambiental estimada (CAE),concentraçãoindicada para tratamentoe a concentração letal ou efetiva (CL/CE50) de cada fármacoem exposição aguda.OFFC apresentouCL50;7dde97,03 mgL-1para L. minor; >100,0mgL-1 para P. mesopotamicuse H. equeseCE50;48h > 100,0mgL-1para P. canaliculatae paraD. magna, e causabaixo risco (RQ = 0,01)para os bioindicadores.O TOL apresentou CL50;7d >100,0mgL-1para L. minor, 3,72 mgL-1para P. mesopotamicus;6,22 mg L-1para o H. equese CE50;48h de 7,59 mgL-1para P. canaliculatae 18,57 mgL-1 para D. magna,ecausabaixo risco (RQ =0,01)para L. minore alto risco para P. mesopotamicus(RQ= 2,68); para H. eques (RQ= 6,22), para P. canaliculata(RQ= 1,31)epara D. magna(RQ= 0,53). Lemnaminoré o melhor bioindicador da toxicidade do FFC e H. eques,bioindicador do TOL. O FFC é seguropara uso na aquicultura, porém oTOL causa risco para os bioindicadores.(AU)

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The aims of this research were to evaluate the acute toxicity (LC/EC50) and the environmental risk of toltrazuril (TOL) and florfenicol (FFC) for plant Lemna minor, snail Pomacea canalicuta, fish Piaractus mesopotamicus and Hyphessobrycon eques and the microcrustace an Daphnia magna. The organisms were acclimated in room bioassay with controlled temperature according to standard to each one. They were exposed at nominal concentrations in static system. For environmental risk (RQ) was used the estimated environmental concentration (EEC) that is the dosage indicate to treatment and the lethal or effective concentration (LC/CE50) from each drug in acute exposure. FFC showed LC50; 7d of 97.03 mg L-1 for L. minor; >100.0 mg L-1 for P. mesopotamicus and H. eques and EC50; 48h > 100.0 mg L-1 for P. canaliculata and D. magna, and it was classified low risk (RQ =0.01) for all bioindicators. TOL howed LC50; 7d >100.0 mg L-1 for L. minor, 3.72 mg L-1 for P. mesopotamicus; 6.22 mg L-1 for H. eques and CE50;48h of 7.59 mg L-1 for P. canaliculata and 18.57mg L-1 for D. magna, and it was classified low risk (RQ = 0.01) for L. minor and high risk for P. mesopotamicus (RQ= 2.68), H. eques (RQ= 6.22), P. canaliculata (RQ= 1.31)and D. magna (RQ=0.53). Lemnaminor was the bioindicator indicating of FFC toxicity and H. eques, bioindicator of the TOL. FFC is safety however and the use of TOL necessaries cautions to treat the wastewaterbefore discard on the environment.

Os objetivos deste estudo foram avaliar a toxicidade aguda(CL/CE50)e o risco ambientaldo toltrazuril (TOL) e doflorfenicol(FFC)paraa planta aquática Lemna minor,o caramujo Pomacea canalicuta,os peixes Piaractus mesopotamicuseHyphessobrycon equeseo microcrustáceo Daphnia magna.Os organismos foram aclimatados em salas de bioensaiode acordo com as normas vigentes para cada organismo. Estesforam expostos àsconcentrações nominaisem sistema estático. Para a avaliação do risco ambiental (RQ) foiutilizadaa concentração ambiental estimada (CAE),concentraçãoindicada para tratamentoe a concentração letal ou efetiva (CL/CE50) de cada fármacoem exposição aguda.OFFC apresentouCL50;7dde97,03 mgL-1para L. minor; >100,0mgL-1 para P. mesopotamicuse H. equeseCE50;48h > 100,0mgL-1para P. canaliculatae paraD. magna, e causabaixo risco (RQ = 0,01)para os bioindicadores.O TOL apresentou CL50;7d >100,0mgL-1para L. minor, 3,72 mgL-1para P. mesopotamicus;6,22 mg L-1para o H. equese CE50;48h de 7,59 mgL-1para P. canaliculatae 18,57 mgL-1 para D. magna,ecausabaixo risco (RQ =0,01)para L. minore alto risco para P. mesopotamicus(RQ= 2,68); para H. eques (RQ= 6,22), para P. canaliculata(RQ= 1,31)epara D. magna(RQ= 0,53). Lemnaminoré o melhor bioindicador da toxicidade do FFC e H. eques,bioindicador do TOL. O FFC é seguropara uso na aquicultura, porém oTOL causa risco para os bioindicadores.

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Fish commonly known as acaris or plecos are freshwater armored catfish economically important as a food resource and as ornamental fish. Most of these species are captured in the Amazon region. However, despite its economic importance, there is a lack of knowledge about their biological aspects. Thus, this study aimed to characterize and evaluate the histopathological aspects of important organs as gills, liver, integument and kidney of seven species of armored freshwater ornamental catfish fromGuamáRiver,Pará State,Brazil. All organs showed typical characteristics of organs of other teleosts. In some species, gills and liver showed slight histopathological changes: telangiectasis, edema and morphological changes related to the presence of parasites (Monogenea and Digenea) in the gills, and changes in the arrangement of hepatocytes rows, and vacuolation of hepatocytes in the liver. Thus, the knowledge of the normal structure of organs and changes found can be used as tools for environmental and health monitoring of animals.(AU)

Os peixes conhecidos como Acaris ou Cascudos são siluriformes de água doce com o corpo revestido por placas ósseas, economicamente importantes como fonte de alimento e peixes ornamentais. A maioria destas espécies é capturada na região amazônica. Contudo, apesar de sua importância econômica, há desconhecimento sobre os aspectos biológicos desses peixes. Assim, o objetivo deste trabalho foi caracterizar e avaliar histologicamente órgãos importantes (brânquias, fígado, rim e tegumento) de sete espécies de peixes ornamentais de água doce do rio Guamá, Pará, Brasil. Todos os órgãos observados apresentaram as características típicas dos órgãos de teleósteos. Em algumas espécies, as brânquias e o fígado mostraram pequenas alterações histopatológicas: edema, telangiectasias e alterações morfológicas relacionadas com a presença de parasitas (Monogenea e Digenea) nas brânquias, e modificações no arranjo de linhas de cordões de hepatócitos e vacuolização destas células foram também observadas. Assim, o conhecimento da estrutura dos órgãos e as alterações encontradas podem ser utilizados como ferramentas para o monitoramento ambiental e sanitário dos animais.(AU)

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