{"id":8921,"date":"2024-01-04T09:46:43","date_gmt":"2024-01-04T12:46:43","guid":{"rendered":"https:\/\/www.infraestruturameioambiente.sp.gov.br\/pgibt\/?page_id=8921"},"modified":"2024-01-04T09:46:43","modified_gmt":"2024-01-04T12:46:43","slug":"leonardo-tristao-silva-ms","status":"publish","type":"page","link":"https:\/\/www.infraestruturameioambiente.sp.gov.br\/pgibt\/leonardo-tristao-silva-ms\/","title":{"rendered":"Leonardo Trist\u00e3o Silva &#8211; MS"},"content":{"rendered":"<p><img decoding=\"async\" loading=\"lazy\" class=\"size-full wp-image-8353 aligncenter\" src=\"https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2023\/01\/faixaposipa.jpg\" alt=\"\" width=\"950\" height=\"163\" srcset=\"https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2023\/01\/faixaposipa.jpg 950w, https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2023\/01\/faixaposipa-320x55.jpg 320w, https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2023\/01\/faixaposipa-768x132.jpg 768w, https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2023\/01\/faixaposipa-250x43.jpg 250w, https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2023\/01\/faixaposipa-550x94.jpg 550w, https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2023\/01\/faixaposipa-800x137.jpg 800w\" sizes=\"(max-width: 950px) 100vw, 950px\" \/><\/p>\n<hr align=\"center\" noshade=\"noshade\" size=\"1\" width=\"100%\" \/>\n<h2 style=\"text-align: center\">Leonardo Trist\u00e3o Silva<\/h2>\n<hr align=\"center\" noshade=\"noshade\" size=\"1\" width=\"100%\" \/>\n<p align=\"center\"><img decoding=\"async\" loading=\"lazy\" class=\"aligncenter size-full wp-image-8922\" src=\"https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2024\/01\/leonardo-tristao-silva.jpg\" alt=\"\" width=\"567\" height=\"384\" srcset=\"https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2024\/01\/leonardo-tristao-silva.jpg 567w, https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2024\/01\/leonardo-tristao-silva-284x192.jpg 284w, https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2024\/01\/leonardo-tristao-silva-250x169.jpg 250w, https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2024\/01\/leonardo-tristao-silva-550x372.jpg 550w, https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2024\/01\/leonardo-tristao-silva-266x180.jpg 266w, https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2024\/01\/leonardo-tristao-silva-443x300.jpg 443w\" sizes=\"(max-width: 567px) 100vw, 567px\" \/><\/p>\n<p style=\"text-align: center;background: white;margin: 0cm 0cm 22.5pt 0cm\" align=\"center\"><span style=\"color: #231f20\">Em 20 de setembro de 2023, Leonardo Trist\u00e3o, aluno de mestrado do Programa de P\u00f3s-Gradua\u00e7\u00e3o em Biodiversidade Vegetal e Meio Ambiente do Instituto de Pesquisas Ambientais, bolsista CAPES, defendeu sua Disserta\u00e7\u00e3o de Mestrado, de forma remota atrav\u00e9s da plataforma Microsoft Teams, intitulada, \u201cVaria\u00e7\u00e3o espacial da biomassa e estrutura da comunidade algal no epip\u00e9lon ao longo de um gradiente de profundidade em dois reservat\u00f3rios de diferentes trofias\u201d, <\/span><\/p>\n<p style=\"text-align: center;background: white;margin: 0cm 0cm 22.5pt 0cm\" align=\"center\"><span style=\"color: #231f20\">A banca examinadora foi presidida pela sua orientadora Dra. Carla Ferragut (Instituto de Pesquisas Ambientais \u2013 IPA) e composta pela Dra. Gisele Carolina Marquardt (Universidade Estadual do Paran\u00e1 \u2013 UNESPAR) e pela Dra. Karine Borges Machado (Universidade Estadual de Goi\u00e1s &#8211; UEG).<\/span><\/p>\n<hr align=\"center\" noshade=\"noshade\" size=\"1\" width=\"100%\" \/>\n<h3 style=\"text-align: center\">Varia\u00e7\u00e3o espacial da biomassa e estrutura da comunidade algal no epip\u00e9lon ao longo de um gradiente de profundidade em dois reservat\u00f3rios de diferentes trofias<\/h3>\n<hr align=\"center\" noshade=\"noshade\" size=\"1\" width=\"100%\" \/>\n<h4 style=\"text-align: center\"><strong>ABSTRACT<\/strong><\/h4>\n<p>Most limnological studies address the pelagic zone and rarely consider the magnitude or variability of phytobenthic changes. The present study evaluated changes in biomass and community structure of algae and cyanobacteria in the epipelon in a depth gradient in a shallow mesotrophic and supereutrophic reservoirs. This study identified the benthic zone with the highest biomass and richness of epipelic algae. Sampling was carried out during the stratification period (summer) and in triplicate, including six depths (0.5 m; 1.0 m; 1.5 m; 2.0 m; 2.5 m; 3.0 m) in the mesotrophic reservoir and nine depths (0.5 m; 1.0 m; 1.5 m; 2.0 m; 2.5 m; 3.0 m; 3.5 m; 4 m and 4.5 m) in the eutrophic reservoir. Higher light attenuation and total phosphorus concentration were found at the 3 m in mesotrophic reservoir. Concerning the epipelon, greater biomass and species richness were found at 1.5 m depth, while the highest values of ash-free dry mass occurred at the deepest points (2.5 m and 3 m). A total of 65 species of epipelic algae were found in mesotrophic reservoir. <em>Oedogonium<\/em> sp. and <em>Pinnularia viridis<\/em> were the species that contributed most to the total biovolume. The epipelon presented the highest biomass of the algae and cyanobacteria at the shallowest depths (0.5m and 1m), constituting the benthic zone with the high biomass production in the mesotrophic reservoir. In the supereutrophic reservoir, the higher availability of light, total phosphorus, and free CO\u2082 was observed at the shallowest depths (0.5 m and 1 m). A total of 51 epipelic algae and cyanobacteria species were found in the eutrophic reservoir. <em>Fragilaria<\/em> sp.1, <em>Microcystis aeruginosa<\/em> and <em>Pinnularia nobilis<\/em> var. <em>regularis<\/em> were the species with the higher contribution to total biomass at different depths. In the epipelon, the highest chlorophyll-a values were observed at the shallowest depths (0.5 m and 1 m), and the highest biomass values were observed at 1 m and 3 m, which was the benthic zone with the higher biomass production. Despite the differences in epipelon zonation in reservoirs of different trophic states, some aspects were similar, such as the influence of light attenuation on the epipelon variation in the depth gradient. Thus, the light was a determining factor for the epipelon growth and could be a limiting factor for the community, regardless of trophy. In conclusion, changes in biomass and structure in the epipelon were associated with the depth gradient, which determined the light and nutrient availability for the community in the mesotrophic and supereutrophic reservoirs.<\/p>\n<p style=\"text-align: justify\"><strong>Keywords:<\/strong> epipelic algae, phytobenthos, benthic environment, environmental factors, zonation, supereutrophic and mesotrophic reservoir<\/p>\n<h4 style=\"text-align: center\"><strong>RESUMO<\/strong><\/h4>\n<p style=\"text-align: justify\">A maioria dos estudos limnol\u00f3gicos aborda a zona pel\u00e1gica e raramente considera a magnitude ou variabilidade das mudan\u00e7as fitobent\u00f4nicas. O presente estudo avaliou as mudan\u00e7as da biomassa e estrutura da comunidade de algas e cianobact\u00e9rias no epip\u00e9lon ao longo de um gradiente de profundidade em reservat\u00f3rio raso mesotr\u00f3fico e supereutr\u00f3fico. Este estudo identificou a zona b\u00eantica de maior biomassa e riqueza de algas epip\u00e9licas. A amostragem foi realizada no per\u00edodo de estratifica\u00e7\u00e3o (ver\u00e3o) e em triplicata, incluindo 6 profundidades (0,5 m; 1,0 m; 1,5 m; 2,0 m; 2,5 m; 3,0 m) no reservat\u00f3rio mesotr\u00f3fico e 9 profundidades (0,5 m; 1,0 m; 1,5 m; 2,0 m; 2,5 m; 3,0 m; 3,5m; 4m e 4,5m) no reservat\u00f3rio eutr\u00f3fico. No reservat\u00f3rio mesotr\u00f3fico, evidenciou-se uma maior atenua\u00e7\u00e3o da luz e concentra\u00e7\u00e3o de f\u00f3sforo total nos pontos de maior profundidade (3 m). Em rela\u00e7\u00e3o ao epip\u00e9lon, maior biomassa e riqueza de esp\u00e9cies foi encontrada em 1,5 m de profundidade, enquanto os maiores valores de massa seca livre de cinzas ocorreram nos pontos mais profundos (2,5m e 3m). Foram encontradas um total de 65 esp\u00e9cies de algas epip\u00e9licas. Oedogonium sp. e Pinnularia viridis foram as esp\u00e9cies maior contribui\u00e7\u00e3o para o biovolume total. O epip\u00e9lon apresentou a maior biomassa da comunidade de algas e cianobact\u00e9rias nas profundidades mais rasas (0,5m e 1m), constituindo-se como a zona b\u00eantica de maior produ\u00e7\u00e3o de biomassa no reservat\u00f3rio mesotr\u00f3fico. No reservat\u00f3rio supereutr\u00f3fico a maior disponibilidade de luz, f\u00f3sforo total e CO\u2082 livre foi observada nas profundidades mais rasas (0,5m e 1 m). Encontrou-se um total de 51 esp\u00e9cies de algas e cianobact\u00e9rias epip\u00e9licas. A Fragilaria sp.1, Microcystis aeruginosa e a Pinnularia nobilis var. regularis foram as esp\u00e9cies com maior contribui\u00e7\u00e3o para biomassa total nas diferentes profundidades. No epip\u00e9lon, os maiores valores de clorofila-a foram observados nas profundidades mais rasas (0,5 m e 1 m), enquanto os maiores valores de biomassa foram observados em 1 m e 3 m, sendo a zona bent\u00f4nica de maior produ\u00e7\u00e3o de biomassa. Apesar das diferen\u00e7as na zona\u00e7\u00e3o do epip\u00e9lon nos reservat\u00f3rios de diferentes trofias, alguns aspectos foram semelhantes, como a influ\u00eancia da atenua\u00e7\u00e3o de luz sobre a varia\u00e7\u00e3o do epip\u00e9lon no gradiente de profundidade. Assim, a luz foi um fator determinante para o crescimento da comunidade epip\u00e9lica e pode ser um fator limitante para a comunidade, independentemente da trofia. Em conclus\u00e3o, as mudan\u00e7as na biomassa e a estrutura do epip\u00e9lon foram associadas ao gradiente de profundidade, que determinou a disponibilidade de luz e nutrientes para comunidade no reservat\u00f3rio mesotr\u00f3fico e no reservat\u00f3rio supereutr\u00f3fico.<\/p>\n<p style=\"text-align: justify\"><strong>Palavras-chave:<\/strong> algas epip\u00e9licas, ambiente bent\u00f4nico, fatores ambientais, zona\u00e7\u00e3o, reservat\u00f3rio supereutr\u00f3fico e mesotr\u00f3fico.<\/p>\n<hr align=\"center\" noshade=\"noshade\" size=\"1\" width=\"100%\" \/>\n<p style=\"text-align: center\"><a href=\"https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2024\/01\/leonardo_tristao_silva_ms.pdf\" target=\"_blank\" rel=\"noopener\"><img decoding=\"async\" loading=\"lazy\" class=\"aligncenter\" src=\"https:\/\/smastr16.blob.core.windows.net\/pgibt\/2013\/09\/pdf_grande.gif\" alt=\"pdf_grande\" width=\"60\" height=\"60\" \/><\/a><a href=\"https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2024\/01\/leonardo_tristao_silva_ms.pdf\"><strong>Leonardo Trist\u00e3o Silva<\/strong><\/a><br \/>\n<a href=\"https:\/\/smastr16.blob.core.windows.net\/pgibt\/sites\/242\/2024\/01\/leonardo_tristao_silva_ms.pdf\">Varia\u00e7\u00e3o espacial da biomassa e estrutura da comunidade algal no epip\u00e9lon ao longo de um gradiente de profundidade em dois reservat\u00f3rios de diferentes trofias<\/a><\/p>\n<hr align=\"center\" noshade=\"noshade\" size=\"1\" width=\"100%\" \/>\n<p style=\"text-align: center\"><strong>\u00a0<a href=\"www.infraestruturameioambiente.sp.gov.br\/pgibt\/dissertacoesteses\/\">VOLTAR AS DISSERTA\u00c7\u00d5ES E TESES<\/a><\/strong><\/p>\n<hr align=\"center\" noshade=\"noshade\" size=\"1\" width=\"&quot;10&lt;\/p\" \/>\n","protected":false},"excerpt":{"rendered":"<p>Leonardo Trist\u00e3o Silva Em 20 de setembro de 2023, Leonardo Trist\u00e3o, aluno de mestrado do Programa de P\u00f3s-Gradua\u00e7\u00e3o em Biodiversidade Vegetal e Meio Ambiente do Instituto de Pesquisas Ambientais, bolsista CAPES, defendeu sua Disserta\u00e7\u00e3o de Mestrado, de forma remota atrav\u00e9s da plataforma Microsoft Teams, intitulada, \u201cVaria\u00e7\u00e3o espacial da biomassa e estrutura da comunidade algal no [&hellip;]<\/p>\n","protected":false},"author":187,"featured_media":0,"parent":0,"menu_order":0,"comment_status":"closed","ping_status":"closed","template":"","meta":[],"_links":{"self":[{"href":"https:\/\/www.infraestruturameioambiente.sp.gov.br\/pgibt\/wp-json\/wp\/v2\/pages\/8921"}],"collection":[{"href":"https:\/\/www.infraestruturameioambiente.sp.gov.br\/pgibt\/wp-json\/wp\/v2\/pages"}],"about":[{"href":"https:\/\/www.infraestruturameioambiente.sp.gov.br\/pgibt\/wp-json\/wp\/v2\/types\/page"}],"author":[{"embeddable":true,"href":"https:\/\/www.infraestruturameioambiente.sp.gov.br\/pgibt\/wp-json\/wp\/v2\/users\/187"}],"replies":[{"embeddable":true,"href":"https:\/\/www.infraestruturameioambiente.sp.gov.br\/pgibt\/wp-json\/wp\/v2\/comments?post=8921"}],"version-history":[{"count":1,"href":"https:\/\/www.infraestruturameioambiente.sp.gov.br\/pgibt\/wp-json\/wp\/v2\/pages\/8921\/revisions"}],"predecessor-version":[{"id":8924,"href":"https:\/\/www.infraestruturameioambiente.sp.gov.br\/pgibt\/wp-json\/wp\/v2\/pages\/8921\/revisions\/8924"}],"wp:attachment":[{"href":"https:\/\/www.infraestruturameioambiente.sp.gov.br\/pgibt\/wp-json\/wp\/v2\/media?parent=8921"}],"curies":[{"name":"wp","href":"https:\/\/api.w.org\/{rel}","templated":true}]}}