Emprego de microscopia de fluorescência para a quantificação microbiana em amostras salinas da indústria do petróleo

Os micro-organismos constituem um grande problema em termos econômicos para a indústria petrolífera. Estes são responsáveis pela produção de substâncias corrosivas e a formação de biofilmes, que causam deterioração dos materiais metálicos. Os principais grupos microbianos presentes em amostras ambientais da indústria do petróleo são as bactérias anaeróbias heterotróficas totais (BANHT) e as bactérias redutoras de sulfato (BRS). Atualmente, a quantificação desses grupos microbianos é realizada através da técnica do Número Mais Provável (NMP) que estima o resultado em aproximadamente 28 dias. Neste trabalho foi otimizada uma metodologia para a microscopia de fluorescência de amostras salinas provenientes de tanques de armazenamento de água/óleo. As condições testadas foram o tipo de óleo de imersão, o tipo de diluente, o volume do corante, o volume da amostra corada e a concentração do fixador (glutaraldeído) numa tentativa de correlacionar com resultados de quantificação de BANHT e BRS através da técnica convencional do NMP. Nesse caso, as células totais foram quantificadas por microscopia de fluorescência utilizando o corante fluorescente laranja de acridina (AO). Verificou-se que houve uma correlação entre os resultados da quantificação de células totais por microscopia de fluorescência e os resultados de BANHT pela técnica do NMP, devido a pouca variação de valores expressos em ambas as quantificações. Entretanto, não foi possível correlacionar os resultados da quantificação de células totais com os resultados de BRS por NMP devido à grande variação dos valores de quantificação de BRS. Na microscopia de fluorescência, foi possível, quantificar os micro-organismos em aproximadamente 30 minutos e através das fotografias, verificou-se ainda que as amostras apresentaram-se nítidas e os micro-organismos com uma boa fluorescência

Avaliação da toxicidade da emodina e sua associação com radiação ultravioleta A em cepas de Escherichia coli e células da linhagem A549

A emodina é uma antraquinona estruturalmente semelhante à aloe-emodina e ambas tem sido apontadas como capazes de causar lesões oxidativas pela produção de ERO. Sua presença em produtos dermocosméticos e de higiene pessoal, associada às informações de que a fotoativação de antraquinonas levaria ao aumento de lesões oxidativas causadas por ERO, torna relevante o estudo da associação da emodina com a radiação UVA. O objetivo desse trabalho foi avaliar a citotoxicidade induzida pela associação da emodina com doses subletais de radiação UVA, em células de Escherichia coli (selvagem e cepas deficientes em enzimas do BER), através de ensaios de sobrevivência bacteriana (taxa de dose de UVA igual a 20J/m/s, totalizando 108kJ/m ao final de 90min de experimento), e em células da linhagem A549 pela exclusão do corante azul de tripan e sobrevivência clonogênica(taxa de dose de UVA igual a 20J/m/s, totalizando 36kJ/m ao final de 30min de experimento). Além disso, a genotoxicidade desses agentes foi estudada por eletroforese em gel de agarose de DNA plasmidial (taxa de dose de UVA igual a 16J/m/s, totalizando 57,6kJ/m ao final de 60min de experimento). De acordo com os resultados: i) Concentrações iguais ou abaixo de 5,55mM de emodina não alteraram a sobrevivência em nenhuma das cepas estudas; ii) As proteínas Xth e Fpg parecem ter um papel importante no reparo das lesões causadas pela emodina, em altas concentrações, sugerindo a participação do reparo por excisão de bases (BER) nesse processo; iii) A associação da emodina com a radiação UVA se mostrou citotóxica em todas as cepas de E. coli; iv) O gene nfo foi o mais importante na resistência bacteriana às lesões induzidas pela associação dos dois agentes, reforçando o envolvimento do BER e indicando uma possível participação do reparo por incisão de nucleotídeos (NIR); v) A emodina parece ter interagido com o DNA plasmidial, alterando seu padrão de migração no gel de agarose; vi) Em células da linhagem A549, a emodina causa efeitos tóxicos imediatos que parecem ser reparados ao longo do tempo. Porém, quando a droga permaneceu por 24 horas em contato com as células, houve uma diminuição na sobrevivência celular que parece ser dosedependente; vii) As concentrações de 10μM e 25μM de emodina, quando associadas ao UVA, se mostraram responsáveis pela redução de mais de 50% na sobrevivência nas células A549, chegando a 100% de morte quando a concentração de emodina foi de 50μM; viii) A radiação UVA potencializou os efeitos citotóxicos da emodina, nos 2 modelos experimentais do presente estudo, indicando que a interação da emodina com a radiação UVA seja genotóxica e portanto prejudicial à saúde.

Avaliação de alterações morfológicas da pele após lesão radioinduzida em ratos Wistar

A radioterapia é uma das modalidades terapêuticas mais utilizadas no tratamento do câncer, visando à destruição das células neoplásicas, a partir da utilização de radiação ionizante. Um dos fatores limitantes da radioterapia é o dano em tecidos sadios vizinhos ao tumor. A irradiação da pele, acidental ou para fins terapêuticos, pode desencadear uma série de lesões culminando na fibrose, o que implica na alteração funcional deste órgão. A avaliação dos efeitos morfológicos associados à irradiação da pele torna-se fundamental para estabelecer estratégias de irradiação mais eficazes e diminuição da morbidade; e em caso de acidentes, adequado manuseio da vítima. O objetivo deste estudo foi avaliar as alterações dérmicas radioinduzidas, utilizando um modelo em ratos. Ratos Wistar, machos, com três meses de idade, tiveram sua pele irradiada, em um campo de 3cm2, com doses únicas de 10, 40 e 60 Gy de elétrons com energia nominal de 4MeV. Após a irradiação, os animais permaneceram sob avaliação constante, sendo as lesões registradas fotograficamente. Os animais foram divididos em grupos e eutanasiados: no dia da irradiação, 5, 10, 15, 25 e 100 dias após a irradiação. Parte da pele foi fixada em formaldeído, incluída em parafina e submetida à microtomia. Os cortes foram corados com hematoxilina-eosina, picrosirius red e imunomarcados com anticorpo anti-TGF-beta1. Outra parte do tecido foi fixada em glutaraldeido e processada para microscopia eletrônica de varredura. Foi observado macroscopicamente o surgimento de lesões cutâneas semelhantes a queimaduras em toda área irradiada. Ao microscópio óptico foi verificado o inicio de desenvolvimento de lesão 5 dias após irradiação. Decorridos 10 dias da irradiação observou-se indícios de cicatrização epidérmica abaixo da crosta formada pela lesão. Aos 15 dias após a irradiação o tecido abaixo da lesão apresentava epiderme reconstruída e características de cicatrização tecidual. Foi visualizado também um infiltrado de polimorfonucleares significativo. Após 25 dias nas doses mais elevadas as lesões persistiam, o que não ocorreu na menor dose, na qual a área irradiada dos animais já se encontrava completamente cicatrizada. Após 100 dias da irradiação na dose de 40 Gy ocorreu a cicatrização da ferida. Na dose de 60 Gy em alguns animais a lesão persistia. Nos animais em que ocorreu a cicatrização houve uma hipertrofia da epiderme (acantose). Foi visualizado um tecido com aspecto morfológico totalmente descaracterizado, e necrosado. Os resultados encontrados na analise através de microscopia eletrônica de varredura corroboram os dados encontrados na microscopia de luz, onde observou-se a descaracterização das fibras de colágeno nas doses mais elevadas. Os resultados indicam que as doses utilizadas induziram um processo inflamatório importante na pele, ativando o sistema imunológico. Este fato promoveu um aumento na expressão do TGFbeta1, um dos responsáveis pelo aumento da produção da matriz extracelular por vários tipos celulares, principalmente por fibroblastos em tecidos lesionados. Alem do aumento de expressão da MEC, o TGFbeta1 também promove a inibição dos processos de degradação da mesma. A intensa expressão desta citocina na pele irradiada pode desencadear o processo de fibrose e, conseqüentemente, afetar a homeostase deste órgão devido ao acúmulo da MEC.

Avaliação de biocidas no controle da corrosão microbiologicamente induzida do aço carbono 1020 por bactérias redutoras de sulfato

Bactérias redutoras de sulfato (BRS) são os principais micro-organismos envolvidos na corrosão microbiologicamente induzida (CMI). Estas bactérias reduzem o sulfato, tendo como resultado a produção de H2S, o que pode influenciar os processos anódico e catódico na corrosão de materiais metálicos em ambientes marinhos, óleos e solos úmidos. Uma das formas de prevenir e controlar esse tipo de corrosão é a adição de biocidas ao meio corrosivo. Esta dissertação tem como objetivo avaliar o uso de biocidas no controle da CMI do aço AISI 1020 por BRS. Para isto, o comportamento da CMI no aço foi avaliado em água do mar sintética, em condições de anaerobiose, na ausência e na presença de uma cultura mista contendo BRS. Um biocida natural (óleo de alho) e outro comercial (glutaraldeído) foram utilizados para controlar a corrosão causada por estas bactérias. Duas formas de adição de biocida foram avaliadas: antes da formação do biofilme e após sua formação na superfície do metal. O crescimento microbiano na superfície do aço foi avaliado através da quantificação das BRS sésseis, pelo método do número mais provável (NMP). O comportamento eletroquímico do aço, na ausência e na presença de BRS e também para os ensaios com biocidas, foi estudado através das técnicas de espectroscopia de impedância eletroquímica (EIE) e polarização potenciodinâmica, sempre usando água do mar sintética como meio eletrolítico. A formação de biofilme e de produtos de corrosão na superfície do aço foi observada através da microscopia eletrônica de varredura (MEV). Os resultados mostraram que o aço exposto ao meio contendo BRS apresentou um processo corrosivo mais acelerado, quando comparado aos sistemas na ausência de micro-organismo. Esse processo foi evidenciado por um decréscimo na magnitude do arco capacitivo, nos ensaios de EIE, e um aumento da densidade de corrente de corrosão (Icorr), nos ensaios de polarização. Na análise de MEV, foi possível observar a formação de corrosão localizada após a remoção do biofilme da superfície. Os ensaios com biocidas, adicionados antes da formação de biofilmes, mostraram uma redução no número de bactérias sésseis, quando comparados com os ensaios sem biocida realizados pelo mesmo período de tempo (7 dias). Foi verificado também um decréscimo do processo corrosivo do aço, evidenciado através de aumento nos arcos capacitivos, nos ensaios de EIE e pelos menores valores de Icorr nos ensaios de polarização, quando comparados com o biofilme formado sem biocidas, nas mesmas condições. Apesar de não ter inibido completamente o crescimento das BRS sésseis, o óleo de alho apresentou maior redução no processo corrosivo quando comparado ao glutaraldeído, indicando sua possível aplicação como biocida natural nestas condições. Os ensaios realizados com biocidas adicionados após a formação do biofilme mostraram que o glutaraldeído apresentou alta eficácia em reduzir o número de células sésseis. Já o óleo de alho exibiu uma ação menos efetiva, sugerindo que este composto não conseguiu penetrar completamente a matriz do biofilme. Entretanto, ambos causaram aceleração do processo corrosivo do aço no meio estudado após 7 dias de exposição

Microbial community analysis of Acropora palamata mucus swabs, water and sediment samples from Hawksnest Bay, St. John, U.S. Virgin Islands

Colonies of the scleractinian coral Acropora palmata, listed as threatened under the US Endangered Species Act in 2006, have been monitored in Hawksnest Bay, within Virgin Islands National Park, St. John, from 2004 through 2010 by scientists with the US Geological Survey, National Park Service, and the University of the Virgin Islands. The focus has been on documenting the prevalence of disease, including white band, white pox (also called patchy necrosis and white patches), and unidentified diseases (Rogers et al., 2008; Muller et al., 2008). In an effort to learn more about the pathologies that might be involved with the diseases that were observed, samples were collected from apparently healthy and diseased colonies in July 2009 for analysis. Two different microbial assays were performed on Epicentre Biotechnologies DNA swabs containing A. palmata coral mucus, and on water and sediment samples collected in Hawksnest Bay. Both assays are based on polymerase chain reaction (PCR) amplification of portions of the small rRNA gene (16S). The objectives were to determine 1) if known coral bacterial pathogens Serratia marcescens (Acroporid Serratiosis), Vibrio coralliilyticus (temperature-dependent bleaching, White Syndrome), Vibrio shiloi (bleaching, necrosis), and Aurantimonas coralicida (White Plague Type II) were present in any samples, and 2) if there were any differences in microbial community profiles of each healthy, unaffected or diseased coral mucus swab. In addition to coral mucus, water and sediment samples were included to show ambient microbial populations. In the first test, PCR was used to separately amplify the unique and diagnostic region of the 16S rRNA gene for each of the coral pathogens being screened. Each pathogen test was designed so that an amplified DNA fragment could be seen only if the specific pathogen was present in a sample. A positive result was indicated by bands of DNA of the appropriate size on an agarose gel, which separates DNA fragments based on the size of the molecule. DNA from pure cultures of each of the pathogens was used as a positive control for each assay.

烟草FtsZ基因的表达特征分析及其对质体发生的影响

FtsZ (filamentation temperature-sensitive，fts)是广泛存在于原核生物和高等植物中的一种功能蛋白。它控制着原核细胞和质体的分裂过程。研究该基因的表达调控特征，为我们进一步认识原核细胞和质体分裂的分子机制及真核细胞的起源和进化等重要问题提供了新的思路。从烟草克隆FtsZ cDNA，构建了谷胱甘肽转移酶（GST, glutathione S-transferase，EC 2.5.1.18）与FtsZ融合蛋白的表达质粒，并将其导入到在异丙基-β-D-硫代半乳糖苷(IPTG)诱导下能高效表达的JM109大肠杆菌中。高表达的融合蛋白通过谷胱甘肽一琼脂糖(glutathione-agarose)亲和层析和SDS-聚丙烯酰胺凝胶电泳纯化后，用以免疫兔子制备抗血清。免疫印迹法表明烟草FtsZ基因表达具有明显的组织器官特征，在质体（叶绿体）分裂活跃部位表达强：幼嫩花瓣>幼叶>幼根>老叶>茎。黑暗处理l天对FtsZ表达似乎无影响，随黑暗培养时间延长，FtsZ蛋白表达逐渐降低，叶绿体转化成为数目众多（增加2-3倍）体积小的淡黄色或白色质体。该实验结果显示，光对植物FtsZ基因表达很可能无直接影响，FtsZ基因表达强弱是决定质体（叶绿体）分裂和细胞中质体（叶绿体）数目多少的主要原因之一。

Detection of usual and atypical aldehyde dehydrogenase alleles by mismatch amplification mutation assay

The genotypes of liver mitochondrial high-affinity aldehyde dehydrogenase-2 (ALDH2) are strongly associated with the drinking behavior and the alcohol liver diseases, since the individuals with atypical ALDH(2)(2) allele have higher levels of acetaldehyde in their plasma. The atypical ALDH(2)(2) allele has a nucleotide base transition (G-->A) in its exon 12. Based on this point mutation, we developed a rapid, reliable and inexpensive method, mismatch amplification mutation assay (MAMA), for the determination of human ALDH2 usual and atypical alleles. Two pairs of primers were designed for the amplification of the usual ALDH(2)(1) allele and the atypical ALDH(2)(2) allele, respectively. If the sample for the detection was heterozygous, it could be amplified by both of the primers. The product of polymerase chain reaction (PCR) of ALDH2 exon 12 could be easily screened by electrophoresis on a 2% agarose gel. The results of the MAMA method were further confirmed by sequencing. In the total of fifty samples from unrelated healthy Chinese Han people from Wuhan, China, the frequency of atypical ALDH(2)(2) allele was found to be 12%.

Genetic diversity study of Caspian brown trout (Salmo trutta caspius Kessler, 1877) population in five rivers in the southern part of Caspian Sea, Iran

For study the genetic diversity of Caspian brown trout population in five rivers in the southern part of Caspian Sea in Iran 182 number generators in the fall and winter of 1390 were collected in Chalus, Sardab Rud, Cheshmeh Kileh, Kargan Rud and Astara rivers. Then about 3-5 g of soft and fresh tissue from the bottom fin fish removed and were fixed in ethanol 96°. Genomic DNA was extracted by using ammonium acetate, then quantity and quality of the extracted DNA were determined by using spectrophotometry and horizontal electrophoresis in 1% agarose gel. The polymerase chain reaction was performed by using 16 SSR primers and sequencing primers (D-Loop) and the quality of PCR products amplified by SSR method were performed by using horizontal electrophoresis in 2% agarose gel. Alleles and their sizes were determined by using vertical electrophoresis in 6% polyacrylamide gel and silver nitrate staining method. Gel images were recorded by gel documentarian, the bands were scored by using Photo- Capt software and statistical analysis was performed by using Gene Alex and Pop Gene software. Also the PCR sequencing products after quality assessment by usinghorizontal electrophoresis in 1.5% agarose gel were purified and sent to South Korea Bioneer Corporation for sequencing. Sequencing was performed by chain termination method and the statistical analysis was performed by using Bio- Edit, Mega, Arlequin and DNA SP software. The SSR method, 5 pairs of primers produced polymorphic bands and the average real and effective number of alleles were calculated 5.60±1.83 and 3.87±1.46 in the Cheshmeh Kileh river and 7.60±1.75 and 5.48±1.32 in the Karganrud river and the mean observed and expected heterozygosity were calculated 0.44 ±0.15 and 0.52 ±0.16 in the Cheshmeh Kileh river and 0.50 ±0.11 and 0.70±0.13 in the Karganrud river. Analysis of Molecular Variance results showed that significant differences in genetic diversity between and within populations and between and within individuals in the studied rivers (P<0.01). The sequencing method identified 35 different haplotype, the highest number of polymorphic position (251) and haplotype (14) were observed in the Chalus river. The highest mean observed number of alleles (2.24±0.48) was calculated in the Sardabrud river, the highest mean observed heterozygosity (1.00±0.03) was calculated in the Chalus river and the highest mean nucleotide diversity (0.13±0.07) was observed in the Sardabrud river and mean haplotype diversity was obtained (1) in three studied rivers. The overall results show that there are no same population of this fish in the studied rivers and Karganrud and Chalus rivers in the SSR and sequencing methods had the highest levels of genetic diversity.

Population genetic structure of Rutilus frisii kutum in Caspian Sea using biometry and microsatellite molecular technique

In order to carry out Biometric studies, 75 samples were caught from 3 locations ( Tajan river, Sefidrud and Shirud) using Salic and the length (±1 mm) and weights (± 5 gr) of samples were determined. Using One-way ANOVA by SPPSS software, there wasn’t significant difference between locations in length and fecondity (P ≥0.01(, but there was significant difference between Shirud and tajan samples with sefidrud in weight ) P≤0.01(. In order to carry out genetic variation studies, 210 fish were caught from 3 different regions of the Iranian coastline (Khoshkrud, Tonekabon, Gorganrud) and 1 region in Azerbaijan (Waters of the Caspian Sea close to Kura River mouth) during 2008-2009 . Genomic DNA was extracted of fin using the phenol-chloroform. The quantity and quality of DNA from samples were assessed by spectrophptometer and 1% agarose gel electro-phoresis. PCR was carried out using 15 paired microsatellite primers. PCR products were separated on 8% polyacrylamide gels that were stained using silver nitrate. Molecular weight calculate using UVTech software. The recorded microsatellite genotypes were used as input data for the GENALEX software version 6 package in order to calculate allele and genotype frequencies, observed (Ho) and (He) expected heterozygosities and to test for deviations from Hardy-Weinberg equilibrium. Genetic distance between two populations was estimated from Nei standard genetic distance and genetic similarity index (Nei, 1972). Genetic differentiation between populations was also evaluated by the calculation of pairwise estimates of Fst and Rst values. From 15 SSR markers were used in this investigation, 9 of them were polymorph. Average of expected and observed heterozygosity was 0.54 and 0.49 respectively. Significant deviations from Hardy-Weinberg expectations were observed in all of location except Anzali lagoon- autumn in AF277576 and EF144125, Khoshkrud in EF144125 and Gorganrud and Kura in AF277576. Using Fst and Rst there was significant difference between locations ) P≤0.01(. According to Fst , the highest population differentiation (Fst= 0.217) was between Gorganrud and Khoshkrud that have the lowest Nm and the lowest (Fst= 0.086) was between Gorganrud and Tonekabon that have the highest Nm. Using Rst the highest population differentiation (Rst= 0.271) was between Tonekabon and spring Anzali lagoon and the lowest (Rst= 0.026) was between Tonekabon and Autumn Anzali 159 lagoon. Also the difference between Spring Anzali lagoon and Autumn Anzali lagoon was noticeable (Fst=0.15). AMOVA analysis with consideration of 2 sampling regions (Iran and Azerbaijan) and 7 sampling locations (Iran: Khoshkrud, Tonekabon, Gorganrud, Spring Anzali lagoon and Autumn Anzali lagoon ; Azerbaijan: the Kura mouth) revealed that almost all of the variance in data namely 83% )P≤0.01( was within locations, Genetic variances among locations was 14% )P≤0.01( and among regions was 3% )P≤0.01(. The genetic distance was the highest (0.646) between Gorganrud and Autumn Anzali lagoon populations, whereas the lowest distance (0.237) was between Gorganrud and Tonekabon River. Result obtained from the present study show that at least 2 different population of Rutilus frissi kutum are found in the Caspian sea,which are including the kura river population and the southern Caspian sea samples and it appears that there is more than one population in southern Caspian sea that should be attantioned in artifical reproduction Center and stoke rebilding.

The genetic diversity of Acipenser stellatus populations in the Caspian Sea was studied using microsatellite technique

A total of 361 caudal fin samples were collected from adult A. stellatus specimens caught in the north Caspian Sea, including specimens from Kazakhstan (Ural River), Russia (Volga River), Azerbaijan (Kura River), specimens caught in the south Caspian Sea including specimens from Fishery Zone 1 (from Astara to Anzali), Fishery Zone 2 (from Anzali to Ramsar), Fishery Zone 3 (from Nowshahr to Babolsar), Fishery Zone 4 (from Miyankaleh to Gomishan) as well as from specimens caught in Turkmenistan (all specimens were collected during the sturgeon stock assessment survey). About 2 g of fin tissue was removed from each caudal fin sample, stored in 96% ethyl alcohol and transferred to the genetic laboratory of the International Sturgeon Research Institute. Genomic DNA was extracted using phenol-chloroform method. The quality and quantity of DNA was assessed using 1% Agarose gel electrophoresis and Polymerase Chain Reaction (PCR) was conducted on the target DNA using 15 paired microsatellite primer. PCR products were electrophoresed on polyacrylamide gels (6%) that were stained using silver nitrate. Electrophoretic patterns and DNA bands were analyzed with BioCapt software. Allele count and frequency, genetic diversity, expected heterozygosity and observed heterozygosity allele number, and the effective allele number, genetic similarity and genetic distance, FST and RST were calculated. The Hardy Wienberg Equilibrium based on X2 and Analysis of Molecular Variance (AMOVA) at 10% confidence level was calculated using the Gene Alex software. Dendrogram for genetic distances and identities were calculated using TFPGA program for any level of the hierarchy. It is evident from the results obtained that the 15 paired primers studied, polymorphism was observed in 10 pairs in 12 loci, while one locus did not produce DNA bands. Mean allele number was 13.6. Mean observed and expected heterozygosity was 0.86 and 0.642, respectively. It was also seen that specimens from all regions were not in Hardy Wienberg Equilibrium in most of the loci (P≤0.001). Highest Fst (0.063) was observed when comparing specimens from Fishery Zone 2 and Fishery Zone 4 (Nm=3.7) and lowest FST (0.028) was observed when comparing specimens from the Volga River and those from the Ural River (8.7). Significant differences (P<0.01) were observed between RST recorded in the specimens studied. Highest genetic distance (0.604) and lowest genetic resemblance (0.547) were observed between specimens from Fishery zones 2 and 4. Lowest genetic distance (0.311) and highest genetic resemblance (0.733) was observed between specimens from Turkmenistan and specimens from Fishery zone 1. Based on the genetic dendrogeram tree derived by applying UPGMA algorithm, A. stellatus specimens from Fishery zone 2 or in other words specimens from the Sepidrud River belong to one cluster which divides into two clusters, one of which includes specimens from Fishery zones 1, 3 and 4 and specimens from Turkmenistan while the other cluster includes specimens from Ural, Volga and Kura Rivers. It is thus evident that the main population of this species belongs to the Sepidrud River. Results obtained from the present study show that at least eight different populations of A. stellatus are found in the north and south Caspian Sea, four of which are known populations including the Ural River population, the Volga River population, the Kura River population and the Sepidrud River populations. The four other populations identified belonging to Fishery zones 1, 3, and 4 and to Turkmenistan are most probably late or early spawners of the spring run and autumn run of each of the major rivers mentioned. Specific markers were also identified for each of the populations identified. The Ural River population can be identified using primers Spl-68, 54b and Spl-104, 163 170, 173, the Volga River population can be identified using primers LS-54b and Spl-104, 170, 173 113a and similarly the population from the Kura River can be identified using primers LS-34, 54b and Spl-163, 173 and that from the Sepidrud River can be identified using primers LS-19, 34, 54b and Spl-105, 113b. This study gives evidence of the presence of different populations of this species and calls for serious measures to be taken to protect the genetic stocks of these populations. Considering that the population of A. stellatus in Fishery zone 2 is an independent population of the Sepidrud River in the Gilan Province, the catch of these fishes in the region needs to be controlled and regulated in order to restore the declining stocks of this species.

The genetic structure and phylogenetics of pikeperch (Sander lucioperca) Anzali and Amirkolaye wetlands and perch (Perca fluviatilis) populations in Aras Dam and south-west of the Caspian Sea

The genetic structure of pikeperch (Sander lucioperca) and perch (Perca fluviatilis) populations was studied using microsatellite technique. A total of 207 specimens of adult pikeperch were collected from Aras dam (57 specimens), Anzali wetland (50 specimens), Talesh (50 specimens) and Chaboksar (50 specimens) coasts. Also a total of 158 specimens of adult perch were collected from Anzali (Abkenar (50 specimens)and Hendekhale(48 specimens)) and Amirkolaye(60 specimens) wetlands. About 2 g of each specimen's dorsal fin was removed, stored in 96% ethyl alcohol and transferred to the genetic laboratory of the International Sturgeon Research Institute. Genomic DNA was extracted using ammonium-acetate method. The quality and quantity of DNA was assessed using 1% agarose gel electrophoresis. Polymerase Chain Reaction (PCR) was conducted on the target DNA using 15 pairs of microsatellite primers. PCR products were electrophoresed on poly acryl amide gels (6%) that were stained that were stained using silver nitrate. DNA bands were analyzed with BioCapt software. Allele count and frequency, genetic diversity, expected and observed heterozygosity , allele number and the effective allele number, genetic similarity and genetic distance, Fst, Rst, Hardy Weinberg Equilibrium based on X2 and Analysis of Molecular Variance (AMOVA) at 10% confidence level was calculated using the Gene Alex software. Dendogram for genetic distances and identities were calculated using TFPGA program for any level of hierarchy. The results for P. fluviatilis showed that from 15 pair of primers that were examined 6 polymorphic and 7 monomorphic loci were produced, while 2 loci didn't produce any DNA bands. Mean allele number was 4.1±1.1 and mean observed and expected heterozygosity was 0.56±0.12 and 0.58±0.14 respectively. It was also seen that specimens from all regions were not in Hardy Weinberg Equilibrium in some of loci (P<0.001). Highest Fst (0.095) with Nm=2.37 was observed between Hendekhale and Amirkolaye and the lowest Fst (0.004) with Nm=59.31 was observed between Abkenar and Hendekhale. According to AMOVA Significant difference (P<0.05) was observed between recorded Rst in the studied regions in Anzali and Amirkolaye lagoons. In another words there are two distinct populations of this species in Anzali and Amirkolaye lagoons. The highest genetic distance (0.181) and lowest genetic resemblance (0.834) were observed between specimens from Hendekhale and Amirkolaye and the lowest genetic distance (0.099) and highest genetic 176 resemblance (0.981) were observed between specimens from Abkenar and Hendekhale. Based on the genetic dendogram tree derived by applying UPGMA algorithm, specimens from Anzali and Amirkolaye wetlands have the same ancestor. On the other hand there is no noticeable genetic distance between the specimens of these two regions. Also the results for S. lucioperca showed that from 15 pair of primers that were examined 6 polymorphic and 7 monomorphic loci were produced, while 2 loci didn't produce any DNA bands. Mean allele number was 3.0±0.6 and mean observed and expected heterozygosity was 0.52±0.21 and 0.50±0.14 respectively. It was also seen that specimens from all regions were not in Hardy Weinberg Equilibrium in some of loci (P<0.001). Highest Fst (0.093) with Nm=2.43 was observed between Aras dam and Anzali wetland and the lowest Fst (0.022) with Nm=11.27 was observed between Talesh and Chaboksar coasts. Significant differences (P<0.05) were observed between recorded Rst in the studied regions exept for Talesh and Chaboksar Coasts. In another words there are three distinct populations of this species in Caspian sea, Anzali wetland and Aras dam. Highest genetic distance (0.110) and lowest genetic resemblance (0.896) were observed between specimens from Aras dam and Anzali wetland and the lowest genetic distance (0.034) and highest genetic resemblance (0.966) were observed between specimens from Talesh and Chaboksar coasts. Based on the genetic dendogram tree derived by applying UPGMA algorithm, specimens from Talesh and Chaboksar coasts have the lowest genetic distance. On the other hand the main population of this species belongs to Anzali wetland. Phylogenetic relationship of these two species was inferred using mitochondrial cytochrome b gene sequencing. For this purpose 2 specimens of P. fluviatilis from Anzali wetland, 2 specimens of S. lucioperca from Aras dam and 2 specimens of S. lucioperca from Anzali wetland were sequenced and submitted in Gene Bank. These sequences were aligned with Clustal W. The phylogenic relationships were assessed with Mega 4. The results of evolutionary history studies of these species using Neighbor-Joining and Maximum Parsimony methods showed that the evolutionary origin of pikeperch in Aras Dam and Anzali wetland is common. On the other hand these two species had common ancestor in about 4 million years ago. Also different sequences of any region specimens are supposed as different haplotypes. 177 As a conclusion the results of this study showed that microsatellite and mtDNA sequencing methods respectively are effective in genetic structure and phylogenic studies of P. fluviatilis and S. lucioperca.

Toxicity of microcystins in the isolated hepatocytes of common carp (Cyprinus carpio L.)

The toxicity of hepatotoxic microcystins produced mainly by Microcystis aeruginosa in mammals and fishes was well studied in recent years. However, there were scarcely reports in toxic effects of microcystins on isolated hepatocytes of fishes, especially investigation of microcystin-induced apoptosis and/or necrosis in carp hepatocytes. In the present study, the isolated hepatocytes of common carp were exposed to various concentrations of microcystins (0.01, 0.1, 1, 10, 100, 1000 mu g L-1) for 2, 4, 8, 16 and 24 h, respectively, and cytotoxicity of microcystins in the toxin-treated cells was determined. Results of this study showed that cytotoxicity of microcystins on carp hepatocytes was time and dose-dependent, and the approximate LC50 of microcystins in carp hepatocytes was 169.2 mu g L-1. The morphological changes typical of apoptosis, such as blebbing of cell membrane, condensation and fragmentation of cell nucleus were observed in the hepatocytes exposed to microcystins (1, 10 and 100 mu g L-1) using fluorescence and differential interference contrast microscopy. Agarose gel electrophoresis of DNA demonstrated a typical apoptotic "ladder pattern" in microcystin-treated hepatocytes after 16 h of exposure. Results of the present study indicated that the form of cell death in microcystin-treated hepatocytes depend on the exposure dose of toxin. When lower concentration of microcystins (10 and 100 mu g L-1) was used for exposure, carp hepatocytes died in apoptosis while, when higher one used (1000 mu g L-1), they died in the form of necrosis. (C) 2006 Elsevier Inc. All rights reserved.

Improvement and observation of immunoelectron microscopic method for the localization of frog Rana grylio virus (RGV) in infected fish cells

In this paper, to understand the roles of amorphous structures which were observed within the viromatrix of Rana grylio virus (RGV), an improved immunoelectron microscopy (IEM) method was developed to detect the localization of RGV in carp Epithelipma papulosum cyprinid (EPC) cells. Infected EPC cells were fixed with 4% paraformaldehyde-0.25% glutaraldehyde mixture, dehydrated completely, and embedded in LR White resin. This method allowed good ultrastructural preservation and specific labeling with anti-RGV antibodies. The results of IEM showed that colloidal gold mainly bound to the capsids of viral particles at the stage of viral assembly, while during the viral maturation colloidal gold bound to the envelop of virions. In addition, within the viromatrix, the amorphous structures, including dense floccules, membranous materials and tubules, also had strong colloidal gold signals, revealing that those amorphous structures were participated in RGV assembly. In contrast, no significant gold labeling signals were obtained in negative controls. The present study not only provided further evidence that amorphous structures within the viromatrix were involved in the process of RGV assembly, but also developed an improved IEM method for studying the interaction between iridovirus and host cells. (C) 2006 Elsevier Ltd. All rights reserved.

Induction of oxidative stress and apoptosis by PFOS and PFOA in primary cultured hepatocytes of freshwater tilapia (Oreochromis niloticus)

Perfluorinated organic compounds (PFOCs) are emerging persistent organic pollutants (POPs) widely present in the environment, wildlife and human. We studied the cellular toxicology of perfluorooctane sulfonate (PFOS) and perfluorooctanoic acid (PFOA) on oxidative stress and induction of apoptosis in primary cultured hepatocytes of freshwater tilapia (Oreochromis niloticus). Cultured hepatocytes were exposed to PFOS or PFOA (0, 1, 5, 15 and 30 mg L-1) for 24 h, and a dose-dependent decrease in cell viability was determined using trypan blue exclusion method. Significant induction of reactive oxygen species (ROS) accompanied by increases in activities of superoxide dismutase (SOD), catalase (CAT) and glutathione reductase (GR) were found, while activities of glutathione peroxidase (GPx) and glutathione-S-transferase (GST) were decreased. Glutathione (GSH) content was reduced following treatment of PFOA and PFOS. A dose-dependent increase in the lipid peroxidation (LPO) level (measured as maleic dialdehyde, MDA) was observed only in the PFOA exposure groups, whereas LPO remained unchanged in the PFOS exposure groups. Furthermore, a significant activation of caspase-3, -8, -9 activities was evident in both PFOS and PFOA exposure groups. Typical DNA fragmentation (DNA laddering) was further characterized by agarose gel electrophoresis. The overall results demonstrated that PFOS and PFOA are able to produce oxidative stress and induce apoptosis with involvement of caspases in primary cultured tilapia hepatocytes. (c) 2007 Elsevier B.V. All rights reserved.

Induction of apoptosis in a carp leucocyte cell line infected with turbot (Scophthalmus maximus L.) rhabdovirus

A rhabdovirus was observed from the diseased turbot (Scophthalmus maximus L.) with lethal syndrome. In this study, a carp leucocyte (CLC) cell line was used to investigate the infection process and cell death mechanism occurring during the virus infection. Strong cytopathogenic effect (CPE) and the morphological changes, such as extreme chromatin condensation, nucleus fragmentation, and apoptotic body formation, were observed under fluorescence microscopy after DAPI staining in the infected CLC cells. Transmission electron microscopy analysis showed cell shrinkage, plasma membrane blebbing, cytoplasm vacuolization, chromatin condensation, nuclear breakdown and formation of discrete apoptotic bodies. The bullet-shaped nucleocapsids were measured and ranged in size from 110 to 150 nm in length and 40 to 60 nm in diameter. And therefore the virus is called Scophthalmus maximus rhabdovirus (SMRV). Agarose gel electrophoresis analysis of the DNA extracted from infected cells showed typical DNA ladder in the course of SMRV infection. Flow cytometry analysis of SMRV infected CLC cells detected apoptotic peak in the virus infected CLC cells. Virus titre analysis and electron microscopic observation revealed that the virus replication fastigium was earlier than that of the apoptosis occurrence. No apoptosis was observed in the CLC infected with UV-inactivated SMRV. All these supported that SMRV infected CLC cells undergo apoptosis and the virus replication is necessary for apoptosis induction of CLC cells. (C) 2004 Published by Elsevier B.V.